6301_Moore_MSWLF_CDLF_Fall2019GW_FID1390315_20200221

is Data - Email CD (data loaded: Yes / No ) Doc/Event #:
ANC DENR I I Environmental Monitoring
Division of Waste Management - Solid Waste Reporting Form
Notice: This form and any information attached to it are "Public Records" as defined in NC General Statute 132-1. As such, these documents are
available for inspection and examination by any person upon request (NC General Statute 132-6).
Instructions:
Prepare one form for each individually monitored unit.
• Please type or print legibly.
Attach a notification table with values that attain or exceed NC 2L groundwater standards or NC 2B surface water standards. The notification
must include a preliminary analysis of the cause and significance of each value. (e.g. naturally occurring, off -site source, pre-existing
condition, etc.).
Attach a notification table of any groundwater or surface water values that equal or exceed the reporting limits.
Attach a notification table of any methane gas values that attain or exceed explosive gas levels. This includes any structures on or nearby the
facility (NCAC 13B .1629 (4)(a)(i).
Send the original signed and sealed form, any tables, and Electronic Data Deliverable to: Compliance Unit, NCDENR-DWM, Solid Waste
Section, 1646 Mail Service Center, Raleigh, NC 27699-1646.
Solid Waste Monitoring Data Submittal Information
Name of entity submitting data (laboratory, consultant, facility owner):
Golder Associates NC, Inc. (on behalf of Moore County)
Contact for questions about data formatting. Include data preparer's name, telephone number and E-mail address:
Name: Benjamin S. Draper, PG Phone: [phone]
E-mail: [e-mail]
NC Landfill Rule: Actual sampling dates (e.g.,
Facility name: Facility Address: Facility Permit # (.0500 or .1600) October 20-24, 2006)
Moore County Landfill 456 Turning Leaf Way 63-01 .500 November 19 - 21, 2019
Aberdeen, NC 28315 January 8, 2020 (Re -sample)
Environmental Status: (Check all that apply)
Initial/Background Monitoring Detection Monitoring Assessment Monitoring QX Corrective Action
of data submitted: (Check all that apply)
Groundwater monitoring data from monitoring wells ❑ Methane gas monitoring data
Groundwater monitoring data from private water supply wells ❑X Corrective action data (specify) Monitored Natural Attenuation Data
Leachate monitoring data
Surface water monitoring data Other(specify)
Notification attached?
No. No groundwater or surface water standards were exceeded.
X Yes, a notification of values exceeding a groundwater or surface water standard is attached. It includes a list of groundwater and surface water
monitoring points, dates, analytical values, NC 2L groundwater standard, NC 26 surface water standard or NC Solid Waste GWPS and
preliminary analysis of the cause and significance of any concentration.
Yes, a notification of values exceeding an explosive methane gas limit is attached. It includes the methane monitoring points, dates, sample
values and explosive methane gas limits.
Certification
To the best of my knowledge, the information reported and statements made on this data submittal and attachments are true and correct.
Furthermore, I have attached complete notification of any sampling values meeting or exceeding groundwater standards or explosive gas
levels, and a preliminary analysis of the cause and significance of concentrations exceeding groundwater standards. I am aware that there
are significant penalties for making any false statement, representation, or certification including the possibility of a fine and imprisonment.
Benjamin S. Draper, PG Senior Project Geologist [phone]
Facility RepjosSMtive Name (Pri
Title
p 2/t /11-v
Date
Golder Associates NC, Inc., 5B Oak Branch Drive, Greensboro, NC 27407
Facility Representative Address
PE C-2862; PG C-399
NC PE Firm License Number (if applicable effective May 1, 2009)
Po„i—A annno
(Area Code) Telephone N
Affix NC Lic
Seal

(OWO GOLDER
REPORT
Water Quality Monitoring Report
2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Submitted to:
Jaclynne Drummond, Hydrogeologist
Solid Waste Section, Division of Waste Management, NC DEQ
2090 US Highway 70
Swannanoa, NC 28778
Submitted by:
Golder Associates NC, Inc.
5B Oak Branch Drive, Greensboro, North Carol
On Behalf of:
Moore County, NC
[phone]

February 21, 2020
Distribution List
Project No. 19127453
Jaclynne Drummond, Hydrogeologist, Solid Waste Section, Division of Waste Management, NC DEQ, 2090 US
Highway 70, Swannanoa, NC 28778, [e-mail] (electronic copy only)
David Lambert, JD, MPA, Solid Waste Manager, Moore County, NC, 5227 Hwy 15-501, Carthage, NC, 28327,
d1ambert1 @moorecountync.gov (hard copy & electronic copy)
Landfill Manager, Moore County, NC, 5227 Hwy 15-501, P.O. Box 1927, Carthage, North Carolina, 28327 (hard
copy & electronic copy)
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February 21, 2020 Project No. 19127453
Executive Summary
On behalf of Moore County, Golder Associates NC, Inc. (Golder) is submitting the enclosed Water Quality
Monitoring Report (Report), which documents the results of the November 19 - 21, 2019, assessment and
corrective action water quality monitoring event, and the January 8, 2020, verification event, at the Moore County
Landfill located in Aberdeen, North Carolina.
The November 2019 water quality monitoring event was the fourth assessment monitoring event for the active
construction and demolition (C&D) landfill groundwater compliance monitoring network in accordance with the
approved Assessment Monitoring Work Plan. Groundwater samples collected from assessment monitoring wells
(i.e., active C&D groundwater monitoring wells) during the November 2019 event were analyzed for Appendix I
constituents plus previously detected Appendix II constituents (naphthalene and sulfide) and the indicator
parameters required by the NC Department of Environmental Quality (DEQ) for C&D landfills [e.g., chloride,
manganese, sulfate, iron, alkalinity, total dissolved solids (TDS), and tetrahydrofuran].
During the November 2019 water quality monitoring event, groundwater samples were also collected from
monitoring wells associated with the upgradient closed municipal solid waste (MSW) landfill which is currently in
corrective action. Per the currently approved Water Quality Monitoring Plan (HDR, July 2006) for the site with the
exception of MW-8, all samples from the monitoring wells in the MSW compliance network are considered
performance (i.e., MNA) monitoring wells and are currently analyzed for Appendix I volatile organic constituents
(VOCs), Resource Conservation and Recovery Act (RCRA) metals, and an approved suite of MNA parameters
(which includes chloride, ethane, ethene, methane, nitrate, sulfate, sulfide, total alkalinity, and total organic
carbon). In addition, several active C&D monitoring wells including MW-4, MW-5, MW-11SR, MW-14, and
MW-17S are also sampled for the same suite of MNA parameters. Samples from monitoring well MW-8 are
analyzed for VOCs listed in Appendix I and RCRA metals.
Surface water and groundwater samples from both facilities were also analyzed for 1,4-dioxane per the May 29,
2018, memorandum from the NC DEQ. During the November 2019 water quality monitoring event, four surface
water samples were collected and analyzed for Appendix I VOCs listed and RCRA metals. A private water supply
well located north of the landfill at the Blake residence (an adjacent property) was sampled and analyzed for
Appendix I VOCs and RCRA metals.
Three (3) inorganic constituents (iron, manganese, and vanadium) were detected at concentrations that exceeded
their respective NC 2L Groundwater Standards in samples collected from one or more downgradient C&D
monitoring wells during the November 2019 water quality monitoring event. Vanadium was detected at estimated
concentrations below the practical quantitation limit (PQL) but above the groundwater standard. In general, the
concentrations of detected inorganic constituents during the November 2019 sampling event are similar to historic
results for the facility.
Two (2) Appendix I organic constituents (benzene and vinyl chloride) were detected in samples from one or more
downgradient monitoring C&D monitoring wells at concentrations that exceeded their respective NC 2L
Groundwater Standards during this sampling event. Additionally, 1,4-dioxane was detected at concentrations
above the NC 2L Groundwater Standard in samples from downgradient wells during this event; this constituent
was analyzed per the May 30, 2018, memorandum and is not part of the facility permit -required testing.
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February 21, 2020 Project No. 19127453
As presented, one (1) inorganic constituent (arsenic) was detected at concentrations exceeding the NC 2L
Groundwater Standard and PQL in samples collected from one or more downgradient MSW monitoring wells
during the November 2019 water quality monitoring event.
Three (3) Appendix I organic constituents (benzene, 1,4-dichlorobenzene, and vinyl chloride) were detected at
concentrations exceeding their respective NC 2L Groundwater Standards in samples collected from one or more
downgradient MSW monitoring wells during this monitoring event. Additionally, 1,4-dioxane was detected at
concentrations above the NC 2L Groundwater Standard in samples from downgradient MSW monitoring wells
during this event. This constituent was analyzed per the May 30, 2018, memorandum and is not part of the facility
permit -required testing. As presented, a verification re -sampling event was conducted on January 8, 2020 due to
an anomalous concentration of benzene detected in sample from MW-15R during the November 2019 sampling
event; the verification results did not confirm the benzene concentration.
Four (4) surface water monitoring points were sampled during the November 2019 monitoring event. One (1)
organic constituent (1,4-dioxane) was detected at quantifiable concentration above the surface water standard in
samples collected from SW-1, SW-3, and SW-4 during the November 2019 water quality monitoring event.
In general, VOC concentrations in groundwater at the site are declining and the number of constituents with
detected concentrations above the applicable groundwater standards in the downgradient groundwater monitoring
network are decreasing. As presented and based on the results summarized herein, Moore County plans to
petition the SWS to return to a Detection Monitoring Program [15A NCAC 13B .0545(b)(9)] at the active C&D
landfill through the submittal of an ASD addendum. Based on available data, impacts observed in groundwater at
the C&D site appear to originate from the upgradient closed, unlined MSW landfill, which is currently in corrective
action.
The changes included in the recent Water Quality Monitoring Plan (Golder, 2019) and approved by NC DEQ in a
communication dated January 2, 2020, will be incorporated into the next monitoring event (tentatively scheduled
for April 2020). Based on the declining COC concentrations in groundwater, the County plans to continue with
MNA unless an increase in VOC concentrations is observed or directed to proceed to an alternate groundwater
remedy (i.e., Phase 11) by NC DEQ.
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February 21, 2020 Project No. 19127453
Table of Contents
EXECUTIVE SUMMARY
1.0 INTRODUCTION.............................................................................................................................................1
1.1 Site Description and Background.........................................................................................................1
1.2 Compliance Monitoring History ............................................................................................................1
1.3 Hydrogeologic Setting..........................................................................................................................4
2.0 FIELD PROGRAM, MONITORING RESULTS, AND DISCUSSION.............................................................5
2.1 Visual Inspection Program...................................................................................................................5
2.2 Monitoring Well Network and Groundwater Elevation Measurements................................................5
2.3 November 2019 Water Quality Monitoring Event.................................................................................6
2.4 Laboratory Analysis Program...............................................................................................................7
2.5 January 2020 Verification Event..........................................................................................................7
3.0 LABORATORY AND FIELD QA/QC..............................................................................................................8
4.0 DATA EVALUATION......................................................................................................................................8
4.1
NC Groundwater Quality Standard Comparisons — C&D Landfill........................................................8
4.2
NC Groundwater Quality Standard Comparisons — MSW Landfill.......................................................9
4.3
NC Surface Water Quality Comparisons — C&D & MSW Landfills......................................................9
4.4
Alternate Source for Arsenic..............................................................................................................10
4.5
Monitored Natural Attenuation Evaluation.........................................................................................10
5.0 CONCLUSIONS............................................................................................................................................11
6.0 REFERENCES
..............................................................................................................................................11
TABLES
Table 1 Summary of Historical Groundwater Elevation Data
Table 2 Summary of Estimated Horizontal Groundwater Flow Velocities
Table 3 Summary of Groundwater Monitoring Well Construction Information
Table 4 Summary of Historical Groundwater Monitoring Results (Detected Constituents)
Table 5 Summary of Historical Groundwater Field Parameters
Table 6 Summary of Historical Surface Water Monitoring Results (Detected Constituents)
Table 7 Summary of Historical Surface Water Field Parameters
Table 8 Summary of Historical Monitored Natural Attenuation Results
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February 21, 2020
Table 9
DRAWINGS
Drawing 1
Drawing 2
FIGURES
Figure 1
Figure 2
Figure 3
Figure 4
Figure 5
APPENDICES
Appendix A
Appendix B
Project No. 19127453
Evaluation of Converging Lines of Evidence for Reductive Biological Attenuation
Groundwater Surface Contour Map (November 19, 2019)
Recent VOC NC 2L Exceedances (November 2019)
MW-4 EPA Natural Attenuation Screening Protocol Worksheet
MW-6 EPA Natural Attenuation Screening Protocol Worksheet
MW-11SR EPA Natural Attenuation Screening Protocol Worksheet
MW-15R EPA Natural Attenuation Screening Protocol Worksheet
BIOCHLOR Results Summary
Groundwater and Surface Water Field Forms
November and January 2020 Groundwater and Surface Water Certificates -of -Analysis, Chain -of -
Custody Forms, and Laboratory Data Reviews
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February 21, 2020 Project No. 19127453
1.0 INTRODUCTION
This report summarizes the water quality monitoring results from the second semi-annual 2019 water quality
monitoring event at the Moore County Landfill conducted November 19 - 21, 2019, and a verification re -sampling
event conducted on January 8, 2020. The Moore County Landfill is comprised of two waste disposal areas: the
active construction and demolition (C&D) landfill located on the western side of the facility and the closed
municipal solid waste (MSW) landfill located on the eastern side of the facility. The facility is owned and operated
by Moore County (the County) under North Carolina (NC) Solid Waste Permit No. 63-01 issued by the North
Carolina Department of Environmental Quality [NC DEQ, formerly known as the NC Department of Environment
and Natural Resources (NC DENR)].
1.1 Site Description and Background
The physical location of the Moore County Landfill is shown on the topographic map inlay on Drawing 1. The
Moore County Landfill is located in the southwestern part of the Moore County between the towns of Pinehurst
and Aberdeen, NC. The site is accessed from State Highway 5, located to the east of the facility. The facility is
bound to the west by Horse Creek and to the north and south by unnamed tributaries of Horse Creek. The
location of these surface water features is shown on Drawing 1. As presented on Drawing 1, topographic surface
elevations at the facility range from approximately 460 feet above mean sea level (AMSL) along the eastern
portion of the closed MSW landfill, to approximately 350 feet AMSL in the southwestern portion of the facility. The
site is surrounded predominantly by wooded, agricultural, or rural residential properties.
As presented, the Moore County Landfill is located on approximately 314 acres and contains a closed MSW
landfill unit, an active C&D landfill unit, and several closed land clearing & inert debris (LCID) units. In conjunction
with Moore County, Republic Services of NC, LLC operates a solid waste transfer station located on the
southwestern portion of the property. The MSW landfill accepted waste from approximately 1968 to 1993 and
was closed prior to October 1993, with final closure approval in December 1996; the County expressed their intent
to comply with post -closure monitoring regulations in January 1997. The MSW landfill area encompasses
approximately 60 acres, 12 of which have a clay cap. The County began transferring MSW in 1993. The County
temporarily stockpiled C&D waste from approximately 1993 to 1996, until the current C&D landfill was permitted
and built (HDR, 2005).
1.2 Compliance Monitoring History
The first water quality monitoring event at the facility was conducted in June 1987 on five monitoring wells (MW-1
through MW-5). Monitoring well MW-5 acts as the facility background well and is located upgradient of the current
C&D landfill. Monitoring wells MW-1 through MW-4 were the downgradient monitoring wells in the original
groundwater monitoring network. Monitoring wells MW-6 through MW-9 were added in March 1995 to monitor the
area between the MSW and the C&D landfill.
Groundwater corrective action was initiated voluntarily due to concerns of off -site migration of volatile organic
compounds (VOCs) detected in groundwater samples and methane gas. According to available records,
concerns of off -site migration of VOCs were first expressed by the NC DEQ in a letter dated January 23, 1996. A
private water supply well at the Blake residence (PW-1), located upgradient of the facility, was added to the
groundwater monitoring network in 1996, along with upstream and downstream surface water monitoring points
(SW-2 and SW-1, respectively). Additional monitoring wells were installed in September 1996 to delineate the
nature and extent of groundwater impacts and to serve as monitoring points for the C&D facility. The monitoring
wells installed in September 1996 included MW-11 S/D, MW-12S/D, MW-13S/D, and MW-14. Monitoring well
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February 21, 2020 Project No. 19127453
MW-14 was installed upgradient of the C&D landfill (between the MSW and the C&D landfill) and was intended to
act as the upgradient monitoring well for the C&D landfill (to differentiate groundwater impacts from the MSW
landfill). Monitoring wells MW-11S/D, MW-12S/D, and MW-13S/D were to act as the downgradient monitoring
network for the C&D landfill. Monitoring wells MW-16S/D were later installed to replace the downgradient
monitoring wells MW-12S/D, which were abandoned during an expansion of the C&D facility.
In November 1999, a work plan was submitted to NC DEQ by HDR Engineering Inc. of the Carolinas (HDR) to
address off -site groundwater and methane migration concerns. After revisions, the work plan was initiated in
March 2000 and water quality assessment activities were commenced. A clay confining unit was identified at
depth, which was reported to limit vertical groundwater contamination. In January 2005, NC DEQ requested that
Moore County complete an assessment of corrective measures (ACM) and select a remedy in accordance with
15A NCAC 2L .0106. HDR submitted the ACM in July 2005 with monitored natural attenuation (MNA) as the
primary proposed remedy with a contingency plan for active landfill gas (LFG) remediation if increasing trends in
VOCs were observed in groundwater. NC DEQ approved the recommendations in the ACM on November 21,
2005; however, they did not require a public hearing, as this was not required for this facility under the applicable
regulations (HDR, 2005). In 2005, a shallow trench vent network consisting of a trench and 12 passive LFG vents
were installed to address LFG migration concerns; this network was expanded with 12 additional LFG vents in
2007. Three in -waste passive gas vents (GV-30, GV-31, and GV-32) were installed in February 2014 as part of
the Contingency Plan Update and Implementation Plan -Revised approved by NC DEQ on June 5, 2013.
A revised Water Quality Monitoring Plan was prepared in July 2006 and approved October 13, 2006, by NC DEQ.
This Plan includes monitoring of NC Appendix I VOCs and RCRA metals for all groundwater and surface water
monitoring points, as well as "performance monitoring" (i.e., MNA) parameters for selected wells. In a letter from
the NC DEQ dated April 18, 2008, Moore County received permission to eliminate hydrogen, carbon dioxide, and
volatile fatty acids from the semi-annual monitoring list, and complete groundwater modeling annually. This letter
also specified that the County collect the full suite of "performance monitoring parameters" in April and October
2011, and present a MNA Corrective Action Evaluation Report (CAER) after completion of the October 2011
sampling event. The CAER was submitted in May 2012 and NC DEQ granted the County permission to continue
MNA for another five-year period at the end of which the County was required to submit another. In order to
better assess surface water quality and potential offsite plume migration two additional surface water points
(SW-3 and SW-4) were added to the compliance monitoring network upon approval of the CAER in May 2012.
Moore County met with NC DEQ on March 10, 2016 to discuss groundwater impacts at the site and the
effectiveness of the previously implemented corrective actions at the facility. In this meeting and in a follow-up,
correspondence sent from NC DEQ on March 14, 2016, the Solid Waste Section (the Section) requested that
Moore County commence assessment monitoring at the C&D landfill or submit an alternate source demonstration
(ASD) to demonstrate the impacts observed in the C&D landfill monitoring network were from a source other than
the C&D landfill. On February 28, 2017, the County submitted an ASD for the Active C&D Landfill, identifying the
upgradient closed MSW landfill as the source of VOCs at downgradient C&D wells.
In two letters dated September 28, 2017, the NC DEQ declined to issue a determination on the ASD for the Active
C&D Landfill and requested Moore County implement landfill gas and groundwater corrective action at the closed
MSW landfill, as well as commence assessment monitoring as detailed in 15A NCAC 13B .0545 at the active
C&D landfill. The County submitted a response to these communications on October 26, 2017 and met with NC
DEQ on November 30, 2017. Following this meeting, Moore County submitted a letter on December 6, 2017
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February 21, 2020 Project No. 19127453
confirming the County's intention to comply with the requests of NC DEQ and requesting an extension to comply.
This request was approved by NC DEQ on December 11, 2017.
Following the November 30, 2017 meeting with NC DEQ, the County submitted a 2nd CAER (detailing MNA
corrective action from April 2012 — October 2016), a Landfill Gas Remediation Plan, a Groundwater Corrective
Action Milestone Schedule (including the submission of the NC Solid Waste .0500 Groundwater Corrective Action
Application), and an Assessment Monitoring Work Plan.
In accordance with the Assessment Monitoring Work Plan, (approved by NC DEQ in a January 23, 2018,
correspondence) replacement wells were installed for monitoring wells MW-11 S, MW-11 D, and MW-15 prior to
the June 2018 water quality monitoring event. As approved, the replacement wells were sampled during the first
assessment monitoring event for the active construction and demolition (C&D) landfill groundwater compliance
monitoring network in June 2018. Groundwater samples collected from assessment monitoring wells (i.e., active
C&D groundwater monitoring wells) during the June 2018 event were analyzed for the constituents listed in
Appendix II and the indicator parameters required by NC DEQ for C&D landfills (e.g., chloride, manganese,
sulfate, iron, alkalinity, total dissolved solids (TDS), and tetrahydrofuran. In addition, to further assess whether the
groundwater impacts seen at the C&D landfill are attributable to the upgradient MSW landfill, monitoring wells
MW-6 and MW-7 were also analyzed for Appendix II constituents.
On February 20, 2019 in a letter submitted to NC DEQ by Golder Associates NC, Inc. (Golder) on behalf of Moore
County, a request was made to decommission monitoring wells MW-16S and MW-16D and replace them in the
groundwater monitoring network with the MW-17S an MW-17D which were installed recently in conjunction with
the permitting of Cell VI. The request was approved by NC DEQ in a letter dated February 22, 2019. Monitoring
wells MW-16S/D were last sampled in April 2019 prior to decommissioning on May 17, 2019. The November
2019 sampling event was the first sampling event in which monitoring wells MW-17S/D were sampled.
During the November 2019 water quality monitoring event, groundwater monitoring was conducted at the closed
MSW landfill in accordance with the approved Water Quality Monitoring Plan and Phase I of the Groundwater
Corrective Action Milestone Schedule which was approved by NC DEQ on February 13, 2018. Phase I of the
Groundwater Corrective Action Milestone Schedule included the following activities:
Installation of the methane cut-off trench to the south of MW-15 (completed November 2, 2018)
Replacement of MW-15 with MW-15R (completed June 1, 2018)
Conversion of MW-15 to a compliance methane monitoring well (completed December 7, 2018)
Continuation of MNA (as detailed in the approved Water Quality Monitoring Plan).
Per the approved Water Quality Monitoring Plan (HDR, July 2006) for the site, with the exception of MW-8, all
samples from the monitoring wells in the MSW compliance network are considered MNA performance monitoring
wells and are currently analyzed for VOCs listed in Appendix I, Resource Conservation and Recovery Act (RCRA)
metals, and an approved suite of MNA parameters (which includes chloride, ethane, ethene, methane, nitrate,
sulfate, sulfide, total alkalinity, and total organic carbon). In addition, several active C&D monitoring wells
including MW-4, MW-5, MW-11 SR, MW-14, and MW-17S are also sampled as MNA performance wells for the
same suite of MNA parameters. Samples from monitoring well MW-8 are currently only analyzed for VOCs listed
in Appendix I and RCRA metals.
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February 21, 2020 Project No. 19127453
In accordance with the NC Solid Waste Rules and the approved Assessment Monitoring Work Plan, upon
completion of the fourth assessment background sampling event (i.e., the November 2019 sampling event), a
report will be submitted to NC DEQ in accordance with 15A NCAC .0545(b)(7) to be sealed by a licensed
geologist as part of the semi-annual report. The concentrations of constituents listed in Appendix II for each
background monitoring event will be compared to established 15A NCAC 02L. 0202 groundwater quality
standards (NC 2L Groundwater Standards) and interim maximum allowable concentration standards (IMAC
Standards). In the case of metals, comparisons will also be made to background concentrations, as appropriate.
Pending the results of assessment background sampling, the County may petition the SWS to return to a
Detection Monitoring Program [15A NCAC 13B .0545(b)(9)] through submittal of an ASD addendum, request
selective Assessment Monitoring for a subset of wells impacted by VOCs and/or a subset of constituents listed in
Appendix II for analysis [15A NCAC .0545(b)(6)], or will begin the process to implement an ACM for landfill gas to
groundwater impacts [15A NCAC 13B .0545(c)] per the approved Assessment Monitoring Work Plan. The results
of this evaluation are presented in Section 5.0 of this report.
1.3 Hydrogeologic Setting
The facility is located in the inner Coastal Plain Physiographic Province of NC. The geologic units of this region
are relatively young, dating from the Cretaceous to the Tertiary period (NCGS, 1985). The site is underlain by
sands, silts, and clays of the Middendorf Formation, which generally consist of intercalated, lenticular, thick -
bedded, light-colored sands and clays (mudstones) with local concentrations of clay-clast conglomerates (NCGS,
1985 and Sohl and Owens, 1991).
The uppermost groundwater beneath the facility is present in a shallow, unconfined aquifer comprised of sands
mixed with thin clay seams and larger seams of fine sand. The uppermost aquifer at the site is approximately 55
feet thick and underlain by a clay confining layer (HDR, 2005). Groundwater occurs at depths varying from
approximately 5 to 38 feet below ground surface across the entire site. Measurements of groundwater elevations
obtained during the November 2019 water quality monitoring event are summarized in Table 1 and were used to
prepare the groundwater surface contour map presented on Drawing 1.
Surface water and groundwater at the site generally flows to the west and southwest toward Horse Creek, which
is located along the western property boundary. Limited surface water and groundwater flows to the north and
south to unnamed tributaries of Horse Creek located along the northern and southern property boundaries.
Based on the November 19, 2019 groundwater surface contour map, the hydraulic gradient in the shallow aquifer
underlying the site, as measured along the conceptual flow path shown on the contour map was calculated to be
approximately 0.018 feet per foot. Groundwater velocities were calculated using a hydraulic conductivity of
3.19 x 10-3 centimeters per second (cm/s), which is the average hydraulic conductivity for the uppermost aquifer
as calculated from slug tests performed at the facility. An effective porosity of 0.35 was selected for the shallow
aquifer at the site based on typical effective porosity values for similar soil types (HDR, 2005). The groundwater
surface contour map and interpreted flow directions are generally consistent with previously submitted
interpretations for this facility.
Using the above values, the estimated rate of groundwater flow for the uppermost aquifer beneath the facility was
calculated using the following modified Darcy equation:
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February 21, 2020 Project No. 19127453
where V9W = average linear velocity (feet/year), K = hydraulic conductivity (feet/year), i = horizontal hydraulic
gradient, and ne = effective porosity.
The average estimated linear groundwater flow velocity under the waste management units is approximately 174
feet/year, which is slower than previous estimates (Table 2). The inconsistency in the current calculated
groundwater flow velocity with previous estimates is due to a change in the hydraulic conductivity value used.
The hydraulic conductivity value selected for this calculation incorporates new slug test data from test performed
in correlation to the recent submittal of a Design Hydrogeologic Report (Golder, 2019) which was prepared for the
proposed Cell VI horizontal expansion. The range of groundwater flow is expected to vary depending on
topographic and hydrogeologic conditions. The linear velocity equation above makes the simplified assumptions
of a homogeneous and isotropic aquifer. Therefore, this equation represents a presumptive estimated value for
the uppermost aquifer and does not account for heterogeneous and/or anisotropic conditions that may be present
in the uppermost aquifer at the facility.
FIELD PROGRAM, MONITORING RESULTS, AND DISCUSSION
Field activities conducted for the November 2019 sampling event are discussed in the following sections
2.1 Visual Inspection Program
In order detect a potential release at the earliest possible time; a visual inspection program is used at the Moore
County closed MSW and active C&D landfills by the sampling personnel. This program includes the examination
of physical indicators such as potential water table mounding beneath the waste management unit, visible signs of
stress in the onsite biological communities, visible signs of leachate migration (i.e., leachate seeps), unexplained
changes in soil characteristics, and any other change to the environment due to the waste management unit.
During the November 2019 compliance monitoring event, no physical indicators of a potential release were
observed in the vicinity of the waste management areas by Golder sampling personnel.
2.2 Monitoring Well Network and Groundwater Elevation Measurements
As presented, there are two groundwater monitoring well networks at the site - one network to monitor
groundwater beneath the active C&D landfill and one to monitor groundwater beneath MSW landfill. One
background monitoring well, MW-5, provides background data for both groundwater monitoring networks. The
approved active C&D landfill groundwater monitoring network consists of eight downgradient monitoring wells
(MW-4, MW-11SR, MW-11 DR, MW-13S, MW-13D, MW-17S, and MW-17D) and one additional upgradient
monitoring well (MW-14) which monitors groundwater between the adjacent upgradient MSW landfill and the C&D
landfill. The closed MSW landfill groundwater monitoring network consists of eight downgradient monitoring wells
(MW-1, MW-2, MW-3, MW-6, MW-7, MW-8, MW-9, and MW-15R). In addition, four C&D monitoring wells (MW-4,
MW-11 S, MW-14, and MW-17S) are also used as "performance" or "MNA" monitoring wells to assess
groundwater impacts from the MSW landfill. Available monitoring well construction information for each
groundwater monitoring well is summarized on Table 3 and the well locations are shown on Drawing 1.
The groundwater monitoring well locations were selected to yield groundwater samples representative of the
conditions in the uppermost aquifer underlying the facility; to monitor for potential releases from the landfill units;
and to assess the progress of natural attenuation. As presented, two upstream (SW-1 and SW-2) and two
downstream (SW-3 and SW-4) surface water monitoring points, and one private water well (PW-1) are also
monitored in accordance with the approved monitoring plan.
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February 21, 2020 Project No. 19127453
Depth -to -water measurements are recorded to the nearest 0.01 foot prior to initiating groundwater purging and
sampling activities. The respective groundwater elevations for this event as well as historical groundwater
elevation data are presented in Table 1.
As presented, recent groundwater elevation data for the groundwater monitoring well network indicate that the
hydraulic head level in the uppermost aquifer beneath the facility is fairly consistent, with temporal variation from
the long-term average limited to approximately 3 - 12 feet (plus or minus). The range in fluctuation appears to be
greatest in the upgradientisidegradient monitoring wells (e.g., MW-5). The range of water table fluctuation in the
downgradient compliance wells varies depending on their location, relative to the hydraulic discharge boundary.
2.3 November 2019 Water Quality Monitoring Event
Personnel from Golder mobilized to the facility from November 19 - 21, 2019, to purge and sample the seventeen
(17) groundwater monitoring wells, to sample four (4) surface water monitoring points, and to sample the Blake
residence water well (i.e., PW-1).
The monitoring wells were purged and sampled using a portable peristaltic or submersible bladder pump and
micro -purge procedures. During the micro -purging process stabilization measurements of temperature, pH,
specific conductivity, turbidity, dissolved oxygen, and oxidation reduction potential (ORP) were recorded on
approximately 2 to 5-minute intervals, depending on the flow cell volume, system volume, and well yield.
Generally, the purge rate for each well was matched to the yield of the monitoring well, as determined by
continuously monitoring the depth to the water. Purge rates of up to 300 milliliters per minute were used during
the November 2019 sampling event. Each monitoring well was purged until stabilization of the water quality
parameters.
Prior to sampling, the laboratory -supplied sample containers were prepared. Each sample container was labeled
with the sample identification number, sampling personnel, date and time of sample collection, project name and
number, and requested chemical analyses. The "performance" or "MNA" monitoring wells identified above were
also analyzed for ferrous iron in the field using a HACH field measurement kit.
The required groundwater samples were collected directly from the peristaltic or submersible portable pump
discharge tubing into the pre -labeled, laboratory -supplied, pre -preserved sample containers after purging was
completed based on stabilization of the water quality parameters. After collection, the samples were placed in a
cooler on ice, under chain -of -custody control. A summary of the November 2019 groundwater analytical results
as well as a summary of the historical groundwater analytical results for the Moore County Landfill are presented
in Table 4.
The completed groundwater sampling logs are presented in Appendix A. Included in each log is a description of
the sampling equipment, methods, location, field observations, and a record of the water quality measurements.
A summary of the stabilized groundwater field parameters recorded at the time of sampling is included in this
report as Table 5.
The surface water samples were collected directly from the stream, by lowering the sample container into the
stream flow with the bottle opening facing downstream, the bottles were filled carefully to prevent overflow and to
minimize turbidity. Measurements of pH, specific conductivity, temperature, turbidity, dissolved oxygen, and
oxygen reduction potential were measured directly from the stream and recorded during the collection of the
surface water samples. After collection, the samples were placed in a cooler on ice, under chain -of -custody
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February 21, 2020 Project No. 19127453
control. A summary of the November 2019 surface water analytical results as well as a summary of the historical
surface water analytical results for the Moore County Landfill are presented in Table 6.
The surface water sampling logs are presented in Appendix A. Included in each log is a description of the
sampling equipment, methods, sample location, field observations, and water quality measurements. A summary
of the field parameters recorded at the time of surface water sampling is included in this report as Table 7.
The sample collected from the Blake residence water well (PW-1) was collected from an outside spigot at the well
house by allowing the water to purge for approximately 5 minutes before the sample bottles were filled. As with
the groundwater and surface water sampling, a sampling log was completed at the time of sampling describing
the sampling equipment, methods, sample location, field observations, and water quality measurements. The
completed sampling log is also included in Appendix A and the field parameters recorded at the time of sampling
are summarized on Table 5.
2.4 Laboratory Analysis Program
The November 2019 groundwater and surface water samples were submitted to Environmental Conservation
Laboratories, Inc. (ENCO) of Cary, NC under chain -of -custody control for analysis. As presented, in accordance
with the Assessment Monitoring Work Plan groundwater samples collected from the assessment monitoring wells
(i.e., active C&D groundwater monitoring wells) during the November 2019 event were analyzed for the
constituents listed in Appendix I and detected Appendix II constituents as well as the indicator parameters
required by NC DEQ for C&D landfills [e.g., chloride, manganese, sulfate, iron, alkalinity, total dissolved solids
(TDS), and tetrahydrofuran].
Per the currently approved Water Quality Monitoring Plan (HDR, July 2006) for the site with the exception of
MW-8, all samples from the monitoring wells in the MSW compliance network are considered performance (i.e.,
MNA) monitoring wells and are currently analyzed for Appendix I VOCs, Resource Conservation and Recovery
Act (RCRA) metals, and an approved suite of MNA parameters (which includes chloride, ethane, ethene,
methane, nitrate, sulfate, sulfide, total alkalinity, and total organic carbon). In addition, several active C&D
monitoring wells including MW-4, MW-5, MW-11 SR, MW-14, and MW-17S are also sampled for the same suite of
MNA parameters. Samples from monitoring well MW-8 are analyzed for Appendix I VOCs and RCRA metals.
Surface water and groundwater samples were also analyzed for 1,4-dioxane per the May 29, 2018, memorandum
from the NC DEQ. Per the laboratory receipt summaries, which can be found at the end of each laboratory
certificate -of -analysis in Appendix B, each sample was received at the laboratory in good condition and was
properly preserved.
2.5 January 2020 Verification Event
Golder personnel mobilized for a second time to the facility on January 8, 2020 to re -sample MW-15R. The
verification re -sampling event was conducted to verify an anomalous concentration of benzene observed in
monitoring well MW-15R during the November 2019 sampling event. The verification samples from MW-15R
were collected utilizing the same methods and procedures as were used during the November 2019 sampling
event. After the verification sample was collected, the samples were placed in a cooler on ice, under chain -of -
custody control, and sent via carrier to ENCO laboratory in Cary, NC for analysis. A copy of the sampling log is
included in Appendix A. As with the November 2019 sampling event, included on the sampling log is a
description of the sampling equipment, sampling method, field observations, location, and water quality
measurements.
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February 21, 2020 Project No. 19127453
3.0 LABORATORY AND FIELD QA/QC
To provide quality assurance and quality control (QA/QC), a field blank was collected by Golder personnel during
the November 2019 water quality monitoring event. During the initial sampling event in November 2019 and
during the verification sampling event performed in January 2020, a laboratory -prepared trip blank accompanied
the volatile organic sample containers throughout the trip from the laboratory, to the site, and eventually back to
the laboratory for analysis. ENCO analyzed the field blank for Appendix I VOCs plus Detects and RCRA metals,
and the trip blanks for Appendix I VOCs. Reviews of the laboratory data were performed by Golder personnel and
are included in Appendix B.
DATA EVALUATION
The results of the analytical data evaluations are presented in the following sections. A summary of the
November 2019 as well as the available historical analytical results is included in Table 4.
NC Groundwater Quality Standard Comparisons — C&D Landfill
Three (3) inorganic constituents (iron, manganese, and vanadium) were detected at concentrations that exceed
their respective NC 2L Groundwater Standard or IMAC in samples collected from one or more downgradient C&D
monitoring wells during the November 2019 water quality monitoring event. Below is a summary of the inorganic
exceedances of the NC 2L Groundwater Standards (or IMACs) within the active C&D landfill groundwater
monitoring network during the November 2019 sampling event.
..
Iron
300 ug/L
.. ..
MW-41 MW-11 SR, MW-11 DR, MW-13S, MW-13D, MW-142, MW-17S
Manganese
50 ug/L
MW-4, MW-11SR, MW-11DR, MW-13S, MW-142, MW-17S
Vanadium
0.3 ug/L (IMAC)
MW-4
1. ug/L = micrograms per liter
2. MW-14 is located upgradient of the C&D landfill (between the MSW and the C&D landfill)
Vanadium was detected at an estimated concentration above the IMAC but below the PQL. Per 15A NCAC 02L
.0202 (b)(1), "where the standard for a substance is less than the practical quantitation limit (PQL), the detection
of that substance at or above the PQL constitutes a violation of the standard." As referenced, the vanadium
concentration detected during the November 2019 sampling event does not constitute a violation of the standard.
Two (2) organic constituents (benzene and vinyl chloride) listed in Appendix I, and one additional organic
constituent (1,4-dioxane), were detected in samples from one or more downgradient monitoring wells at
concentrations exceeding their respective NC 2L Groundwater Standards during this monitoring event. Below is a
summary of the organic exceedances of the NC 2L Groundwater Standards within the active C&D landfill
groundwater monitoring network during the November 2019 sampling event.
constituent NC 2L or NC 2L Groundwater Standard - Exceedance Location
IMAC
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February 21, 2020
Project No. 19127453
F1stituen �Jmff
Vinyl Chloride
0.03 ug/L
Groundwater StandardExceedance Location
MW-11SR, MW-11DR, MW-13S, MW-14'
1,4-Dioxane
3.0 ug/L
MW-11SR, MW-11DR, MW-13S, MW-141, MW-17D
1. MW-14 is located upgradient of the C&D landfill (between the MSW and the C&D landfill)
4.2 NC Groundwater Quality Standard Comparisons — MSW Landfill
As presented, one (1) inorganic constituent (arsenic) was detected at a concentration that exceeded the NC 2L
Groundwater Standard in samples collected from one or more downgradient MSW monitoring wells during the
November 2019 water quality monitoring event. Below is a summary of the inorganic exceedances of the NC 2L
Groundwater Standard within the closed MSW landfill groundwater monitoring network during the November 2019
sampling event.
Three (3) organic constituents (benzene, 1,4-dichlorobenzene, and vinyl chloride) listed in Appendix I, and one
additional organic constituent (1,4-dioxane) were detected at concentrations exceeding their respective NC 2L
Groundwater Standards in samples collected from one or more downgradient MSW monitoring wells during the
November 2019 monitoring event. As presented, a verification re -sampling event was conducted in January 2020
to verify an anomalous concentration of benzene observed in monitoring well MW-15R during the November 2019
sampling event. The results of the verification re -sampling of MW-15R did not confirm the anomalous
concentration; however, benzene was also detected above the NC 2L Groundwater Standard during the
verification sampling event. The following is a summary of the organic exceedances of the NC 2L Groundwater
Standard with the closed MSW landfill groundwater monitoring network during the November 2019 sampling
event.
Benzene
NC 2L or
IMAC
1.0 ug/L
NC 2L Groundwater ..
StandardConstituent
IF
MW-6, MW-7, MW-8, MW-9, MW-15R
1,4-Dichlorobenze
6.0 ug/L
MW-8
Vinyl Chloride
0.3 ug/L
MW-6, MW-7, MW-15R'
1,4-Dioxane
3.0 ug/L
MW-2, MW-7, MW-8, MW-9
1. Denotes estimated concentration below the PQL
4.3 NC Surface Water Quality Comparisons — C&D & MSW Landfills
As presented, four surface water monitoring points were sampled during the November 2019 monitoring event.
One organic constituent (1,4-dioxane) was detected at quantifiable concentration above the surface water
standard in samples collected from SW-1, SW-3, and SW-4 during the November 2019 monitoring event; this
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February 21, 2020 Project No. 19127453
constituent was analyzed per the May 30, 2018, memorandum and is not part of the facility permit -required
testing.
4.4 Alternate Source for Arsenic
Based on previously collected data for this site, arsenic appears to be naturally occurring. The site -specific soil
data presented in the Second Semi -Annual 2016 Water Quality Monitoring Report indicate that concentrations
detected in naturally occurring soils on site can account for those measured in groundwater samples. Therefore,
data support that above -standard concentrations of arsenic are naturally occurring.
4.5 Monitored Natural Attenuation Evaluation
As presented as part of the corrective action program for the closed MSW landfill, additional "performance" or
MNA parameters are collected to document natural attention. A summary of the "performance" or MNA
parameters is included in this report as Table 8. Following each second semi-annual water quality monitoring
event, a series of select monitoring wells disseminating from the highest historical VOC concentrations (i.e.,
MW-6, MW-15) towards the hydraulic discharge feature (i.e., Horse Creek) are used to evaluate the natural
attenuation process. The select groundwater monitoring wells include MW-4, MW-6, MW-11SR, and MW-15R.
These monitoring wells were selected because of their location relative to each other and the groundwater plume.
As presented, the monitoring wells are situated along a relatively straight line parallel to groundwater flow (see
Drawing 1) and follow a path from the highest historical concentrations of VOCs towards the hydraulic discharge
feature. These select monitoring wells also correlate with the study performed by HDR in the Water Quality
Monitoring Plan (2006). The November 2019 analytical results for these select monitoring wells were evaluated
using the Environmental Protection Agency (EPA)'s natural attenuation screening protocol (1999).
To assist in the screening process the MNA results were first incorporated into Table 9 which acts as a summary
of the results and provides a basic qualitative evaluation of the potential for biological degradation (or attenuation)
of VOCs. The assimilated data was then processed quantitatively using the EPA's natural attenuation screening
protocol worksheets. Based on the EPA's screening protocol worksheets, monitoring wells MW-6, MW-11 SR,
and MW-15R received scores greater than 20, which indicates strong evidence for anaerobic biodegradation of
VOCs. Monitoring well MW-4 received a score of 11, which indicates limited evidence for anaerobic
biodegradation of VOCs (EPA, 1999). The EPA natural attenuation screening protocol worksheets are included
as Figures 1— 4.
Based on the results of the screening protocol, there is strong evidence that natural attenuation is occurring at the
site. Since there is strong evidence that natural attenuation is occurring via the biodegradation of VOCs, the
EPA's BIOCHLOR modeling software was used to simulate remediation by natural attenuation at the site. Current
and historical results from monitoring wells MW-4, MW-6, MW-11 SR, and MW-15R were input into the modeling
software. Modeling parameters for advection, dispersion, and the plume area were also input. The modeling
parameters for advection, dispersion, and the plume area were determined to be the same as previous models
performed for the site, allowing a direct comparison to previous results. A 50-year simulation period was selected
for the model, representing the time at which waste was first placed in the landfill (the original source). The
November 2019 results represent current conditions at the facility and therefore, the model was calibrated to the
current sample results by adjusting the biotransformation data within a prescribed range specified by literature
values within the BIOCHLOR program. Once the model was calibrated a forecasted model was created by
changing the simulation period to 100 years to assess the size of the contaminant plume in the future.
BIOCHLOR generates plots that compare concentrations of tetrachloroethene (PCE), trichloroethene (TCE),
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February 21, 2020 Project No. 19127453
dichloroethene (DCE), and vinyl chloride (VC) over time with no degradation to concentrations where sequential
1 st order decay is occurring. The centerline plots can be used to forecast the contaminant plume size over time.
A summary of the results of the BIOCHLOR model are provided on Figure 5.
Because PCE and TCE were not detected in samples from downgradient monitoring wells MW-4, MW-6,
MW-11SR, and MW-15R during the November 2019 monitoring event, the BIOCHLOR model could not be
calibrated; however, the absence of PCE and TCE in these downgradient samples could be considered evidence
of biodegradation. The concentration of DCE in the samples from MW-4, MW-6, MW-11SR, and MW-15R plots
on or below the 1st order sequential decay curve. In both samples, the cis-1,2-DCE variety was the prominent
form of DCE indicating that the detections represent daughter products of TCE. The centerline plot for VC shows
concentrations in samples from MW-6, MW-11S, and MW-15 plot below the 1st order sequential decay curve.
The results from these plots indicate that natural attenuation is occurring at the site and that as long as conditions
at the site continue to be strongly anaerobic, biodegradation of VOCs will continue. According to the current data,
the plume size has stabilized, as indicated by the BIOCHLOR model. There is evidence that more aerobic
conditions exist in the monitoring well furthest from the contaminant plume (MW-4). Aerobic conditions in the
furthest downgradient well are not likely to impact natural attenuation at the site as DCE and VC both degrade co -
metabolically and can be directly oxidized to carbon dioxide under aerobic conditions (EPA, 2000).
Currently, the three primary constituents -of -concern (COCs) at the site are benzene, 1,4-dichlorobenzene (1,4-
DCB), and VC. An iso-concentration map for each current COC has been included in this report as Drawing 2.
The COC 1,4-DCB was not detected above the NC 2L Groundwater Standard in groundwater at the site during
the November 2019 sampling event. Both benzene and VC typically degraded faster under the proper aerobic
conditions; however, both will degrade anaerobically if the right conditions exist. A review of the historical
concentrations of both benzene and VC show that concentrations of both COCs have decreased over time.
5.0 CONCLUSIONS
In general, VOC concentrations in groundwater at the site are declining and the number of constituents with
detected concentrations above the applicable groundwater standards in the downgradient monitoring network are
decreasing. As presented and based on the results summarized herein, Moore County plans to petition the SWS
to return to a Detection Monitoring Program [15A NCAC 13B .0545(b)(9)] at the active C&D landfill through the
submittal of an ASD addendum. It is the County's belief that impacts observed in groundwater at the site originate
from the upgradient closed MSW landfill which is currently in corrective action.
The changes included in the recent Water Quality Monitoring Plan (Golder, 2019) and approved by NC DEQ in a
communication dated January 2, 2020, will be incorporated into the next monitoring event (tentatively scheduled
for April 2020). Based on the declining COC concentrations in groundwater, the County plans to continue with
MNA unless an increase in VOC concentrations is observed or directed to proceed to an alternate groundwater
remedy (i.e., Phase II) by NC DEQ.
REFERENCES
Golder Associates NC, Inc. (Golder), Alternate Source Demonstration for Active C&D Landfill, Moore County
Construction and Demolition Landfill, NC SWP# 63-01, Submitted to NC DEQ: February 28, 2017.
Golder Associates NC, Inc. (Golder), Assessment Monitoring Work Plan, Moore County Construction and
Demolition Landfill, NC SWP# 63-01, Submitted to NC DEQ: January 5, 2018.
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February 21, 2020 Project No. 19127453
Golder Associates NC, Inc. (Golder), Corrective Action Evaluation Report, Moore County Landfill, NC SWP#
63-01, Submitted to NC DENR: May 15, 2012.
Golder Associates NC, Inc. (Golder), Groundwater Corrective Action Evaluation Report, Moore County
Landfill, NC SWP# 63-01, Submitted to NC DEQ: October 16, 2017.
Golder Associates NC, Inc. (Golder), Groundwater Corrective Action Milestone Schedule, Moore County
Closed MSW Landfill, NC SWP# 63-01, Submitted to NC DEQ: January 31, 2018.
Golder Associates NC, Inc. (Golder), Landfill Gas Remediation Plan, Moore County Closed MSW Landfill, NC
SWP# 63-01, Submitted to NC DEQ: January 31, 2018.
Golder Associates NC, Inc. (Golder), Request for Extension, Moore County Landfill, NC SWP# 63-01, Submitted
to NC DEQ: December 6, 2017.
Golder Associates NC, Inc. (Golder), Request for Monitored Natural Attenuation Parameter Modification,
Moore County Landfill, NC SWP# 63-01, Submitted to NC DENR: January 22, 2008.
Golder Associates NC, Inc. (Golder), Response to Letters Received from NC DEQ Dated September 28, 2017,
Moore County Landfill, NC SWP# 63-01, Submitted to NC DEQ: October 26, 2017.
Golder Associates NC, Inc. (Golder), Second Semi -Annual Water Quality Monitoring Report, Moore County
Landfill, NC SWP# 63-01, Submitted to NC DEQ: March 29, 2017.
Golder Associates NC, Inc. (Golder), Water Quality Monitoring Plan, Moore County Landfill, NC SWP# 63-01,
Submitted to NC DEQ: Submitted to NC DEQ: December 10, 2019.
HDR Engineering, Inc. of the Carolinas (HDR), Addendum to Plan to Address Potential Contamination, Moore
County Landfill, NC SWP# 63-01, Submitted to NC DENR: March 20, 2000.
HDR Engineering, Inc. of the Carolinas (HDR), Assessment of Corrective Measures Report, Moore County
Landfill, NC SWP# 63-01, Submitted to NC DENR: July 29, 2005.
HDR Engineering, Inc. of the Carolinas (HDR), Phase I Environmental Assessment, Moore County Landfill, NC
SWP# 63-01, Submitted to NC DENR: November 30, 1999
HDR Engineering, Inc. of the Carolinas (HDR), Water Quality Monitoring Plan, Moore County Landfill, NC
SWP# 63-01, Submitted to NC DENR: July 20, 2006.
Joyce Engineering, Inc., Contingency Plan Update and Implementation Plan - Revised, Moore County
Landfill, NC SWP# 63-01, Submitted to NC DENR: May 16, 2013.
North Carolina Department of Environment, Health, and Natural Resources (NC DEHNR), Division of Solid Waste
Management, RE: Water Quality Monitoring at Moore County Sanitary Landfill, Moore County Landfill,
NC SWP# 63-01, NC DEHNR to Moore County: January 23, 1996.
North Carolina Department of Environment and Natural Resources (NC DENR), Division of Waste Management,
RE: Request for Monitored Natural Attenuation Parameter Modification, Moore County Landfill, NC
SWP# 63-01, NC DENR to Moore County: April 18, 2008.
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February 21, 2020
Project No. 19127453
North Carolina Department of Environmental Quality (NC DEQ), Solid Waste Section, Division of Waste
Management, RE: Alternate Source Demonstration, Moore County Construction and Demolition Landfill,
NC SWP# 63-01, NC DEQ to Moore County: September 28, 2017.
North Carolina Department of Environmental Quality (NC DEQ), Solid Waste Section, Division of Waste
Management, RE: Groundwater Corrective Action and Landfill Gas Corrective Action, Moore County
Closed MSW Landfill, NC SWP# 63-01, NC DEQ to Moore County: September 28, 2017.
North Carolina Department of Environmental Quality (NC DEQ), Solid Waste Section, Division of Waste
Management, RE: Groundwater Corrective Action Milestone Schedule, Moore County Closed MSW
Landfill, NC SWP# 63-01, NC DEQ to Moore County: February 13, 2018.
North Carolina Department of Environmental Quality (NC DEQ), Solid Waste Section, Division of Waste
Management, RE: Request for Extension, Moore County Closed MSW Landfill, NC SWP# 63-01, NC DEQ
to Moore County: December 11, 2017.
North Carolina Department of Environmental Quality (NC DEQ), Solid Waste Section, Division of Waste
Management, RE: Water Quality Monitoring Report, 2nd Semiannual 2015 Sampling Event, Moore
County Landfill, NC SWP# 63-01, NC DEQ to Moore County: March 14, 2016.
North Carolina Geologic Survey (NCGS), Geologic Map of North Carolina, 1985.
Sohl, Norman F. and Owens, James P., Cretaceous Stratigraphy of the Carolinas Coastal Plain, The Geology
of the Carolinas, pages 191-220, 1991.
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February 21, 2020
Signature Page
Golder Associates NC, Inc.
Benjamin S. Draper, PG, PMP
Senior Project Geologist
BSD/RPK/bsd:
pew
Rachel P. Kirkman, PG
Associate and Senior Consulant
Engineering Lic. No. C-2862/Geology Lic. No. C-399
Project No. 19127453
Golder Associates NC, Inc. is a licensed user of the Golder trademark, and an associated operating entity.
Golder and the G logo are trademarks of Golder Associates Corporation.
gAprojectslmoore county119127453 - moore -env services fy19-201p100 - wqm & reportingt200 deliverables1252 final issued\2nd sa 2019\2020-02-21 wgmr moore county landfill.docx
4 GOLDER 14

TABLES

February 2020 Page 1 of 2 Project No. 19127453
TABLE 1
Summary of Historical Groundwater Elevation Data
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
P03/0519PO
377.00
361.00
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NINI
NI
NI
377.10
349.40
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
376.10
359.70
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
04/13/93
378.41
361.39
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
10/12/93
375.60
358.57
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
04/20/94
376.53
359.69
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
05/20/94
376.53
359.86
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
10/24/94
376.40
359.81
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
03/13/95
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
04/20/95
377.11
359.94
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
09/22/95
376.31
359.35
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
03/28/96
377.30
9.31
360.25
5.94
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
10/29/96
377.57
9.04
360.45
5.74
NI
NI
NI
NI
376.32
12.56
375.59
12.45
384.49
16.09
NI
NI
NI
NI
NI
NI
04/08/97
377.30
9.31
360.16
6.03
NI
NI
NI
NI
375.35
13.53
374.60
13.44
383.93
16.65
NI
NI
NI
NI
NI
NI
10/29/97
376.11
10.50
359.92
6.27
NI
NI
NI
NI
374.68
14.20
373.82
14.22
382.61
17.97
NI
NI
NI
NI
NI
NI
04/30/98
378.37
8.24
360.89
5.30
NI
NI
NI
NI
377.17
11.71
376.36
11.68
385.43
15.15
NI
NI
NI
NI
NI
NI
10/14/98
376.88
9.73
360.29
5.90
NI
NI
NI
NI
375.21
13.67
374.28
13.76
382.97
17.61
NI
NI
NI
NI
NI
NI
04/27/99
377.01
9.60
359.91
6.28
NI
NI
NI
NI
374.87
14.01
374.14
13.90
383.50
17.08
NI
NI
NI
NI
NI
NI
10/21/99
377.46
9.15
361.18
5.01
NI
NI
NI
NI
376.64
12.24
375.70
12.34
383.97
16.61
NI
NI
NI
NI
NI
NI
04/19/00
376.10
10.51
360.35
5.84
NI
NI
NI
NI
375.47
13.41
374.60
13.44
383.53
17.05
NI
NI
NI
NI
NI
NI
10/19/00
376.28
10.33
359.70
6.49
NI
NI
NI
NI
373.50
15.38
372.66
15.38
382.31
18.27
NI
NI
NI
NI
NI
NI
04/10/01
376.72
9.89
359.96
6.23
NI
NI
NI
NI
374.02
14.86
373.26
14.78
382.76
17.82
NI
NI
NI
NI
NI
NI
10/11/01
375.50
11.11
359.34
6.85
NI
NI
NI
NI
372.52
16.36
371.87
16.17
381.39
19.19
NI
NI
NI
NI
NI
NI
04/18/02
367.67
18.94
355.57
10.62
NI
NI
NI
NI
372.99
15.89
372.33
15.71
381.84
18.74
NI
NI
NI
NI
NI
NI
10/08/02
374.63
11.98
358.88
7.31
NI
NI
NI
NI
371.37
17.51
370.83
17.21
380.59
19.99
NI
NI
NI
NI
NI
NI
04/09/03
377.15
9.46
361.18
5.01
NI
NI
NI
NI
376.01
12.87
375.19
12.85
383.97
16.61
NI
NI
NI
NI
NI
NI
10/13/03
376.86
9.75
359.78
6.41
NI
NI
NI
NI
374.90
13.98
391.58'
9.00
NI
NI
NI
NI
NI
NI
04/26/04
376.36
10.25
359.25
6.94
NI
NI
NI
NI
373.57
15.31
371.80
16.24
382.67
17.91
NI
NI
NI
NI
NI
NI
10/25/04
376.01
10.60
359.21
6.98
NI
NI
NI
NI
376.53
12.35
382.55
18.03
NI
NI
NI
NI
NI
NI
04/04/05
376.52
10.09
359.84
6.35
NI
NI
NI
NI
374.04
14.84
373.31
14.73
382.74
17.84
NI
NI
NI
NI
NI
NI
10/04/05
375.09
11.52
358.59
7.60
NI
NI
NI
NI
372.08
16.80
381.57
19.01
NI
NI
NI
NI
NI
NI
04/28/06
375.96
10.65
360.19
6.00
NI
NI
NI
NI
373.33
15.55
372.77
15.27
382.04
18.54
NI
NI
NI
NI
NI
NI
10/09/06
375.51
11.10
359.19
7.00
NI
NI
NI
NI
372.55
16.33
371.84
16.20
381.64
18.94
NI
NI
NI
NI
NI
NI
04/23/07
379.95
6.66
360.19
6.00
NI
NI
NI
NI
374.58
14.30
373.87
14.17
383.17
17.41
NI
NI
NI
NI
NI
NI
10/30/07
375.55
11.06
359.64
6.55
NI
NI
NI
NI
372.33
16.55
371.54
16.50
381.38
19.20
NI
NI
NI
NI
NI
NI
04/21/08
376.31
10.30
359.83
6.36
NI
NI
NI
NI
374.06
14.82
373.35
14.69
383.04
17.54
NI
NI
NI
NI
NI
NI
10/06/08
376.32
10.29
359.88
6.31
NI
NI
NI
NI
374.40
14.48
373.69
14.35
382.97
17.61
NI
NI
NI
NI
NI
NI
04/13/09
376.60
10.01
360.14
6.05
NI
NI
NI
NI
374.04
14.84
373.35
14.69
382.96
17.62
NI
NI
NI
NI
NI
NI
10/13/09
375.14
11.47
358.87
7.32
NI
NI
NI
NI
371.45
17.43
370.93
17.11
381.16
19.42
NI
NI
NI
NI
NI
NI
04/26/10
376.47
10.14
359.51
6.68
NI
NI
NI
NI
374.18
14.70
373.44
14.60
382.96
17.62
NI
NI
NI
NI
NI
NI
10/19/10
376.13
10.48
359.71
6.48
NI
NI
NI
NI
373.16
15.72
372.49
15.55
382.36
18.22
NI
NI
NI
NI
NI
NI
04/18/11
375.79
10.82
359.20
6.99
NI
NI
NI
NI
372.21
16.67
371.60
16.44
381.74
18.84
NI
NI
NI
NI
NI
NI
10/10/11
374.62
11.99
359.16
7.03
NI
NI
NI
NI
370.88
18.00
370.33
17.71
380.77
19.81
NI
NI
NI
NI
NI
NI
04/17/12
374.76
11.85
358.40
7.79
NI
NI
NI
NI
371.43
17.45
370.51
17.53
381.07
19.51
NI
NI
NI
NI
NI
NI
10/09/12
374.42
12.19
360.10
6.09
NI
NI
NI
NI
371.43
17.45
370.95
17.09
380.55
20.03
NI
NI
NI
NI
NI
NI
04/15/13
374.88
11.73
359.73
6.46
NI
NI
NI
NI
372.34
16.54
371.74
16.30
381.09
19.49
NI
NI
NI
NI
NI
NI
09/30/13
375.04
11.57
359.43
6.76
NI
NI
NI
NI
373.09
15.79
372.33
15.71
381.70
18.88
NI
NI
NI
NI
NI
NI
04/16/14
376.24
10.37
360.74
5.45
NI
NI
NI
NI
374.38
14.50
373.64
14.40
382.52
18.06
NI
NI
NI
NI
NI
NI
10/15/14
<366.89
>19.72
359.87
6.32
NI
NI
NI
NI
372.14
16.74
371.55
16.49
381.27
19.31
NI
NI
NI
NI
NI
NI
04/15/15
376.26
10.35
359.72
6.47
NI
NI
NI
NI
373.68
15.20
373.00
15.04
382.47
18.11
NI
NI
NI
NI
NI
NI
10/07/15
376.21
10.40
360.99
5.20
NI
NI
NI
NI
373.38
15.50
372.75
15.29
381.83
18.75
NI
NI
NI
NI
NI
NI
04/11/16
376.42
10.19
359.98
6.21
NI
NI
NI
NI
374.47
14.41
373.66
14.38
383.19
17.39
NI
NI
NI
NI
NI
NI
11/30/16
376.24
10.37
359.93
6.26
NI
NI
NI
NI
373.75
15.13
372.92
15.12
382.65
17.93
NI
NI
NI
NI
NI
NI
04/11/17
375.99
10.62
360.00
6.19
NI
NI
NI
NI
373.25
15.63
372.53
15.51
382.18
18.40
NI
NI
NI
NI
NI
NI
12/12/17
375.34
11.27
360.02
6.17
NI
NI
NI
NI
372.10
16.78
371.52
16.52
381.45
19.13
NI
NI
NI
NI
NI
NI
06/20/18
375.43
11.18
359.49
6.70
370.24
15.89
370.27
16.09
373.51
15.37
372.75
15.29
382.28
18.30
362.14
12.02
359.45
15.11
352.61
17.36
11/27/18
377.35
9.26
361.01
5.18
371.22
14.91
371.17
15.19
375.64
13.24
374.82
13.22
383.92
16.66
363.95
10.21
363.80
10.76
353.59
6.15
04/02/19
377.03
9.58
360.66
5.53
371.18
14.95
371.13
15.23
375.47
13.41
374.66
13.38
383.94
16.64
363.46
10.70
361.54
13.02
353.55
6.42
11/19/19
375.76
10.85
360.08
6.11
370.10
16.03
370.15
16.21
372.74
16.14
372.14
15.90
381.92
18.66
361.96
12.20
362.02
12.54
352.47
7.35
MEAN
376.17
10.55
359.64
6.39
370.10
16.03
370.15
16.21
373.77
15.11
372.98
15.06
382.46
17.93
362.88
11.28
361.70
12.86
353.06
9.32
MAXIMUM
379.95
18.94
361.39
10.62
371.22
16.03
371.17
16.21
377.17
18.00
376.36
17.71
385.43
20.03
363.95
12.20
363.80
15.11
353.59
17.36
MINIMUM
367.67
6.66
349.40
5.01
370.10
14.91
370.15
15.19
370.88
11.71
370.33
11.68
380.55
9.00
361.96
10.21
359.45
10.76
352.47
6.15
G TRCJECTSNw, Co yn 127453-Moore-Env Services M9-201100-WGM&R,p,d,ng%00 CALCULATICNS12020-02-15 WOMB Tables 4 G O L D E R

February 2020 Page 2 of 2 Project No. 19127453
TABLE 1
Summary of Historical Groundwater Elevation Data
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
•
1
1
r
MI.
03/05/90
382.00
368.00
358.00
NI
NI
NI
NI
NI
NI
NI
NI
NI
03/12/91
381.90
368.30
358.30
NI
NI
NI
NI
NI
NI
NI
NI
NI
03/10/92
380.90
366.60
357.30
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
04/13/93
382.86
369.08
359.00
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
10/12/93
379.47
365.97
356.66
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
04/20/94
380.87
366.96
357.43
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
05/20/94
380.79
367.00
357.55
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
10/24/94
380.62
366.73
357.53
NI
NI
NI
NI
NI
NI
NI
NI
NI
NI
03/13/95
389.69
387.32
384.68
383.85
NI
NI
04/20/95
381.27
367.39
357.77
388.66
385.99
383.30
383.13
NI
NI
09/22/95
380.95
366.89
357.28
387.85
384.75
382.23
382.35
NI
NI
03/28/96
381.79
11.08
367.75
7.75
358.16
5.66
388.65
17.21
385.85
16.16
383.37
14.48
383.05
23.01
NI
NI
10/29/96
381.90
10.97
368.18
7.32
358.15
5.67
389.12
16.74
386.50
15.51
384.04
13.81
383.48
22.58
NI
NI
04/08/97
381.79
11.08
367.84
7.66
358.10
5.72
388.90
16.96
386.22
15.79
383.73
14.12
383.25
22.81
NI
NI
10/29/97
381.18
11.69
367.15
8.35
357.67
6.15
387.84
18.02
384.71
17.30
382.64
15.21
382.27
23.79
NI
NI
04/30/98
382.95
9.92
368.81
6.69
358.69
5.13
389.90
15.96
388.14
13.87
385.83
12.02
384.40
21.66
NI
NI
10/14/98
381.82
11.05
367.43
8.07
357.73
6.09
388.23
17.63
385.36
16.65
383.04
14.81
382.63
23.43
NI
NI
04/27/99
381.75
11.12
367.65
7.85
358.16
5.66
388.55
17.31
385.83
16.18
383.22
14.63
383.09
22.97
NI
NI
10/21/99
382.81
10.06
368.29
7.21
358.54
5.28
388.81
17.05
386.23
15.78
385.10
12.75
383.22
22.84
NI
NI
04/19/00
382.01
10.86
367.89
7.61
358.07
5.75
388.60
17.26
385.92
16.09
383.62
14.23
383.14
22.92
NI
NI
10/19/00
381.01
11.86
367.00
8.50
357.29
6.53
387.55
18.31
384.43
17.58
381.65
16.20
382.11
23.95
NI
NI
04/10/01
381.55
11.32
367.51
7.99
358.09
5.73
387.94
17.92
385.48
16.53
382.73
15.12
382.40
23.66
NI
NI
10/11/01
380.37
12.50
366.46
9.04
356.93
6.89
386.59
19.27
383.40
18.61
380.31
17.54
381.35
24.71
NI
NI
04/18/02
380.75
12.12
366.97
8.53
357.63
6.19
386.92
18.94
384.23
17.78
381.34
16.51
382.81
23.25
NI
NI
10/08/02
379.89
12.98
365.87
9.63
356.21
7.61
385.52
20.34
382.71
19.30
379.60
18.25
380.70
25.36
NI
NI
04/09/03
382.98
9.89
368.50
7.00
356.33
7.49
388.87
16.99
387.01
15.00
384.81
13.04
383.55
22.51
NI
NI
10/13/03
381.87
11.00
367.68
7.82
357.67
6.15
388.65
17.21
386.26
15.75
383.85
14.00
383.37
22.69
NI
NI
04/26/04
381.46
11.41
367.19
8.31
357.31
6.51
388.15
17.71
385.09
16.92
382.50
15.35
382.75
23.31
NI
NI
10/25/04
381.21
11.66
367.11
8.39
357.14
6.68
387.86
18.00
384.81
17.20
382.31
15.54
382.96
23.10
NI
NI
04/04/05
381.68
11.19
367.55
7.95
357.73
6.09
388.11
17.75
385.53
16.48
383.05
14.80
382.67
23.39
NI
NI
10/04/05
380.49
12.38
366.20
9.30
356.31
7.51
386.83
19.03
383.70
18.31
380.85
17.00
381.75
24.31
NI
NI
04/28/06
381.27
11.60
367.11
8.39
357.54
6.28
387.58
18.28
384.66
17.35
381.90
15.95
382.66
23.40
NI
NI
10/09/06
380.54
12.33
366.52
8.98
356.78
7.04
386.91
18.95
383.70
18.31
380.87
16.98
381.75
24.31
NI
NI
04/23/07
381.93
10.94
367.94
7.56
358.14
5.68
388.41
17.45
386.01
16.00
383.55
14.30
383.07
22.99
NI
NI
10/30/07
380.77
12.10
366.68
8.82
356.79
7.03
386.84
19.02
383.82
18.19
381.29
16.56
381.54
24.52
NI
NI
04/21/08
381.53
11.34
367.70
7.80
357.75
6.07
388.08
17.78
385.86
16.15
383.06
14.79
382.66
23.40
NI
NI
10/06/08
381.46
11.41
368.68
6.82
357.57
6.25
387.94
17.92
385.30
16.71
382.96
14.89
382.75
23.31
NI
NI
04/13/09
381.67
11.20
367.79
7.71
357.86
5.96
388.15
17.71
385.50
16.51
382.97
14.88
382.82
23.24
NI
NI
10/13/09
380.32
12.55
366.25
9.25
356.32
7.50
386.40
19.46
383.22
18.79
379.90
17.95
381.18
24.88
NI
NI
04/26/10
381.53
11.34
367.65
7.85
357.52
6.30
388.19
17.67
385.88
16.13
383.09
14.76
382.96
23.10
NI
NI
10/19/10
381.26
11.61
366.80
8.70
356.98
6.84
387.46
18.40
384.80
17.21
381.89
15.96
382.28
23.78
NI
NI
04/18/11
380.78
12.09
366.89
8.61
357.01
6.81
387.08
18.78
384.20
17.81
381.08
16.77
381.75
24.31
NI
NI
10/10/11
379.98
12.89
365.92
9.58
355.92
7.90
385.83
20.03
382.94
19.07
379.42
18.43
380.81
25.25
NI
NI
04/17/12
380.32
12.55
366.81
8.69
357.06
6.76
386.04
19.82
383.43
18.58
379.09
18.76
381.17
24.89
NI
NI
10/09/12
379.83
13.04
366.17
9.33
356.66
7.16
384.89
20.97
382.71
19.30
379.51
18.34
380.48
25.58
NI
NI
04/15/13
380.34
12.53
366.87
8.63
357.27
6.55
385.84
20.02
383.71
18.30
380.84
17.01
381.16
24.90
NI
NI
09/30/13
380.56
12.31
366.88
8.62
356.82
7.00
386.43
19.43
383.95
18.06
381.38
16.47
381.85
24.21
NI
NI
04/16/14
382.43
10.44
367.90
7.60
357.47
6.35
387.59
18.27
385.19
16.82
382.57
15.28
382.50
23.56
NI
NI
10/15/14
380.46
12.41
366.40
9.10
356.44
7.38
386.26
19.60
383.51
18.50
380.55
17.30
381.33
24.73
NI
NI
04/15/15
381.27
11.60
367.40
8.10
357.51
6.31
387.46
18.40
384.91
17.10
382.17
15.68
382.49
23.57
NI
NI
10/07/15
382.44
10.43
367.63
7.87
357.63
6.19
387.50
18.36
385.26
16.75
382.09
15.76
381.68
24.38
NI
NI
04/11/16
381.70
11.17
367.65
7.85
357.63
6.19
388.34
17.52
385.69
16.32
383.21
14.64
383.02
23.04
NI
NI
11/30/16
381.43
11.44
367.48
8.02
357.30
6.52
388.05
17.81
384.93
17.08
382.58
15.27
382.68
23.38
NI
NI
04/11/17
381.18
11.69
367.06
8.44
357.27
6.55
387.69
18.17
384.69
17.32
382.02
15.83
382.23
23.83
NI
NI
12/12/17
380.61
12.26
366.61
8.89
357.26
6.56
386.88
18.98
383.49
18.52
380.79
17.06
381.44
24.62
NI
NI
06/20/18
380.96
11.91
367.06
8.44
356.93
6.89
387.52
18.34
384.67
17.34
382.04
15.81
382.28
23.78
395.97
35.41
11/27/18
382.91
9.96
368.78
6.72
358.32
5.50
389.00
16.86
386.74
15.27
384.29
13.56
383.75
22.31
398.38
33.00
04/02/19
378.95
13.92
368.29
7.21
358.12
5.70
389.08
16.78
386.77
15.24
384.32
13.53
383.67
22.39
399.17
32.21
11/19/19
380.94
11.93
366.76
8.74
356.88
6.94
387.54
18.32
385.11
16.90
381.35
16.50
381.91
24.15
397.58
33.80
MEAN
381.25
11.61
367.30
8.19
357.44
6.43
387.70
18.22
385.02
17.05
382.33
15.59
382.43
23.67
397.78
33.61
MAXIMUM
3112.98
13.92
369.08
9.63
359.00
7.90
389.90
20.97
388.14
19.30
385.83
18.76
384.40
25.58
399.17
35.41
MINIMUM
378.95
9.89
365.87
6.69
355.92
5.13
384.89
15.96
382.71
13.87
379.09
12.02
380.48
21.66
395.97
32.21
Notes:
1.) ft AMSL = feet above mean sea level
2.) -- = not measured or no data
3.) TOC = top of casing
4.) DTW = Depth to Water
5.) NI = not installed
6.) MW = monitoring well
7.)' = anamolous data
8.) TOC and water elevation data for dates prior to October 2007 from HDR Engineering, Inc. of the Carolinas Semi -Annual Monitoring Reports and the July 2006 Water Quality Monitoring Plan.
9.) MW-10 TOC elevation inferred from historical depth -to -groundwater and groundwater elevation measurements.
10.) Groundwater elevation and depth -to -water measurements appear to be anamolous for MW-14 during the 10/13/03 event and MW-15 during the 4/19/00 event and are not included in mean, maximum or minimum calculations.
12.) Groundwater elevation for MW-3 for April 2017 is from April 13 (not April 11) due to meter malfunction on April 11.
G TRCJECTSNw, Co yn 127453-Moore-Env Services M9-201100-WGM&Reporling%00 CALCULATICNS12020-02-15 WOMB Tables 4 G O L D E R

February 2020 Page 1 of 1
TABLE 2
Summary of Estimated Horizontal Groundwater Flow Velocities
Water Quality Monitoring Event, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Notes:
1.) Horizontal velocities based on the modified Darcy equation Vgw = Ki/ne.
2.) Values for K are based on the average of hydraulic conductivities generated from the April 4, 2005 slug testing for the
current groundwater monitoring well network as part of HDR Engineering, Inc. of the Carolinas July 2005
Assessment of Corrective Measures Report for the Moore County Landfill.
3.) Values for ne are based on an effective porosity of 35% typical for soils at the site, as referenced in the July 2005
Assessment of Corrective Measures Report.
G:\PROJECTS\Moore County\19127453 -Moore -Env Services FY19-20\P100 - WQM & Reporting\600 CALCULATIONS\2020-02-15 WQMR Tables 4
Project No. 19127453
G 0 L D E R

February 2020 Page 1 of 1 Project No. 19127453
TABLE 3
Summary of Groundwater Monitoring Well Construction Infromation
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Well Identification
MW-1
Con,structionllWCoordinateM6u,nd
Date
06/05/87
Northing
508605.64
1854636.41
Surface
E evation
AMSL)
390.70
Measuring Point
Elevation
(ft AMSL)
392.87
tfa' We I I
D- pth
eet)
20
Well Depth
Elevation (ft
AMSL)
370.70
W Fe' Its
lame er
(Inche
2
creened
Interval
(ft bgs)
6.97 - 17.07
-��creened
Interval
(ft AMSL)
383.73 - 373.63
Geology of Screened Interval
1W
Sand
Well Status
IL
Groundwater Monitoring Well (Active)
Associated Waste Unit
MSW Landfill
MW-2
06/06/87
508508.07
1853819.73
373.39
375.50
20
353.39
2
7.52 - 17.77
365.87 - 355.62
Sand
Groundwater Monitoring Well (Active)
MSW Landfill
MW-3
06/06/87
508781.79
1852845.34
362.00
363.82
16.5
345.50
2
5.75 - 15.88
356.25 - 346.12
Sand and Silty Clay
Groundwater Monitoring Well (Active)
MSW Landfill
MW-4
06/06/87
509793.80
1853641.22
363.40
366.19
15
348.40
2
4.28 - 14.09
359.12 - 349.31
Sand and Silty Clay
Groundwater Monitoring Well (Active)
C&D Landfill
MW-5
06/06/87
510970.55
1853091.84
384.06
386.61
20
364.06
2
6.96 - 17.21
377.10 - 366.85
Sand and Clayey Sand
Groundwater Monitoring Well (Active)
Upgradient (MSW and C&D Landfills)
MW-6
03/06/95
510385.96
1853881.79
403.50
405.86
20
383.50
2
5.00 - 20.00
398.50 - 383.50
Sand to Silty Sand
Groundwater Monitoring Well (Active)
MSW Landfill
MW-7
03/06/95
509783.24
1853820.43
399.20
402.01
20
379.20
2
4.00 - 19.00
395.20 - 380.20
Sand, Silt, Silty Sand, Clay
Groundwater Monitoring Well (Active)
MSW Landfill
MW-8
03/06/95
509384.99
1853844.10
395.20
397.85
20
375.20
2
5.00 - 20.00
390.20 - 375.20
Sand, Silt, Silty Sand, Clay
Groundwater Monitoring Well (Active)
MSW Landfill
MW-9
03/06/95
508964.80
1854268.28
403.70
406.06
30
373.70
2
15.00 - 30.00
388.70 - 373.70
Silty Sand
Groundwater Monitoring Well (Active)
MSW Landfill
MW-11 S
09/16/96
510361.58
1852939.03
380.36
382.34
20
360.36
2
5.00 - 20.00
375.36 - 360.36
Sand to Silty Sand
Groundwater Monitoring Well (To Be Decomissioned)
C&D Landfill
MWA 1 D
09/16/96
510342.65
1852938.03
380.03
383.05
40
340.03
2
30.00 - 40.00
350.03 - 340.03
Silty Sand
Groundwater Monitoring Well (To Be Decomissioned)
C&D Landfill
MW-11 SR
06/01/18
510452.38
1852905.36
383.41
386.13
28
355.41
2
18.00 - 28.00
358.13 - 368.13
Clayey Sand
Groundwater Monitoring Well (Active)
C&D Landfill
MW-11 DR
05/31/18
510453.00
1852911.56
383.41
386.36
44
339.41
2
34.00 - 44.00
342.36 - 332.36
Sand
Groundwater Monitoring Well (Active)
C&D Landfill
MW-13S
09/18/96
509580.75
1853131.47
386.35
388.88
20
366.35
2
5.00 - 20.00
381.35-366.35
Sand to Silty Sand
Groundwater Monitoring Well (To Be Replaced and Decomissioned)
C&D Landfill
MW-13D
09/18/96
509568.07
1853130.65
385.65
388.04
40
345.65
2
30.00 - 40.00
355.65 - 345.65
Sand to Silty Sand
Groundwater Monitoring Well (To Be Replaced and Decomissioned)
C&D Landfill
MW-14
09/16/96
510056.32
1853641.99
397.88
400.58
20
377.88
2
5.00 - 20.00
392.88 - 377.88
Sand to Silty Sand
Groundwater Monitoring Well (Active)
Upgradient (C&D Landfill)
MW-15R
05/29/18
510589.03
1854391.51
428.81
431.48
47
381.81
2
37.00 - 47.00
384.48 - 374.48
Sand
Groundwater Monitoring Well (Active)
MSW Landfill
MW-17S
06/04/18
509704.03
1852096.70
371.45
374.16
18
353.45
2
8.00 - 18.00
363.45 - 353.45
Sand
Groundwater Monitoring Well (Active)
C&D Landfill
MW-17D
06/01/18
509693.71
1852101.52
372.05
374.56
34
338.05
2
29.00 - 34.00
343.05 - 338.05
Clay/Sandy-Clay
Groundwater Monitoring Well (Active)
C&D Landfill
MW-18
06/04/18
509369.85
1852249.28
365.35
368.50
13
352.35
2
5.00 - 13.00
360.35 - 352.35
Gravelly Sand, Sand, Sandy Clay
Groundwater Monitoring Well (Proposed)
C&D Landfill
Notes:
1.) ft AMSL = feet above mean sea level
2.) ft BGS = feet below ground surface
3.) Well construction information for monitoring wells MWA through MWA6S/D collected from boring logs and well construction records from HDR Engineering, Inc. of the
Carolinas July 2006 Water Quality Monitoring Plan. TOC and Ground Elevations are taken from the July 2005
Assessment of Corrective Measures Report and/or well records where available.
GOLDER
G:\PROJECTS\Moore CwnpA79127433 - Mcore - Env Services FV1920\P100 - W OM 8 Reporting\6W CALCULATIONS\2020-02-15 W OMR Tables

Page 1 of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (De -d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second Seml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
0.1
[hd."qWqjjB-191*""d
•
A�
•-
W. C&D Mmit
1mg W.11.
•
.•
Adm C&D
-
Mllitllilg W1111
& MNA PW
...... Mmi-img
W,11,
CI ... d MSW
M..ft.rJ.g W.11.
& MNA P-
C1 ... dMSW
Off.it.
ND
-
NC2L=10ug/L
ug/L
OM1191
-
-
-
NO
-
-
-
-
-
NO
-
-
-
-
-
-
-- -
NO
NO
ND
-
--
-
-
-
--
NO
--
EPAMCL=10ug/L
ug/L
OW10192
-
-
-
NO
-
-
-
-
-
NO
-
-
-
-
-
-
-- -
ND
NO
ND
-
--
-
-
-
--
NO
--
ug/L
04/20/95
-
-
-
NO
-
-
-
-
-
-
-
-
-
-
-
-
-- -
--
--
-
NO
NO
ND
-
-
NO
NO
--
ug/L
O6/27195
-
-
-
-
-
-
NO
ug/L
09/22/95
-
-
-
NO
-
-
-
-
-
-
-
-
-
-
-
-
-- -
NO
--
--
ND
NO
ND
-
-
ND
ND
--
ug/L
03/2 96
-
-
-
NO
-
-
-
-
-
-
-
-
-
-
-
-
-- -
ND
NO
--
NO
NO
NO
--
--
NO
NO
--
uw
10129196
NO
NO
NO
NO
NO
NO
NO
NO
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/08/97
--
--
--
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
ND
--
NO
NO
--
uw
10129197
NO
NO
NO
NO
NO
NO--
NO
NO
NO
NO
--
NO
NO
--
ug/L
04/30/98
--
--
--
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
NO
NO
--
uw
10114198
NO
NO
NO
NO
NONO
NO
NO--
NO
NO
NO
NO
--
NO
NO
--
ug/L
04/27/99
--
--
--
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
NO
NO
--
ug/L
10/21/99
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
18
NO
NO
--
NO
NO
--
ug/L
OW14100
-
-
-
-
-
-NO
ug/L
04/1900
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
ND
NO
NO
NO
--
NO
NO
--
ug/L
10/1700
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
NO
NO
--
ug/L
10111101
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
NO
NO
--
ug/L
04/ 02
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
-
NO
NO
NO
NO
NO
NO
ug/L
10/0 02
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
-
-- -
--
--
-
9
NO
10
NO
NO
NO
ug/L
04/0903
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
-
NO
NO
10
NO
NO
ug/L
1011W03
-
-
-
NO
NO
-
NO
NO
NO
-
NO
-
-
-
NO
NO
-- -
--
--
-14
7
11
14
NO
ug/L
04/2604
-
-
-
NO
NO
-
NO
NO
NO
-
NO
-
-
-
NO
NO
-- -
--
--
-
NO
NO
NO
12
NO
NO
ug/L
10/25I04
-
-
-
NO
NO
-
NO
NO
-
-
NO
-
-
-
NO
NO
-- -
--
--
--
15
NO
ND
14
--
NO
NO
--
ug/L
04/04/05
-
-
-
10
10
-
15
10
13
-
10
-
-
-
10
10
-- -
--
--
--
10
15
29
10
-
10
NO
--
10104/05
NO
NO
13
NO
NO
I
NO
NO
NO
NO91
-- -
--
--
--
13
15
21
ND
-
12
NO
--
u91L
04/28/06
--
--
--
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
11
NO
-- -
NO
NO
NO
12
NO
11
i6
--
NO
NO
--
u91L
10/09/06
-
--
-
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
13
NO
-- -
NO
NO
NO
14
NO
NO
11
--
NO
NO
--
u91L
04/24/07
-
--
-
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
NO
NO
NO
38
27
--
NO
NO
--
u91L
10/30/07
-
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
NO
3.2
J NO
6.9
J 7.8
J --
NO
NO
NO
u91L
04/23/08
-
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
3.2
J NO
NO
NO
NO
NO
2.3
J --
NO
NO
NO
u91L
10/06/08
-
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
NO
NO
NO
ND
7.7
J --
NO
NO
NO
u91L
04/13/09
-
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
5.1
J 5.]
J -- -
NO
NO
NO
8.2
J 171
11.4
0.fiu
6.J
NO
NO
/
10
5
5
6
J 8.3
1
2
11.6
NO
NO
/
0
NO
NO
NO
NO
NO
NO
10.5
10.
5.23
J
3.14
J NO
3.50
142
31.0
13
28.5
m
8Ju
NO
NO
u91
10/19/10
100
5.16 J
NO
10.3
NO
NO
NO
21.2
bL
10.2
NO
NO
NO
MIS
33.0
280
26.6
2.6
NO
NO
u91
018111
NO
NO
-
NO
NO
NO
NO
5.05
B -
-
-
20.0
12.5
B -- -
3.29
B NO
5.35
B 18.7
14.6
B 19.2
14.6
B --
16.1 B
5.3B
3.37 J
u91L
10/10/11
-
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
2.96
J 5.48
J 4.73
J 19.0
Dry
--
5.67 J
5.2: J
NO
u91L
04/17/12
-
--
10
4.42 B
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
4.95
B -- -
NO
4.31
B 3.32
B NO
2 4
17.9
B Dry
--
NO
NO
5.70 J
u91L
10/09/12
-
--
10
NO
NO
-
4.17
J ND
4.58 J
NO
4.17
J -
-
-
6.36
J 5.72
J -- -
2.90
J NO
2.91
J 9.82
J 21.6
iD.7
Dry
--
9.74 J
NO
NO
u91L
04/15/13
-
--
10
3.97 B
NO
-
NO
NO
NO
5.21
B
ND
-
-
-
NO
4.87
B -- -
2.87
B NO
4.42
B 17.8
NO
14.7
B Dry
--
NO
NO
3.34 J
u91L
09/30/13
-
--
10
NO
NO
-
NO
NO
NO
NO
11.5
-
-
-
9.62
J NO
-- -
NO
NO
NO
24.5
32.0
18.0
Dry
--
20.9
NO
NO
u91L
04/16114
-
--
10
NO
NO
-
NO
NO
NO
ND
NO
-
-
-
8.25
J NO
-- -
NO
NO
NO
23.3
19.7
19.5
Dry
--
15.2
NO
NO
u91L
10/15114
5.4
--
10
Dry
NO
-
NO
5.%
J
6.18 J
NO
NO
-
-
-
NO
13.7
-- -
NO
NO
NO
6.99
J iD.8
30.6
ON
--
14.1
NO
NO
ug/L
04/15115
5.4
-
10
ND
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
NO
20.3
21.8
8.41
J Dry
--
NO
NO
NO
uo/L
1010]/15
5.4
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
7.45
J -- -
NO
NO
NO
NO
20.0
32.4
873
J --
ND
NO
ND
ug/L
04/11/16
5.4
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
12.9
-- -
NO
NO
NO
12.6
27.0
38.7
29.6
--
11.3
NO
ND
ug/L
11/30/i6
6.8
--
10
ND
ND
-
22.8 (ND)
NO
12.9 (ND)
NO
43.4 (ND)
-
-
-
48.1 (ND)
16.9 (ND)
-- -
NO
NO
NO
65.8(NO)
20.4(ND)
85.6(41.9)
39.6(42.4)
--
14.9(NO)
ND
ND
(Dissolved)
u9/L
11/301i6
6.8
--
10
-
-
-
-
-
--
-
-
-
-
-
-
-
-- -
--
--
--
--
--
--
14.4
(Verification Event)
ug/L
02/09/17
6.8
--
10
NO
-
-
-
-
--
-
-
-
-
-
-
-
-- -
--
--
--
--
--
40.5
--
--
--
--
--
(Dissolved)
u9/L
02/09/17
6.8
--
10
-
-
-
-
-
-
-
-
-
-
-
-
-
-- -
--
--
--
--
--
39.0
--
--
--
--
--
ug/L
04/11/17
6.8
--
10
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
7.78
J NO
-- -
NO
NO
NO
10.5
8.67
J 53.7
31.8
--
NO
ND
ND
u9/L
12/12117
6.8
--
10
NO
NO
-
NO
NO
NO
NO
17.8
-
-
-
19.3
NO
-- -
NO
NO
NO
25.9
21.5
53.2
25.4
--
BA9 J
ND
ND
u9/L
06/20/18
7.6
--
10
NO
-
NO
NO
NO
NO
NO
-
NO
-
-
22.7
NO
-- -
NO
NO
NO
22.8
NO
38.6
-
NO
NO
--
NO
u9/L
11)2]118
7.6
10
-
NO
-
NO
NO
NO
NO
NO
-
NO
-
-
NO
NO
-- -
NO
NO
NO
NO
14.9
MA
-
NO
NO
NO
NO
u9/L
04/02119
7.6
10
-
NO
-
NO
NO
NO
NO
NO
-
NO
-
-
NO
NO
-- -
NO
NO
NO
NO
11.7
NO
--
NO
NO
NO
NO
u9/L
11/19/19
7.6
10
NO
NO
NO
NO
NO
NO
NO
NO NO
NO
NO
NO
NO
NO
36.5
NO
NO
NO
NO
Barium
ug/L
03/OS/90
-
-
-
35
-
-
-
-
-
15
-
-
-
-
--
-
-- -
57
27
13
-
-
-
-
--
-
NO
-
NC2L=700 ug)L
ug/L
03/21191
-
-
--
35
-
-
-
-
--
23
-
-
-
-
-
-
-- -
73
66
23
--
--
--
--
--
--
ND
--
EPA MCL = 2000 ug/L
ug/L
03/10192
-
-
--
30
-
-
-
-
--
23
-
-
-
-
-
-
-- -
43
69
12
--
--
--
--
--
--
ND
--
ug/L
04/20195
-
-
--
NO
-
-
-
-
--
-
-
-
-
-
-
-
-- -
--
--
--
NO
NO
NO
--
--
ND
ND
--
ug/L
06/27195
-
-
--
_
_
_
_
_
--
_
_
_
_
_
_
_
-- _
--
--
--
--
--
--
--
--
--
ND
--
ug/L
09/22/95
-
--
--
NO
-
-
-
-
--
-
-
-
-
-
-
-
-- -
NO
--
--
NO
NO
NO
--
--
ND
ND
--
ug/L
03/28/96
-
--
--
NO
-
-
-
-
--
-
-
-
-
-
-
-
-- -
NO
NO
--
NO
NO
NO
--
--
ND
ND
--
ug/L
10129/96
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04108/97
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
ND
--
ND
ND
--
ug/L
10/29/97
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/30198
-
-
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/14198
-
-
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/27199
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/21199
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
03/14100
-
--
--
_
_
_
_
_
--
_
_
_
_
_
_
_
_ _
--
--
--
--
--
--
--
--
--
ND
--
ug/L
04/19100
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/17100
-
-
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
ND
--
ND
ND
--
ug/L
04/10101
-
-
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/11101
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/18102
-
--
--
NO
NO
-
NO
NO
--
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/08102
-
--
--
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/09103
-
--
--
NO
NO
-
NO
NO
-
-
NO
-
NO
NO
NO
-
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10/13103
-
-
--
NO
NO
-
NO
NO
NO
-
NO
-
-
-
NO
NO
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/26104
-
--
--
NO
NO
-
NO
NO
NO
-
NO
-
-
-
NO
NO
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10125IN
-
--
--
NO
NO
-
NO
NO
-
-
NO
-
-
-
NO
NO
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
.104/05
-
--
--
NO
NO
-
NO
NO
NO
-
NO
-
-
-
NO
NO
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
10104/05
-
--
-
NO
NO
-
NO
NO
NO
-
NO
-
NO
NO
NO
NO
-- -
--
--
--
NO
NO
NO
NO
--
ND
ND
--
ug/L
04/28/06
-
--
--
NO
NO
-
NO
NO
NO
NO
NO
-
-
-
NO
NO
-- -
NO
NO
ND..............
ND..
ND.............
ND..
N..D..
ND.........
ND
ug/L
10/09/06
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
ND
ND
-
ug/L
04/24107
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
ND
ND
-
ug/L
10/30107
100
13
246
J
21.1
J 2.0
124
J
41.6 J
52.8
J
8
J
444
J 90.8
J
466
J 65.8
J 138
J 40.1
J 17.0
J 80.2
J 155
J
603 J
J
14......6
1---..- 1 J
04/2 1081.5
100
J
2
18
J
55.
1.
2
J 106
571
................
J
J
J 58.5
J 28
J 81.1
J 1230.2
J
J
J
Jug/L
ug/L
10/06I08
10000
12
16.5
J 14
J
J
418
J
8
J
45.7
J 203
409
J 58.8
J 138
J 42.0
J 31.2
J 83.1
J 12
J
51A J
15.6 J
ND
ug/L
04/13109
1.8
41
1.
J
16.1
J 17.8
J
49.2
5
J
7.4
69
J
51.3
J 139
485
J 65.8
J 172
J 42.6
J 367
J 89.8
J 14.9
J
81.6 J
14.5 J
ND
10/15109
100
13.J
27.8
J
26.3
J 53
8.
J
54.2 J
76.
6
J
0
J
447
J 84.60
J
286
J 66.7
J 181
J 40.0
J 333.9
J 786
J 20.8
J
67.5 J
14.5 J
1.ug/L 02 J
ug/L
4/26/10
00
9.4J
33A
J
19.]1
J 1 35
J
480 J
57
J
77.4
499
J
J
43.3
J 66.0
J 198
J 39.8
J 34
J 80.3
J 1.7
136
J
6].2 J
14.8 J
NO
10/19/10
100
i66 J
24.3
J
7
J 41
J
414 J
29.5
J
73.1
J
42.4
J 81
J
314
J 52.6
J 4.9
J 29.5
J 252
J 69.7
J
J ------..
539 J
11.8 J
NDug/L
ug/L
(A/18/11
100
J
286
J
22.3
J 16.39
J
5 .9 J
41.28
J
703.1
J
48.1
J 86.9
J
488
J 64.8
J 214
J 40.2
J 282
J 81.9
J 17.5
J
703 J
15.4 J
NO
ug/L
10/10/11
100
131
43 J
286
J
29
J 11
J
69 J
7
77
J
47.5
J 56.4
J
461
J 66.7
J 220
J 39.9
J 301
J 74.7
J Dry
71.7 J
15.5 J
ND
ug/L
4/1]/12
100
1J
29.5
J
24.3
6
4J
2
40.5
J
606.2
J
52.1
J 65.2
J
627
J 75.0
J 21.]
J 39.8
J 301
J 4.9
J Dry
675 J
15.5 J
NO
ug/L
10/09/12
100
19.5
4 J
22
J
22A
J 21.6
J
47A J
101
J
8
J
3
J 465
J
520
J 68.1
J 18.8
J 39.5
J 397
J 73.0
J Dry
642 J
14.7 J
107 J
ug/L
0/15/13
100
146 J
217
J
21.8
J 21
J
47.8 J
26.8
J
0
J
49.4
J 794
J
405
J 60.8
J 204
J 42.7
J 36.7
J 86.4
J Dry
78A J
14.6 J
NO
ug/L
09/30/13
100
124 J
342
J
235
J 24A
J
56.9 J
245
J
86.8
J
56.5
J 111
35.8
J 383
J 21.1
J 5.5
J 47.1
J 90.1
J Dry
653 J
14.9 J
ND
ug/L
4/16/14
--
100
13.6 J
33.8
J
176
J 255
J
27 J
15.9
J
527
J
47.3
J 798
J
33
J 41.8
J 15.2
J 426
J 28.9
J 102
Dry
60.6 J
162 J
NO
ug/L
10/15/14
1
10000
Dry
25.6
J
20.5
J 148
J
127
J
713
J
50.4
J 112
33.6
J 46.3
J 255
J 49.3
J 31.1
J 98.4
J Dry
103
231 J
NO
ug/L
(AM 115
1
156 J
40
J
21.9
J 368
J
114
J
887
49.2
J 105
466
J 53.3
J 32.9
J 45.0
J 284
J 93.7
J Dry
747 J
18.2 J
NO
ug/L
10/0]115
1
100
47 J
42A
J
17
J 17.7
J
41
21.2
J
693
45.8
J 74.8
J
304
J 52.1
J 252
J 36.6
J 286
J 92.8
J 12.6
J
888 J
15.8 J
ND
4/11/16
1
100
1J
49
J
14.0
J 31.0
J
1
69.3
J
706
0ug/L
J
41.5
J 145
31.9
J 38.8
J 340
J 44.4
J 286
J 4.0
J 838
J
65.5 J
18.5 J
NO
ug/L
11/30/16
1
100
137
4.4 B
45.9
J
166
B 22.
33
B
84
J
36.7
B 115
286
B 38.2
B 300
B 44.5
J 242
B 4.2
J 870
B
751 J
17.8 B
7.92 J
ug/L
(A/11117
1
100
14J
43.5
J
232
J 23.1
J
131
285
82
45.3
J 113
299
J 4.5
J 326
J 45.0
J 266
J 106
9.34
J
.7 J
8J
NO
ug/L
12/1217
1
100
12.5 J
45
J
313
J 11.0
J
131
35.6
4.3
43.5
J 524
J
348
J 55.6
J 368
J 47.9
J 286
J 98.2
J 14.
J
77.3 J
18.7 JND
ug/L
06/20/18
1A
100
11.7 J
-
58
.
105
43
59.9 J
-
.
.
.
1.8
.
.
--
NO
ug/L
11/27/18
39
1
80
31.6
110
604
68.4
40.4
59.0
305
38.7
3
38.9
392
78.8
323
5.5
202
NO
/L
0/02
.4
490
162
289
976
59
0
-
37.8
91.
30.4
38.3
335
37.8
408
78.4
38.9
5.2
208
NDu9
L
59.3
36.]
11.]
3.9
]1.2u
9
68.3 16.5
1 37.8
54.9
38.5
52.7
38.3
117
19.8
1 102
20.7
NO
GOLDER

Page 2 of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det-d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
�it.rimg' j
,.P t,..
.. _P�.
Mlh,d JjMMjMB,ck,r
... d
•
Ati,,
•
C&D M,,it*ri,g
W,11,
•
.•
Ati�.C&DM.�it.ri�gW.11.&MNAP.ff.r..�..M.�it.ri�gW.11.
I. th,
Cl
Cl-d MSW M..Rri.g
W.11. & MNA
P.6--.. M-i-mg
W.11.
Cl ... d MSW
Offsit'
Pri-t. W.11
Bl-k.
Cadmium
ug/L
03105/90
--
--
-
ND
-
-
-
-
--
ND
-
-
-
-
-
-
-- -
ND
ND
ND
-
--
-
-
--
--
ND
-
NC2L=2 ug/L
ug/L
OM1191
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
-- -
ND
ND
ND
--
--
-
-
--
--
ND
--
EPA MCL=5ug/L
ug/L
03/10/92
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
-- -
ND
ND
ND
--
--
--
--
--
--
ND
--
ug/L
04/2095
-
-
-
ND
_
-
_
_
_
_
_
_
_
_
_
-
-- _
..
..
--
ND
ND
ND
--
--
ND
ND
--
ug/L
O6/21195
ND--
ug/L
09/22/95
-
-
-
ND
-
-
-
-
-
-
-
-
-
-
-
-
-- -
ND
--
--
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
WOW97
ND
ND
-
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
w
W30198
ND
ND
ND
ND
D
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
w
W27199
ND
ND
ND
ND
D
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
OW14100
-
-
-
-
-
-ND
ug/L
04/1900
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10117100
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
-
-- -
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
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C> GOLDER

Page 3 of 20
Project No. 19127453
TABLE 4
Summary of 1-11-1ca1 Groundwater Monitoring Results (De -d Constlt... ts(
Water Quality Monitering Report, 2019 Second S-1-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
�it.rimg'
Cobalt Total
NC 2L IMAC=1 ug/L
R.p.r1mg
ug/L
ug/L
ug/L
u L
S..pl.
O6/20/18
1112711E
04/02119
11/19/19
Mth.d JjVMjMB,ck,r
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10
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ND
ND
ND
ND
ND
-
-
-
ND
r
--
--
ND
--
--
--
Cl-d
--
--
--
MSW
--
--
--
M..Rri.g W.H. & MNA
-
--
--
P.6--.. M-it.dmg
-
-
-
W.11.
-
--
--
-
-
--
--
--
--
Cl.s.d MSW
--
--
--
Offsit'
--
--
--
ND
ND
ND
upper
ug/L
-
-.
.-
-
-
-.
-
-.
--
-
--
--
--
--
--
-10
ND
ND
N
NC2L=1000 ug/L
ugrL
OW21191
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
--
-
14
12
ND
--
-
--
--
--
--
ND
--
EPA MCL=1300 ug/L
ug/L
03/10/92
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
--
-
ND
110
ND
--
-
--
--
--
--
ND
--
ug/L
04/2095
-
-
-
ND
_
_
_
_
_
_
_
_
_
_
_
-
--
_
..
..
--
ND
ND
11
--
--
14
ND
--
ug/L
O612]195
-
-
-
-
-
-
--
ND
ND
ND
--
--
ND
ND
--
ug/L
03/28196
--
--
--
ND
-
-
-
-
-
-
-
-
-
-
-
-
--
-
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
012 196
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/08197
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
1012 197
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/30/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
1011 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/2]199
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
10121199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
03/14/00
-
-
-
-
-
-
ND
uWL
&41 9100
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
1017100
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ 1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
Wl 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/0903
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1303
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 /&4
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/25104
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
-
-
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
Wo /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04105
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
M128106
-
-
-
-
-
-
--
--
ug/L
10/09106
ug/L
04/24107
-
-
-
-
-
-
--
--
ug/L
10/30/07
-
-
-
-
-
-
--
--
ug/L
04/23I08
ug/L
O6/2018
1.6
-
10
2.28 6
-
ND
ND
ND
ND
5.70
6
-
ND
-
-
ND
1.90
B
-
--
--
--
--
ND
ND
--
--
--
--
--
4.51 J
ug/L
11/2] 18
1.6
10
-
ND
-
ND
ND
ND
ND
3.17
6
-
ND
-
-
ND
ND
-
--
--
--
--
--
--
--
--
--
--
--
2.26 J
ug/L
04/02119
1.6
10
-
ND
-
ND
ND
ND
ND
3.37
J
-
ND
-
-
ND
ND
-
--
--
--
--
--
--
--
--
--
--
--
ND
u L
11/19/19
1.6
10
-
ND
-
ND
ND
2.75
J -
1.76
J
-
ND
-
-
ND
-
ND
2.96 J
--
--
--
--
--
--
--
--
--
--
ND
Lead
ug/L
..
-.
--
18
-
-
-
-.
-.
--
-
--
--
--
--
--
-
296
ND
NC 2L=15 uqL
ug/L
OM1191
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
--
-
ND
ND
ND
--
--
--
--
--
--
ND
--
EPA MCL = 15 ug/L'
ug/L
ON10192
-
-
-
14
-
-
-
-
-
25
-
-
-
-
-
-
--
-
10
39
12
--
--
--
--
--
--
ND
--
--
]
ND
18
--
--
18
ND
--
ug/L
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ND--
ugtL
09/22195
-
-
-
ND
-
-
-
-
-
-
-
-
-
-
-
-
--
-
ND
--
--
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
ND
--
--
ND
ND
--
ugtL
10/29196
--
--
--
ND
ND
-
12
ND
-
-
13
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
39
--
ugVL
M10 /97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
%
--
ugtL
10129197
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
70
--
ugVL
ml 0/98
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
42
--
ugtL
10/14198
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
26
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ugVL
W2 /99
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
13
--
ND
186
--
ugtL
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
135
--
ugtL
0314/00
ND--
ugtL
04/19/00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
101 7/00
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
04/10101
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
10
--
ND
14
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ugVL
101 1101
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ND
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ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
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04/18102
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-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
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uWL
1010 102
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ND
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ND
ND
ND
ND
ND--
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ND
ND
ND
--
ND
ND
--
uglL
04/09/03
--
--
--
10
ND
-
11
ND
-
-
48
-
ND
15
ND
-
--
-
--
--
--
ND
13
ND
19
--
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uWL
1011 103
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ND
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ND
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ND
ND
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ND
ND
ND
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ND
11
--
uglL
04/26/04
--
--
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ND
ND
20
ND
ND
-
12
-
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ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
1M /&4
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ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
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uglL
04/04/05
--
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ND
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19
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-
15
-
-
-
ND
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--
-
--
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12
14
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1010 105
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04/28/06
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ND
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-
ND
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13
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uglL
10/09/06
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--
ND
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107
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ND
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uglL
10/30/07
--
--
10
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ND
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3.1 J
ND
ND
ND
15.9
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-
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3.9 J
2.6
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4.6 J
5.2 J
2.6 J
2.5
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6.5 J
6.8 J
ND
uglL
04/23/08
-
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-
ND
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ND
ND
4.3 J
-
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-
ND
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--
-
ND
ND
ND
ND
ND
ND
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15.8
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5.0 J
-
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2.2
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2.9 J
4.9 J
ND
2.2
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uglL
04/13109
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3.1 J
ND
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2.4 J
-
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6.3 J
4.6
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--
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2.3
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5.2 J
6.4 J
5.5
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10A
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uglL
10/15109
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2.86 J
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ND
ND
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3.90 J
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2.27
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3.37 J
ND
uglL
04/26I10
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390 J
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2.27 J
ND
5.86 J
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-
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3.82 J
2.85
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2.47 J
ND
3.17 J
4.54 J
3.09 J
3.89
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3.95 J
2.18 J
ND
uglL
1019110
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4.14 J
ND
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3.45
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2.07 J
2.21
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--
-
ND
ND
ND
ND
ND
ND
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1.92 J
8.93 J
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uglL
04/18/11
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2.78
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278 J
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2.00
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4.75 J
-
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5.09 J
2.79
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--
-
ND
ND
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5.57 J
5.07 J
ND
5.19
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6.87 J
19.0
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uglL
1010111
-
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10
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-
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ND
ND
ND
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-
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--
-
ND
ND
ND
ND
ND
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Dry
--
ND
ND
ND
uglL
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-
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10
ND
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ND
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2.26
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ND
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-
-
ND
ND
--
-
ND
ND
ND
ND
4.08 J
ND
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--
ND
16.6
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uglL
10/09/12
-
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10
ND
ND
-
ND
ND
ND
2.51
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3.21 J
-
-
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3.49 J
ND
--
-
ND
ND
ND
3.89 J
2.89 J
ND
Dry
--
ND
20.6
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uglL
04/15113
-
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10
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ND
-
ND
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2.11
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--
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ND
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20.4
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uglL
09/30/13
-
--
10
ND
ND
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241 J
ND
ND
2.75
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7.30 J
-
-
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4.05 J
ND
--
-
ND
ND
ND
6.67 J
5.81 J
3.31 J
Dry
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5.32 J
37.3
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uglL
04/16/14
--
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10
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ND
-
325 J
ND
8.% J
3.06
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2.54 J
-
-
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4.17 J
ND
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ND
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5.24 J
7.02 J
2.83 J
Dry
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4.95 J
60.5
ND
uglL
1015/14
2.1
--
10
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ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
18.3
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uglL
04/15115
2.1
--
10
ND
ND
-
ND
ND
ND
ND
9.49 J
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
26.2
ND
uglL
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2.1
--
10
ND
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-
ND
ND
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4.58
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5.23 J
-
-
-
ND
ND
-
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3.55
J ND
ND
3.21 J
4.36 J
5.90 J
6.76
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ND
22.2
ND
uglL
04/11116
2.1
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
4.87
J --
ND
21.0
ND
ugl
11/30/16
3.1
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
11.5
ND
ugl
04/11/17
3.1
--
10
ND
ND
-
ND
ND
ND
4.48
J
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
36.0
ND
ugl
12/12117
3.1
--
10
ND
ND
-
3.37 J
ND
ND
ND
ND
-
-
-
].48 J
ND
-
--
ND
ND
ND
7.80 J
ND
ND
5.91
J --
3.33 J
15.6
ND
ugl
06/20/18
3.1
-
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
-
ND
ugtL
11/2]/18
3.1
10
-
ND
-
3.42 J
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
23.7
ND
ug/L
04/02119
3.1
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
ND
ND
ND
ND
ND
ND
--
23.8
ND
MA
ND
ug/L
11/19/19
3.1
10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
26.3
ND
,> GOLDER

Page 4 of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det-d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S-l-Annual Sampling Event
Moor. County Landfill, NC Solld We- Permit No. 83-01
Aberdeen, Moore County, North Carolina
_Ple
Mlh,d
d
Ati,, C&D
M,,it*ri,g
Well,
I. the
Cl
Cl.e.d
MSW
M..ftr.g Well. & MINA
P.ff.mmn.. M-i-ing
Well.
Pri-t. Well
Bl.nk.
Mercury
ug/L
03I05/90
--
--
-�
0.5
--
-
--
--
--
ND
--
-
--
--
--
--
--
-
ND
0.5
ND
-
NC2L=1 ug/L
ug,
OM1191
-
-
-
O.fi
-
-
-
-
-
0.6
-
-
-
-
-
-
--
-
0.8
2.4
0.6
--
--
-
-
--
--
ND
--
EPA MCL=tug/L
ug/L
03/10/92
-
-
-
0.]
-
-
-
-
-
1.1
-
-
-
-
-
-
--
-
ND
6
1.3
--
--
--
--
--
--
ND
--
ug/L
04/2095
-
-
-
ND
_
-
_
_
_
_
_
_
_
_
_
-
--
_
..
..
--
ND
ND
0.3
--
--
1.2
ND
--
ug/L
06/2]/95
ND--
ug/L
09/22195
-
-
-
ND
-
-
-
-
-
-
-
-
-
-
-
-
--
-
ND
--
--
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO 97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W3 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
03/14/00
-
-
-
-
-
-ND
ug/L
04/1900
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ ] 00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/09/03
-
-
-
ND
ND
-
ND
ND
-
-
3.67
-
ND
ND
ND
-
--
-
--
--
--
1.01
ND
ND
ND
--
ND
ND
--
uWL
1011 03
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/26104
--
--
--
ND
ND
-
ND
ND
ND
-
2.5
-
-
-
ND
0.5
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/04105
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
1010 /05
ND
ND
1.6
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/28106
--
--
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09106
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/24107
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10130107
-
-
0.2
0.17 J
ND
-
ND
ND
ND
0.24
0.25
-
-
-
0.12
J 0.43
--
-
0.21
0.16 J
ND
ND
ND
ND
ND
--
0.1] J
ND
ND
ug/L
04/23108
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06108
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
0.21
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15109
-
-
0.2
ND
ND
-
ND
ND
0.0582 J
ND
ND
-
-
-
ND
ND
--
-
0.0952 J
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26110
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1019/10
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010/11
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
0.418
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/1]112
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
0.175 J
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09112
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15113
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30113
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16114
-
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1011 14
0.17
-
0.2
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.17
-
0.2
ND
ND
-
ND
ND
ND
0.0261
J 0.11fi88 J
-
-
-
ND
ND
--
-
ND
ND
ND
0.0796 J
ND
ND
Dry
--
ND
ND
ND
ug/L
1010]115
0.17
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
0.19] J
ND
ND
0.201
--
ND
ND
ND
ug/L
04/11/16
0.17
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
0.274
ND
0.219
--
ND
ND
ND
ug/L
11/30/16
0.17
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.17
-
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12117
0.10
--
0.2
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.11930
J ND
--
-
0.103 J
ND
ND
ND
ND
0.118 J
0.111 J
--
ND
ND
ND
ug/L
O6/20/18
0.15
--
0.2
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]/18
0.15
0.2
-
0.281
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
--
-
ND
ND
ND
ND
0.338
0.187 J
--
ND
ND
ND
ND
ug/L
04/02119
0.15
0.2
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
--
-
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.15
0.2
-
ND
-
ND
ND
ND
-
ND
-
ND
-
-
ND
-
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Nickel Tofal
ug/L
06=18
2.2
-
50
4.03 B
-
3.14 B
2.30
B 2.61 B
8.]fi B
2.30
B -
ND
-
-
ND
3.18 B
-
--
--
--
--
ND
ND
--
--
--
--
--
3A1 J
NC2L=100ug&
ug/L
11/2]/18
2.2
10
-
ND
-
ND
ND
ND
6.48 J
ND
-
ND
-
-
ND
ND
-
--
--
--
--
--
--
--
-
--
--
--
ND
u9/L
04/02119
2.2
10
-
ND
-
ND
ND
ND
5.47 J
ND
-
ND
-
-
ND
ND
-
--
--
--
--
--
--
--
-
--
--
--
ND
u L
11/19/19
2.2
10
-
ND
-
ND
ND
ND
-
ND
-
ND
-
-
ND
-
ND
ND
--
--
--
--
--
--
-
--
--
--
ND
Selenium
uNL
04/28I06
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
NC 2L=20 ugIL
uNL
10/09/06
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
EPA MCL=50 uuIL
uNL
04/24/07
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
4L
10/30/07
-
-
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ugr
04/23108
-
-
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
1010&08
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
04 ixol)
-
--
10
ND
ND
-
17.0
B 5.2 B
ND
ND
ND
-
-
-
6.4
B ND
-
--
ND
ND
ND
4.7 B
13.9 B
14.6 B
15.2 B
--
ND
ND
3.9 J
ug1L
10/15109
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
2.47 B
ND
--
1.02 B
ND
3.03 J
ug1L
04/2fi110
-
--
10
ND
ND
-
ND
ND
ND
ND
2.46 J
-
-
-
1.35
J ND
-
--
ND
ND
ND
1.17 J
1.18 J
ND
3.22 J
--
ND
ND
ND
ug1L
10/19/10
-
--
10
ND
ND
-
ND
ND
ND
ND
1.72 J
-
-
-
ND
1.84 J
-
--
ND
2.48 J
1.09
J 0.919 J
2.88 J
4.50 J
1AS J
--
1.30 J
ND
ND
ug1L
04/18111
-
--
10
ND
ND
-
ND
ND
ND
4.90
J ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
10/10/11
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
2.71
J ND
ND
ND
Dry
--
ND
ND
ND
ug1L
04/1]/12
-
--
10
ND
ND
-
ND
4.47(ND) J
ND
2.86(ND)
J ND
-
-
-
5.54(ND)
J ND
-
--
ND
ND
ND
4.55(ND) J
ND
ND
Dry
--
ND
ND
ND
ug1L
10/09/12
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
12.4
Dry
--
ND
ND
ND
ug1L
04/15113
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug1L
09/30/13
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug1L
04/1fi114
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug1L
10/15114
5.0
--
10
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug1L
04/15115
5.0
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug1L
10/07/15
5.0
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
04/11/16
5.0
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
11/30/16
6.2
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
04/11/1]
6.2
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
12/12117
6.2
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug1L
O6/20118
6.2
--
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]I18
6.2
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ugrL
0102119
6.2
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
11/19119
n2
10
ND
ND
ND
ND
ND
ND
ND
ND
ND
I ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
,> GOLDER

Page 5 of 20
Project No. 19127453
TABLE 4
Summary of Hl,terical Groundwater Monitoring Result, (Detected Conetlt... t,)
Water Quality Monitering Report, 2019 Second Seml-Annual Sampling Event
Moor. County Landfill, NC Solld Waste Permlt No. 83-01
Aberdeen, Moore County, North Carolina
�it.rimg' j
,.P t,..
.. _Ple
Mlh,d JjMMjMB,ck,r
... d
•
Ati,, C&D
•
M,,it*ri,g
Well,
•
.•
Ati�.C&DM.�it.ri�gW.11.&MNAP.ff.r..�.eM.�it.ri�gW.11.
f,� the
Cl
11
Cl-d MSW M-ftri.g
Well. & MNA
Peff--e M-i-mg
Well.
Cl ... d MSW
�Sit'
Pri-t. Well
Bl-ks
elver
u9/L
04/28I06
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
= ug
u9/L
10/0906
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
EPAMCL=100 ug/0
u9/L
04/24/07
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
il_
10KI 107
-
-
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23/OB
-
--
10
2.8 B
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
2.1 J
ug/L
10/06/08
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
4.6 B
ND
--
ND
ND
2 J
ug/L
04/13/09
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
3." J
ND
--
ND
ND
ND
ug/L
04/26/10
-
--
10
ND
ND
-
3.57
J
ND
ND
ND
6.48
J
-
-
-
5.35 J
ND
-
--
ND
ND
ND
3.86 J
5.70 J
5.55 J
2.17 J
--
5.29 J
ND
ND
ug/L
10/19/10
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
--
10
ND
ND
-
ND
ND
ND
ND
4.46
J
-
-
-
5.35 J
ND
-
--
ND
ND
ND
5.13 J
ND
5.64 J
1.95 J
--
ND
ND
ND
ug/L
10/10/11
-
--
10
ND
ND
-
ND
ND
ND
ND
8.74
J
-
-
-
ND
ND
-
--
ND
ND
ND
ND
9.37 J
ND
Dry
--
ND
ND
ND
ug/L
04/17/12
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
--
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
2.66 J
2.43 J
Dry
--
ND
ND
ND
ug/L
04/15/13
--
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.19 J
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
--
--
10
ND
ND
-
2.99
J
ND
ND
ND
4.63
J
-
-
-
4A0 J
ND
-
--
ND
ND
ND
4.63 J
5.55 J
2.61 J
Dry
--
4.09 J
ND
ND
ug/L
04/18/14
--
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/15/14
1.9
--
10
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/15
1.9
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
1.9
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11116
1.9
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/i6
1.9
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
1.9
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
-
--
ND
ND
ND
ND
1.92 J
ND
ND
--
ND
ND
ND
ug/L
12/12/17
1.9
--
10
ND
ND
-
2.75
B
ND
ND
ND
1.90
B
-
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
2.43 B
ND
1.95 J
ug/L
O6/20/18
1.9
-
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/ 7118
1.9
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
1.9
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
1.9
10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
an ium
ugtL
O6/20/18
1.4
-
25
ND
-
2.86 J
1.81
J
ND
ND
ND
-
3.39 J
-
-
3.60 J
ND
-
--
--
--
--
4A0 J
3.09 J
--
--
--
--
--
ND
NC2LIMAC=0.3 ug/L
ug/L
11/2]/18
1.4
10
-
ND
-
1.0 J
2.86
J
ND
1.42 J
ND
-
2.90 J
-
-
1.98 J
ND
-
--
--
--
--
-
-
--
--
--
--
--
ND
ugtL
04/02119
1.4
10
-
ND
-
1.0 J
ND
ND
ND
ND
-
2.46 J
-
-
1.68 J
ND
-
--
--
--
--
-
-
--
--
--
--
--
ND
u L
11/19/19
1.4
10
-
ND
-
ND
ND
ND
-
1.92
J -
ND
-
-
ND
-
ND
ND
--
--
-
-
-
--
--
--
--
--
ND
Zinc
ug/L
03/05/90
--
--
--
34
26--
-
43
79
if
-
-
-
-
--
-
ND
-
NC2L=1000 ug/L
ug/L
03/21/91
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
--
-
24
24
ND
--
-
-
--
--
--
ND
--
EPA MCL=5000 ug/L
ugtL
03/10/92
-
-
-
30
-
-
-
-
-
31
-
-
-
-
-
-
--
-
40
31
21
--
--
-
--
--
--
ND
--
--
4]
60
51
--
--
49
ND
--
ugtL
0612]/95
-
-
-
-
ND--
ugtL
09/22/95
-
-
-
ND
-
-
-
-
-
-
-
-
-
-
-
-
--
-
ND
--
--
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
ND
--
--
ND
ND
--
ugtL
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M10 /97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M1 0/98
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/14/98
--
--
--
ND
ND
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M12 /99
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/21/99
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugtL
0314/00
-
-
-
_
_
-
-
_
_
_
_
_
_
_
_
_
--
_
..
..
..
..
..
..
..
..
..
ND
--
ugVL
M1 9/00
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
1017/00
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M1 0/01
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
1011/01
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M11 /02
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/08/02
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M10 /03
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/13/03
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M12
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10125I04
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
-
-
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ugVL
M10 /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ugtL
10/04/05
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
--
-
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/28/06
-
-
-
-
-
--
--
ug/L
10/09/06
-
-
-
-
-
--
--
ug/L
04/24/07
-
-
-
-
-
--
--
ug/L
10/30/07
-
-
-
-
-
--
--
ug/L
04/23/08
ug/L
O6/20/18
4.4
-
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
--
-
--
--
--
ND
ND
-
--
--
--
--
ND
ug/L
11/2]I18
4.4
10
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
--
-
--
--
--
--
--
-
--
--
--
--
ND
ug/L
04/02119
4.4
10
-
ND
-
ND
ND
ND
6.14 J
ND
-
ND
-
-
ND
ND
--
-
--
--
--
--
--
-
--
--
--
--
ND
ug/L
11/19119
44
70
--
ND
-
ND
ND
ND
-
22.6
-
ND
-
-
5.24 J
-
ND
ND
--
--
--
--
--
--
--
--
--
--
ND
C> GOLDER

Page 6 of 20
Project No. 19127453
TABLE 4
Summary of 1-11-1ca1 Groundwater Monitoring Results (De —d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
�it.rimg' j
,.P t,..
.. _P�.
Mlh,d JjMMjMB,ck,r
... d
•
Ati,,
•
C&D M,,it*ri,g
W,11,
•
.•
Ati�.C&DM.�it.ri�gW.11.&MNAP.ff.r..�..M.�it.ri�gW.11.
I. th,
Cl
Cl—d MSW M..Rri.g
W.11. &
MNA P.6--..
M-i-mg W.11.
Cl ... d MSW
�Sit'
Pri-t. W.11
Bl-k.
Iron
ugL
005
d_
2.3.9
0
3
—
—
— --
--
NNDD
----
2L=300 ugL
uL
03191
]09
251
17M
6500
--NC
--
EPA M L=300u L
ugL
031092
213
S
9
3110
3
ND
ugL
020 95
186
_
..
--
13-40
9600
71M
-- --
57200
ND
--
ug/L
06/27/95
—
—
—
_
_
—
_
_
_
_
_
_
_
_
_
—
_ ..
..
..
..
..
..
_ ..
.. ..
..
ND
--
ug/L
09/2 95
—
—
—
ND
_
—
_
_
_
_
_
_
_
_
_
—
_ --
ND
..
--
ND
ND
ND
-- --
ND
ND
--
--
ND
ND
--
ND
ND
ND
-- --
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
—
--
ND
ND
ND
ND --
ND
ND
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uWL
W3 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uWL
W2 199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
03/14/00
—
—
—
_
—
—
_
_
_
_
_
_
_
_
_
_
_ ..
..
..
..
..
..
..
.. ..
..
ND
--
ug/L
04/1900
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/ ] 00
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
04/ 001
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/1101
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
04/1 02
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
NO
NO
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/0 02
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uWL
Wo 103
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10113I03
--
--
--
ND
ND
--
ND
ND
ND
—
ND
—
—
—
— ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uWL
W2
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
—
—
— ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uWL
WO /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/04/05
--
--
--
ND
ND
--
ND
ND
ND
—
ND
—
ND
ND
ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
ug/L
04/28/06
—
—
—
—
—
--
--
ug/L
10/09/06
—
—
—
—
—
--
--
--
ug/L
04/24/07
ug/L
10/30/07
ug/L
04/23I08
ug/L
O6/20/18
22
—
300
72.9 J
—
83700
81400
10300
20200
1790
--
144000
—
--
135000
5220
— --
--
--
--
--
—
--
-- --
--
--
ND
ug/L
11/2]/18
22
50
—
ND
—
88300
62600
21400
23100
41]
—
141000
—
—
142000
10300
— --
--
—
--
--
--
--
-- --
--
--
ND
ug/L
04/02119
22
50
—
ND
—
.2700
65600
28800
23200
MO
—
129000
—
—
134000
3890
— --
--
—
--
--
--
--
-- --
--
--
ND
u L
11/19/19
22
50
—
ND
—
75900
99700
60"
—
15500
—
101000
—
—
152000
—
38400 181
--
—
--
--
--
--
-- --
--
--
ND
Manganese
IL
03/05/90
--
--
—
ND
—
—
—
—
—
ND
—
—
—
—
—
—
— --
31
ND
ND
--
--
--
-- --
--
ND
--
NC2L=50 ug/L
ug/L
OM1191
—
—
—
20
—
—
—
—
—
14
—
—
—
—
—
—
— --
50
50
13
--
--
--
-- --
--
ND
--
EPA MCL=50 ug/L
ug/L
oNl OY92
—
—
—
ND
—
—
—
—
—
ND
—
—
—
—
—
—
— --
4]
32
ND
--
--
--
-- --
--
ND
--
--
23
23
173
-- --
1020
ND
--
ug/L
06/27/95
—
—
—
_
_
—
—
—
_
_
_
—
_
_
—
_
_ ..
..
—
..
..
..
..
.. ..
..
ND
--
--
ND
--
ND
ND
ND
-- --
ND
ND
--
ug/L
03/28/96
--
--
--
ND
—
--
--
—
—
—
—
—
—
—
—
—
— --
ND
ND
--
ND
ND
ND
-- --
ND
ND
--
UW
10129/96
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
0108/97
--
--
--
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
10129/97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
M130/98
--
--
--
ND
ND
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
10114/98
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
04/27/99
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
10121/99
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
03/14/00
—
—
—
_
_
—
—
_
_
_
_
_
_
_
_
_
_ ..
..
..
..
..
..
..
.. ..
..
ND
--
uw
W19/00
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/17/00
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
W10/01
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/11/01
--
--
--
ND
ND
--
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
W18/02
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/08/02
--
--
--
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
—
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
W09/03
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
ug/L
10/13/03
--
--
--
ND
ND
—
ND
ND
ND
—
ND
—
—
—
ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
�Ml�
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
uw
10/25104
--
--
--
ND
ND
—
ND
ND
—
—
ND
—
—
—
ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
W04/05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND --
ND
ND
--
uw
10/04105
--
--
--
ND
ND
—
ND
ND
ND
—
ND
—
ND
ND
ND
ND
— --
--
--
--
ND
ND
ND
ND --
ND
ND
--
uw
04/28106
—
—
—
—
—
--
--
ug/L
10/09106
—
—
—
—
—
--
--
uw
04/24107
—
—
—
—
—
--
--
--
ug/L
10/30107
—
—
—
—
—
--
--
uw
04/23108
ug/L
O6/20118
1.5
—
50
ND
—
200
11
18.9
J 13
40.2 J
3
86
.63
--
----
----
----
----
----
----
----
----
----
----
----
ND
112]8
0
10
—
1]3
203
14]
58.2
125
103
384
1
NDugL
0/02I
352 J
—
1
1
146
8
174
68.
NDug/L
ug/L
11/9
10
—
2.68 J
19
1
188
15.2
--
131
--
248
--
—
212
—
114 2.71 J
--
--
--
--
--
--
-- --
--
--
ND
C> GOLDER

Page ] of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det-d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
Ati,,
•
C&D M,,it.ri,g
W,11,
•
.•
Adw. C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
M-it.rmg W.11.
Cl-d MSW M..ftrJ.g
We 1. & MNA
Peff--e M-it.dmg
Well.
Cl ... d MSW
Olfsit'
Acetone
u9/L
03I05/90ND
--
NC2L=6000 u9/L
ug/L
OM1191
-
-
-
_
_
-
-
-
_
_
-
-
_
_
_
-
_ ..
..
..
..
..
..
-
-
..
..
ND
--
ug/L
03/10/92
N D--
ug/L
04/20/95
ND--
ug/L
06/2] 95
-
-
-
-
-
--
ND
ND
--
--
ND
ND
--
ug/L
09/22195
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
- --
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO 97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W3 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
3085
ND
--
uWL
W2 199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
541
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
335
3%
ND
ND
--
108
ND
--
uWL
OW 4100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
139
--
728
ND
--
ug/L
10/ ] 00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
185
ND
ND
ND
--
2628
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
167
-
ND
ND
ND
-
- --
--
--
--
129
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
422
110
ND
ND
--
ND
ND
--
ug/L
04/09/03
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
192
ND
ND
--
119
ND
--
ug/L
10/13I03
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
125
113
ND
ND
--
ml
ND
--
uWL
W2
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/04I05
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
ND
1400
ND
ND
--
123
ND
--
uWL
1010 /05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/28106
--
--
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09106
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/24107
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
in
ND
ND
--
ND
ND
--
ug/L
10130107
-
-
100
ND
ND
-
ND
ND
ND
ND
17
-
-
-
4.8 J
4.3
J - --
ND
ND
ND
no
60
7.]
5.6
--
16
ND
ND
ug/L
04/23108
-
-
100
ND
ND
-
ND
37 J
ND
5.7 J
15
J -
-
-
ND
5.5
J - --
ND
ND
ND
420
120
10
J ND
--
220
ND
ND
ug/L
10/06108
-
-
100
ND
4.9 B
-
5.3
B
ND
5.1 B
ND
280
-
-
-
7.6 B
ND
- --
ND
ND
ND
1100
160
20
B 210
--
56 J
ND
5.0 J
ug/L
04/13/09
-
-
100
ND
ND
-
ND
ND
ND
ND
88
J -
-
-
ND
ND
- --
ND
ND
ND
48 J
240
ND
45 J
--
160
ND
ND
ug/L
10/15109
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
78 J
ND
ND
--
ND
ND
ND
ug/L
04/26110
-
-
100
ND
ND
-
ND
ND
ND
ND
6.2
J -
-
-
ND
2.3
J - --
ND
ND
ND
80 J
25 J
8.9
J 140
--
]] J
ND
ND
ug/L
1019/10
-
-
100
ND
ND
-
ND
ND
ND
ND
7.0
J -
-
-
ND
ND
- --
ND
ND
ND
180
1700
ND
170
--
ND
ND
ND
ug/L
04/18/11
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
10
J - --
ND
ND
ND
29 J
36 J
36
J ND
--
ND
ND
ND
ug/L
1010/11
-
-
100
ND
ND
-
82
J
ND
ND
ND
ND
-
-
-
ND
4.4
J - --
ND
ND
ND
15 J
--
5.0
J Dry
--
ND
ND
ND
ug/L
04/1]112
-
-
100
ND
ND
-
ND
ND
ND
ND
10
J -
-
-
ND
6.0
J - --
ND
ND
ND
10 J
56 J
18
J Dry
--
12 J
ND
ND
ug/L
10/09112
-
-
100
ND
ND
-
ND
ND
ND
ND
16
J -
-
-
ND
5.1
J - --
ND
ND
ND
ND
290
13
J Dry
--
ND
ND
ND
ug/L
04/15113
--
-
100
ND
ND
-
26
J
ND
ND
ND
6.3
J -
-
-
ND
10
J - --
ND
ND
ND
150
88 J
12
J Dry
--
73 J
ND
ND
ug/L
09/30113
--
-
100
ND
ND
-
11
J
ND
ND
ND
18
J -
-
-
ND
5.6
J - --
ND
ND
ND
94 J
24 J
5.5
J Dry
--
9.8 J
ND
ND
ug/L
04/16114
--
-
100
ND
ND
-
8.4
J
ND
5.2 J
ND
37
J -
-
-
ND
27
J - --
ND
ND
ND
280
36 J
15
J Dry
--
fi.3 J
ND
ND
ug/L
1011 14
1.2
-
100
Dry
ND
-
ND
ND
7.4 J
ND
14
J -
-
-
ND
25
J - --
ND
ND
ND
16 J
110
12
J Dry
--
66 J
ND
ND
ug/L
04/15I15
1.2
-
100
ND
ND
-
ND
ND
13 J
ND
32
J -
-
-
ND
10
J - --
ND
ND
ND
210
110
7.0
J Dry
--
16 J
ND
ND
ug/L
1010]115
1.2
-
100
ND
ND
-
13
J
ND
9.4 J
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
130
200
2.6
J 98 J
--
64 J
ND
ND
ug/L
04/11116
1.2
--
100
ND
ND
-
ND
ND
ND
ND
52
J -
-
-
ND
21
J - --
ND
ND
ND
290
110
55
J 300
--
ND
ND
ND
ug/L
11/30/16
10
--
100
ND
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13 J
ND
ND
-
-
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12
J - --
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ND
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46 J
10 J
19
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04/11/17
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--
100
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ND
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ND
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ND
20 J
ND
880
--
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ND
ND
ug/L
12/12117
10
--
100
ND
ND
-
ND
ND
ND
ND
ND
-
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ND
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ND
ND
ND
ND
ND
11
J 20 J
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ND
ND
ND
ug/L
O6/20/18
10
-
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ND
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ND
ND
2fi B
ND
-
ND
-
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ND
ND
- --
ND
ND
ND
20 B
19 B
20
B --
ND
11 B
ug/L
11/2]/18
10
20
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ND
-
ND
ND
ND
ND
ND
-
ND
-
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ND
ND
- --
ND
ND
ND
28
190
51
--
ND
5fi
ND
ND
ug/L
04/02119
10
20
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ND
-
ND
ND
ND
ND
ND
-
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-
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ND
ND
ND
12 J
490
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--
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21
ND
ND
u L
11/19/19
10
20
ND
ND
ND
ND
ND
ND
ND
NO ND
ND
ND
ND
ND
12 J
ND
190
ND
ND
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Beene
ug/L
03/05/90
--
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--
NC2L=1 ug/L
ug/L
OM1191
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_
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--
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ug/L
ON10192
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--
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--
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04/20/95
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--
8.8
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09/22195
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-
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-
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ND
-
-
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ND
ND
ND
ND
6
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03/28196
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--
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10/29196
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04/0819]
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ND
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04/30/98
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10/14/98
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-
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ND
8.5
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u9/L
04/27/99
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ND
-
ND
ND
-
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ND
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ND
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5.3
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6.2
10
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10/21/99
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-
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ND
ND
-
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11
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3
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ND
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4
11
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04/19/00
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-
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uw
10117100
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04/10/01
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-
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ND
-
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ND
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-
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ND
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ND
--
u9/L
10/11/01
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04/18/02
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-
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ND
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-
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--
uw
10108102
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ND
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ND--
--
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ND
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04/09/03
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ND
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ND
-
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ND
ND
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ND
ND
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--
uw
10113103
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04/26104
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ND
--
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ND
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-
ND
-
-
-
ND
ND
- --
--
--
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ND
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1 o/n/m
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04/04105
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,> GOLDER

Page 8 of 20
Project No. 19127453
TABLE 4
Summary of Hl,terical Groundwater Monitoring Result, (Detected Conetlt... t,)
Water Quality Monitering Report, 2019 Second Seml-Annual Sampling Event
Moor. County Landfill, NC Solld Waste Permit No. 83-01
Aberdeen, Moore County, North Carolina
Dt..t.d M-it.limg
th,d J"MIMBIC1,1111"d
Ati,,
C&D M,,it.,i,g
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--
—
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--
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ug&
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—
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—
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—
—
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—
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--
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--
ug/L
03/10/92
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04/20/95
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—
—
—
—
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ND
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--
--
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09/22I95
—
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—
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—
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ND
ND
ND
ND
--
--
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--
--
ND
ND
--
ND
ND
ND
--
--
ND
ND
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ug/L
10/29/96
--
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--
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ND
—
ND
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—
—
ND
—
ND
ND
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— — --
--
--
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ND
ND
ND
--
ND
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--
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ND
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--
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10/29/97
--
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ND
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—
—
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—
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— — --
--
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ND
ND
ND
--
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N
ND
ND
ND
ND
ND
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ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
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81
—
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—
—
ND
—
ND
ND
ND
— — --
--
--
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ND
ND
ND
ND
--
ND
ND
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uWL
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ND
ND
ND
ND
ND
ND
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ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
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ND
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ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
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ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ ] 00
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
NO
NO
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
—
—
—
ND
ND
—
ND
ND
—
—
ND
—
ND
ND
ND
— — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
M/0 103
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10113I03
--
--
--
ND
ND
—
ND
ND
ND
—
ND
—
—
—
ND
ND — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
M/2
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
—
ND
ND
ND
—
ND
—
—
—
ND
ND — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
�10 /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04/05
--
--
--
ND
ND
—
ND
ND
ND
—
ND
—
ND
ND
ND
ND — --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
M12 /06
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09/06
--
--
--
ND
ND
—
ND
ND
ND
ND
ND
—
ND
ND
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
uWL
M12 /07
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10130/07
--
--
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23/08
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010 /08
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26/10
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1019/10
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010/11
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]/12
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/14
—
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1011 14
0.48
—
3
Dry
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.48
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1010]115
0.48
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11116
0.48
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.48
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.48
—
3
ND
ND
--
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12117
0.48
—
3
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
0.48
—
3
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]/18
0.48
1
—
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02119
0.48
1
—
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.48
1
—
ND
—
ND
ND
ND
—
ND
—
ND
—
—
ND
— ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Carbon disulfide
ug/L
10/30/07
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
NC 2L=700 ug/L
ug/L
04/23/08
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06/08
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26/l0
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/19/10
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
Uw
10110111
100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
Dy
ND
ND
ND
ug/L
04/17/12
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
1.6 1
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/13
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
—
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/14
--
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/16/14
1.5
--
100
Dry
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/15
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/16
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12/17
1.5
--
100
ND
ND
—
ND
ND
ND
ND
ND
—
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20118
1.5
--
100
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]I18
1.5
5
—
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND — --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02119
ND
—
ND
ND
ND
ND
ND
—
ND
—
—
ND
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
11/19119
1.5
5
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
,> GOLDER

Page 9 of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det-d Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
M-111•
Ati,, C&D
•
M,,it.ri,g W,11,
•
r
Adw. C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
r
M-it.rimg W.11.
,
Cl-d MSW M..Rri.g
We 1.
& MNA Peff--e
M-it.,mg Well.
Cl ... d MSW
Offsit'
Carbon iMachlaritle
u9/L
03/OS/90
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
-
-
--
-
-
--
--
ND
--
NC2L=0.3ug/L
ug/L
03/21/91
-
-
-
_
-
-
-
_
_
-
-
_
_
_
-
_ ..
..
..
..
..
..
-
-
..
..
ND
--
EPA MCL = 5 ug/L
ug/L
03/10/92
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
ug/L
04/20/95
-
-
-
-ND
ug/L
06/2] 95
-
-
-
-
--
ND
ND
ND
--
--
ND
ND
--
ug/L
09/22I95
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
---
ND
ND
ND
9
ND
ND
--
--
ND
ND
--
--
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO 97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W3 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
OW 4100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ ] 00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
Wo 103
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/13103
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04105
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 /06
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09106
--
--
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 /07
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/30107
--
--
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23108
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06108
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15109
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26110
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1019/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010/11
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]112
-
-
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09112
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15113
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30113
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16114
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1011 14
0.17
-
1
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.17
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
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ND
ND
ND
ND
ND
ND
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--
ND
ND
ND
ug/L
1010]115
0.17
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
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ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11116
0.17
-
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ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
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ND
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ug/L
11/30/16
0.17
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.17
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12117
0.17
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
0.17
-
1
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
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--
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ug/L
11/2]/18
0.17
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-
ND
-
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ND
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-
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ND
ND
ND
ND
--
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ND
ND
ND
ug/L
04/02119
0.17
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.17
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Chlarabenzene
ug/L
03/05/90
--
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
NC2L=50 ugll.
ug/L
OM1191
-
-
-
_
_
_
_
_
_
_
_
_
_
_
_
_
_ ..
..
..
..
..
..
..
..
..
..
ND
--
EPA MCL=100 ug/L
ug/L
ON10192
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
ug/L
04/20/95
-
-
-
_
_
-
-
_
_
_
_
_
_
_
_
_
_ ..
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..
..
..
..
..
..
..
..
ND
--
uw
OM7195--
ND
ND
6.5
--
ND
ND
--
ug/L
09/22195
--
--
--
ND
-
--
--
-
-
ND
-
-
-
-
-
-
- --
ND
ND
ND
ND
ND
6
--
--
ND
ND
--
uw
OM8196
ND--
ND
ND
--
ND
ND
ND
--
ND
ND
--
ug/L
10/29196
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
UW
M/08197
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
7.5
ND
--
ND
ND
--
UW
W30/98
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
5.4
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
5.1
ND
--
ND
ND
--
UW
��7199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
6.1
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
7.1
ND
--
ND
ND
--
UW
ON14100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
3
ND
ND
ND
6
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
32
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
-
ND
ND
5.5
ND
ND
ND
ND
ND
ug/L
04/10/01
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
7.3
ND
--
ND
ND
--
uw
10111101
ND
ND
ND
ND
ND
ND
ND
ND
N D
ND
13
N D
ND
ND
uw
04/18/02
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
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ND
ND
10.5
ND
--
ND
ND
--
uw
10108102
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ND
ND
ND
ND
ND
ND
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ND
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8.6
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--
ND
ND
--
uw
04/09/03
--
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--
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-
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10113103
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04/26104
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--
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-
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--
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10.9
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--
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uw
1 M51M
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11.9
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uw
04/04105
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--
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ND
ND
--
ND
ND
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-
ND
-
-
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ND
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10104105
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ND
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--
uw
04/28/06
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--
--
ND
ND
-
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ND
ND
-
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ND
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78
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--
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--
uw
10/09/06
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uw
04/24/07
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ND
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-
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uw
10/30/07
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04/13/09
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,> GOLDER

Page 10 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
Ati,,
•
C&D M,,it.ri,g
W,11,
•
r
Adw. C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
r
M-it.rimg W.11.
,
Cl-d
MSW M..Rri.g
We 1. & MNA
Peff--e M-it.,mg
Well.
Cl ... d MSW
Offsit'
Chlorcelhane
u9/L
03/OS/90
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
-
-
--
-
-
--
--
ND
--
NC2L=3000 u9/L
ug/L
OM1191
-
-
-
_
_
-
-
-
_
_
-
-
_
_
_
-
_ ..
..
..
-
..
..
-
-
..
..
ND
--
ug/L
03/10/92
-
-
-
-
-
--
ug/L
04/20/95
-
-
-
-
-
--
ug/L
06/2] 95
-
-
-
-
-
--
13.3
4.2
8.5
--
--
6.6
ND
--
ug/L
09/22I95
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
---
ND
ND
ND
12
14
ND
--
--
ND
ND
--
--
ND
ND
--
23
14
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
-
-
ND
ND
-
-
-
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO 97
ND
-
ND
ND
ND
ND
ND--
23
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
17
ND
ND
ND
--
ND
ND
--
ug/L
04/30/98
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
19
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
16
ND
ND
ND
--
ND
ND
--
ug/L
04/2]/99
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
15
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
11
ND
ND
ND
--
ND
ND
--
uWL
OW 4100
ND
ND
ND
ND
ND
2
ND
ND
ND--
ND
ND
ND
6
ND
ND
2
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ ] 00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
Wo 103
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10113I03
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04/05
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 /06
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09/06
--
--
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/24/07
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10130/07
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
1.3 J
ND
ND
ND
--
ND
ND
ND
ug/L
04/23/08
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010 /08
-
--
10
ND
ND
-
ND
ND
ND
ND
2.0 J
-
-
-
1.2 J
ND
- --
ND
ND
ND
4.8 J
0.55 J
1.3
J 2.5 J
--
0.]8 J
ND
ND
ug/L
04/13/09
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
1.1 J
ND
ND
ug/L
10/15/09
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26/10
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1019/10
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
--
10
ND
ND
-
ND
ND
ND
ND
0.80 J
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010/11
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]/12
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
0.54 J
ND
ND
ug/L
10/09/12
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.65 J
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
0.79 J
ND
ND
ug/L
09/30/13
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/14
--
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1011 14
0.23
--
10
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.23
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1010]115
0.23
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/i6
0.23
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.23
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.23
--
10
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12117
0.23
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
0.6 J
--
ND
ND
ND
ug/L
O6/20/18
0.23
--
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]/18
0.23
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02119
0.23
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.23
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1,2-Dichlaraben-.
ug/L
04/24/07
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
EPA MCL=600u L
ug/L
10/09I0]
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ugrL
10/30/07
-
-
5
ND
0.33 J
-
ND
ND
ND
ND
0.39 J
-
-
-
2.7 J
0.T1
J - --
ND
0.75 J
ND
ND
ND
0.61
J ND
--
0.81 J
ND
ND
ug/L
04/23/08
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.1 J
ND
- --
ND
0.43 J
ND
ND
ND
0.69
J ND
--
ND
ND
ND
ug/L
10/06/08
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.5 J
ND
- --
ND
0.42 J
ND
ND
ND
0.64
J ND
--
ND
ND
ND
ug/L
04/13I09
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.3 J
0.49
J - --
ND
0.64 J
ND
ND
ND
0.73
J ND
--
ND
ND
ND
ug/L
10115I09
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.2 J
0.75
J - --
0.62 J
0.67 J
ND
ND
ND
0.69
J ND
--
0.81 J
ND
ND
ug/L
04/26I10
-
-
5
ND
ND
-
ND
ND
ND
ND
0.50 J
-
-
-
2.0 J
ND
- --
ND
0.50 J
ND
ND
ND
0.82
J ND
--
ND
ND
ND
ug/L
1019110
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.1 J
0.57
J - --
ND
0.53 J
ND
ND
ND
0.88
J ND
--
ND
ND
ND
ug/L
04/18/11
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.0 J
0.64
J - --
ND
0.43 J
ND
ND
ND
0.67
J ND
--
0.51 J
ND
ND
--
0.47 J
0.49 J
ND
ND
--
0.49
J Dry
0.86 J
ND
ND
ug/L
04/1]/12
-
-
5
ND
0.36 J
-
ND
ND
ND
ND
0.33 J
-
-
-
2.0 J
0.75
J - --
0.49 J
0.64 J
ND
ND
ND
0.66
J Dry
--
ND
ND
ND
ug/L
10/09/12
--
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
2.0 J
0.54
J - --
ND
0.49 J
ND
ND
ND
0.76
J Dry
--
0A8 J
ND
ND
ug/L
04/15113
--
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.7 J
0.56
J - --
ND
ND
ND
ND
ND
0.65
J Dry
--
ND
ND
ND
ug/L
09/30/13
--
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.2 J
0.45
J - --
ND
ND
ND
ND
ND
0.72
J Dry
--
ND
ND
ND
ug/L
04/16/14
--
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.] J
ND
- --
ND
ND
ND
ND
ND
0.68
J Dry
--
ND
ND
ND
ug/L
101 W14
0.19
-
5
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
1.3 J
0.54
J - --
ND
ND
ND
ND
ND
0.58
J Dry
--
0.59 J
ND
ND
ug/L
04/15115
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.4 J
0.72
J - --
ND
ND
ND
ND
ND
0.51
J Dry
--
ND
ND
ND
ug/L
1010]115
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.1 J
0.50
J - --
ND
0.42 J
ND
ND
ND
ND
ND
--
0.65 J
ND
ND
ug/L
04/11/i6
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
1.0 J
0.59
J - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.92 J
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.94 J
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
0.5] J
ND
ND
ug/L
12/12117
0.19
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.B2 J
0.41
J - --
0.44 J
ND
ND
ND
ND
ND
ND
--
0.59 J
ND
ND
ug/L
O6/20/18
0.19
-
5
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]/18
0.19
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
1.1
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
0.19
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
1.1
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
uq/L
11/19/19
0,19
1
ND
ND
ND
ND
ND
ND
1.8
ND ND
ND
ND
ND
ND
049 J
0.41
J
ND
0.84 J
ND
ND
,> GOLDER

Page 11 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
Ati,, C&D
•
M,,it.ri,g W,11,
•
r
Adw. C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
r
M-it.rimg W.11.
,
Cl-d MSW M..Rri.g
We 1. & MNA
Peff--e M-it.,mg
Well.
Cl ... d MSW
Offsit'
1,4-Dlchlarabenzene
ug/L
03/OS/90
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
-
-
--
-
-
--
--
ND
--
NC2L=6 ug/L
ug/L
OM1191
-
-
-
_
_
-
-
-
_
_
-
-
_
_
_
-
_ ..
..
..
..
..
..
-
-
..
..
ND
--
EPA MCL=]5 ug/L
ug/L
03/10/92
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
-
--
--
ND
--
ug/L
04/20/95
N D--
ug/L
06/2] 95
-
-
-
-
-
--
ND
3.3
7.4
--
--
2
ND
--
ug/L
09/22I95
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
---
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ND
ND
ND--
ND
ND
]
6
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
].8
-
- --
--
--
--
ND
ND
]
fi.i
--
ND
ND
--
ug/L
04/30/98
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
7.1
ND
--
ND
ND
--
uWL
1011 198
ND
ND
ND
ND
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- --
ND
ND
ND
0.50 J
ND
ND
Dry
--
0.87 J
ND
ND
ugtL
04/15/15
0.13
--
5
ND
3.0
J --
ND
ND
ND
ND
0.49
J -
-
-
ND
0."
J - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ugtL
1010]115
0.13
--
5
ND
3.9
J --
ND
ND
0.45 J
ND
0.53
J -
-
-
0.]3 J
ND
- --
ND
ND
ND
0.58 J
ND
ND
1.1 J
--
0.62 J
ND
ND
uglL
04/111i6
0.13
--
5
ND
1.]
J --
ND
ND
0.62 J
ND
0.42
J -
-
-
0.66 J
ND
- --
ND
ND
ND
ND
ND
ND
0.90 J
--
0.61 J
ND
ND
ugtL
11/30/16
0.13
--
5
ND
1.9
J --
ND
ND
0.48 J
ND
0.44
J -
-
-
0.59 J
ND
- --
ND
ND
ND
ND
ND
ND
0.]] J
--
0.]0 J
ND
ND
ug/L
04/1111]
0.13
--
5
ND
2.8
J --
ND
ND
0.68 J
ND
0.58
J -
-
-
0.61 J
ND
- --
ND
O.dd
J ND
ND
ND
ND
ND
--
1.1 J
ND
ND
ugtL
12/12/17
0.13
--
5
ND
1.]
J --
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
0.66 J
--
0.48 J
ND
ND
ugtL
O6/20/18
0.13
--
5
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
0.49 J
--
ND
ugtL
11/2]I18
0.13
1
--
ND
-
0.64 J
ND
ND
ND
ND
-
ND
-
-
0.50 J
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
0.13
1
--
ND
-
ND
ND
ND
0.]6 J
ND
-
ND
-
-
ND
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
11/19/19
0.13
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
0.93 JI
ND
I ND
I ND
,> GOLDER

Page 12 d 20
Project No. 19127453
TABLE 4
Summary of Hl,terical Groundwater Monitoring Result, (Detected Conetlt... t,)
Water Quality Monitering Report, 2019 Second Seml-Annual Sampling Event
Moor. County Landfill, NC Solld Waste P-lt No. 83-01
Aberdeen, Moore County, North Carolina
th,d J'MMjW'M..,ctl,.r
... d
•
Ati,,
C&D M-it
ri,g Well,
r
r
Adim C&D M-it.rmg Well.
& MNA P.ff.r.-e M-it.rimg Well.
Cl-d MSW M-ftri.g
Well. & MNA
Peff--e
M-it.dmg
Well.
Cl ... d MSW
Offsit'
1,2-Dlchlorae0i...
u9/L
10/30/01
-
-
1
ND
ND
ND
NC2L=0.4 ug/L
ug&
04/23I08
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
EPA MCL=5ug/L
ug/L
1010&08
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/ wio
-
-
1
ND
0.45 J
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/19/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- --
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
-
1
ND
0.48 J
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/10/11
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]/12
-
-
1
ND
0.40 J
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/1&14
--
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
1.4
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/15/14
0.21
-
1
Dry
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/15
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11116
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30116
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12/17
0.21
-
1
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
0.21
-
1
ND
-
ND
ND
ND
ND
ND
-
ND -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/27/18
0.21
1
-
ND
-
ND
ND
ND
ND
ND
-
ND -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
0.21
1
-
ND
-
ND
ND
ND
ND
ND
-
ND -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.21
1
-
ND
-
ND
ND
ND
-
ND
-
ND -
- ND
-
ND
ND
ND
N......D
ND
N...D..
N3......D
N....D
N------D
ND
D
N----
cis-1,2-Dicharcthe
l
ugL
428O6
ND
31
ND
84
.......
ND
13.9
16.3
13
ND
6.4
ND
196
ND
ND
18.4
ND
ND
NC2L=70 ugL
ug
10/09/06
ND
263
..
ND
ND
8.
ND
12
13
11.3
ND
1
ND
43
9.5
9.3
19.4
ND
ND
-
EPA MCL=70ug/L
ug
4/24/07
ND
214
-----
ND
5
121
ND
83
...............
19.3
87
ND
ND
ND
15.3
ND
ND
7.3
ND
ND
-
ug
10/30/07
5
ND
25
38
..........
J
3.0
J
5.3
4.4 J
98
20
1.2
ND
5.1
0.35 J
14
6.4
1.6
J 1]
...D
30 J
ND
ND
ug
4/23/08
5
ND
19
36
J
11
ND
ND
98
20
].0
-
ND
3
J ND
.8 J
1
J 22
3
J .2 J
ND
ND
ND
ug
10/06/08
5
ND
22
1.6
J
32
..
J
4.3 J
ND
87
14
5.2
ND
2.08
J ND
25
J 12
ND
ND
ND
ug
4/13/09
5
ND
19
2
J
3.6
J
24 J
ND
23
J
14
64
..........
ND
37
J ND
ND
29
J 12
ND
ND
ND
ug
10/15/09
5
ND
22
43
J
2.0
J
30 J
6.2
81
17
12
19 J
4.6
J 041 J
15
5.1
1.8
J 16
50
ND
ND
ug
4/26/10
5
ND
18
30
J
2.6
J
2.9 J
O.fiO J
80
13
52
ND
2.8
J 0.43 J
7.5
32
J 2.3
J 7.2
ND
ND
ND
ug
10/19/10
5
ND
23
34
J
2.6
J
44 J
ND
57
13
68
ND
30
J ND
84
ND
28
J 10
ND
ND
ND
ug
4/18/11
5
ND
18
28
J
2.1
J
20 J
ND
63
12
82
ND
2.8
J ND
68
3.4
J 1.9
J 11
ND
ND
ND
ug
10/10/11
5
ND
19
34
J
2.0
J
3.4 J
3.0 J
67
12
91
1.5 J
2.6
J ND
1.3
1
J Dry
28 J
ND
ND
ug
4/11/12
5
ND
19
33
J
1.9
J
0.J
1.8 J
64
11
80
4 J
22
J 0.39 J
16
28
J 1.6
J Dry
ND
ND
ND
ug
10/09/12
5
ND
18
2.2
J
1.6
J
2.05 J
ND
66
7.0
55
15 J
25
J ND
9.1
32
J 2.0
J Dry
N
ND
ND
ug
4/15/13
5
ND
23
18
J
J
2J
ND
69
7.3
66
ND
1.7
J ND
11
1.2
J 1.7
J Dry
ND
ND
ND
ug
09/30/13
5
ND
14
1.2
J
1.9
J
3.2 J
ND
1.8
J
-- --
4.0 J
--
43
J
ND
1.2
J ND
56
27
J 1.7
J Dry
ND
ND
ND
ug
0116/14
5
ND
16
0.fi6
J
1.9
J
6.8
ND
24
J
6.7
2.1
J
ND
1
J ND
6
1
J 2.1
J Dry
ND
ND
ND
ug
10/15/14
0.15
5
Dry
17
1.3
J
1.4
J
4.9 J
0.4J
2.9
J
53
....
5.5
070 J
1.6
J ND
4.3 J
2.65
J 1.2
J Dry
ND
ND
ND
ug
4/15/15
0.15
5
ND
4
0.]6
J
0.72
J
3.7 J
3.1 J
2.2
J
34 J
6.4
ND
2.0
J ND
1J
047
J 0.89
J Dry
ND
ND
ND
ug
10/07/15
0.15
5
ND
15
1.3
J
1.5
J
2.9 J
ND
25
J
43 J
2.5
J
ND
17
J ND
2.6 J
2.7
J 0.69
J 1.5 J
--
ND
ND
ND
ug/L
04/11/i6
0.15
-
5
ND
8.6
-
0.82
J
1.4
J
3.9 J
1.0 J
1.1
J
- -
- 3.1 J
3.9
J -
--
ND
0.88
J ND
2.0 J
0.49
J 0.85
J OA2 J
--
0.50 J
ND
ND
ug/L
11/30/16
0.15
-
5
ND
8.8
-
0.79
J
0.94
J
3.9 J
0.58 J
1.5
J
- -
- 3.6 J
1.7
J -
--
ND
0.68
J ND
2.0 J
2.1
J 0.63
J 0.53 J
--
0.52 J
ND
ND
ug/L
04/11/17
0.15
-
5
ND
10.0
-
1.4
B
1.3
B
3.8 J
ND
1.2
B
- -
- 3.0 J
3.0
J -
--
ND
1.9
B ND
2.5 B
ND
0.60
B ND
--
0.fifi B
ND
0.54 J
ug/L
12/12/17
0.15
-
5
ND
9.9
-
1.6
J
0.84
J
4.3 J
ND
1.6
J
- -
- 2.2 J
3.4
J -
--
1.1 J
0.81
J ND
0.68 J
1.8
J 0.84
J 1.0 J
--
2.0 J
ND
ND
ug/L
O6/20/18
0.15
-
5
ND
-
2.6
J ND
ND
2.8 J
ND
-
1.6 J -
- 3.0 J
ND
-
--
ND
1.2
J ND
4.4 J
1.0
J 0.54
J --
1.9 J
ND
--
ND
ug/L
11/2]/18
0.15
1
-
ND
-
3.6
0.40
J
1.5
3.1
0.80 J
-
1.8 -
- 3.0
ND
-
--
ND
ND
ND
3.3
0.64
J 1.0
--
1.6
ND
ND
ND
ug/L
04/02/19
0.15
1
-
ND
-
3.3
0.fi2
J
0.98
J
4.8
ND
-
1.1 -
- 2.3
ND
-
--
ND
0.44
J ND
1.3
ND
1.3
--
2.5
ND
ND
ND
u L
11M9/19
0.15
1
-
ND
-
2.4
1.1
0.71
J
-
1.5
-
1.1 -
- 3.9
-
1.8
ND
0.72 J
0.84
J ND
1.5
2.0
0.43
J
0.76 J
ND
ND
ND
trans-1,2-Dichlorcethene
ugtL
04/28/O6
--
-
-
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
NC2L=100 ug/L
ugtL
10/09/O6
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
EPAMCL=100ug/L
ug/L
'4107
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/30/07
-
-
5
ND
4.2 J
-
ND
ND
ND
ND
4.1
J
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ugtL
04/23/OB
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010&08
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26/10
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/19/10
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/10/11
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/17/12
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
--
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ND
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ND
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ND
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ND
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ND
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--
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ND
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ug/L
04/16/14
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ND
ND
ND
ND
- -
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ND
-
--
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ND
ND
ND
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ND
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ug/L
10/15/14
0.21
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ND
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ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/15
0.21
-
5
ND
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-
ND
ND
ND
ND
ND
- -
- ND
ND
-
--
ND
ND
ND
ND
ND
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--
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ug/L
10/07/15
0.21
-
5
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ND
ND
ND
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ND
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04/11116
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11/30/16
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04/11/17
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12/12/17
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11/19119
0.21
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ND
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,> GOLDER

Page 13 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
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ug/L
03/10/92
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-
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04/20/95
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ND
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09/22I95
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- ---
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ND
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ND
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ug/L
10/29/96
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ND
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-
-
ND
-
ND
ND
ND
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--
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10/29/97
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10/14/98
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ug/L
10/21/99
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ND
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-
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ND
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ND
ND
ND
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--
--
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ND
ND
ND
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ND
ND
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ND
ND
ND
ND
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ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
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ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
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--
ug/L
10/ ] 00
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ND
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ND
- - --
--
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ND
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--
ug/L
04/ 001
-
-
-
ND
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-
ND
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-
-
ND
-
ND
ND
ND
- - --
--
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--
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ND
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ug/L
10/1101
-
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ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
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--
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--
uWL
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10/13103
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ND
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--
ug/L
10/04/05
--
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-
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ND
ND
-
ND
-
ND
ND
ND
ND - --
--
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ND
ND
ND
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--
uWL
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ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09/06
--
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-
ND
ND
ND
ND
ND
-
-
-
ND
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ND
ND
ND
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10/30/07
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1010 /08
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04/13/09
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-
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10/15/09
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-
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04/26/10
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04/18/11
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1010/11
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ND
ND
ND
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ND
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--
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04/1]/12
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-
1
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ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
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--
ND
ND
ND
ug/L
10/09/12
-
-
1
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-
ND
ND
ND
ND
ND
-
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ND
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ND
ND
ND
ND
ND
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--
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04/15/13
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-
1
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-
ND
ND
ND
ND
ND
-
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-
ND
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ND
ND
ND
ND
ND
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--
ND
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ug/L
09/30113
-
-
1
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ND
ND
ND
ND
-
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ND
ND - --
ND
ND
ND
ND
ND
ND
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--
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ND
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ug/L
04/16114
-
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1
ND
ND
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ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
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--
ND
ND
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ug/L
1011 14
0.13
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ND
ND
ND
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-
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ND
ND
ND
ND
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--
ND
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ug/L
04/15115
0.13
-
1
ND
ND
-
ND
ND
ND
ND
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-
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ND
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ND
ND
ND
ND
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0.13
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ND
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0.62 1
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0.66 1
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ND
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04/11116
0.13
-
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ND
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-
ND
ND
ND
ND
ND
-
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-
ND
ND - --
ND
ND
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ND
ND
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11/30/16
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0.48 J
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04/11/17
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ND
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12/12117
0.13
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0.48 J
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O6/20/18
0.13
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0.41 J
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0.46 1
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04/02119
0.13
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11/19/19
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0.58 3
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03/05/90
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NC2L=3 u9/L
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03/21191
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03/10192
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04/20/95
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09/22195
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04/08/97
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uw
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26
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04/30198
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ND
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40
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uw
10114198
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32--
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04/27199
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03/14100
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04/10101
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10/11101
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04/18102
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10/08102
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04/09103
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10/13103
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04/26104
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ug/L
10/25/04
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-
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04194/05
-
-
--
ND
ND
--
ND
ND
ND
-
ND
-
ND
ND
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04/05
-
-
--
ND
ND
--
ND
ND
ND
-
ND
-
ND
ND
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04Y28/06
-
--
--
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09/06
-
--
--
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/24107
-
--
--
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/30107
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23108
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06108
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13109
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15109
-
-
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26110
-
-
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/19110
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
0.67
1 ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18111
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/10/11
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]/12
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09/12
-
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
-
-
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
--
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16/14
--
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/15/14
0.13
--
1
Dry
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/15
0.13
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
0.13
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/16
0.13
-
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.13
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.13
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12/17
0.13
--
1
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
06/20/18
0.13
--
1
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]I18
0.13
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
0.13
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
11/19/19
0.13
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
,> GOLDER

Page 14 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMBICkIll,"d
Ati,,
C&D M,,it.,i,g
W'11,
Adw. C&D
M-it.lmg W.1l..&
MNA P.ff--e
M-it.mg
W.11.
Cl-d MSW M..Rri.g
We 1. &
MNA Peff--e M-it.dmg
Well.
Cl ... d MSW
Offsit,
Dlbromome0iane
ug/L
03I05/90
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
-
-
--
-
-
--
--
ND
--
NC 2L MC= 70 ug/L
ug,
OM1191
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
--
--
--
-
-
--
--
ND
--
ug/L
03/10/92
-
-
-
-
-
--
ug/L
04/20/95
-
-
-
-
-
--
ug/L
06/2] 95
-
-
-
-
-
--
ND
ND
ND
--
--
ND
ND
--
ug/L
09/22I95
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
- ---
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
11
--
ND
ND
--
uWL
WO 97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W3 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
OW 4100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ ] 00
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
NO
NO
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
Wo 103
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/13103
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10125I04
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
-
-
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
WO /05
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/04105
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uWL
W2 /06
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/09106
--
--
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/24107
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10130107
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23108
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06108
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15109
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26110
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1019/10
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18/11
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
1010/11
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/1]112
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09112
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15113
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30113
-
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16114
--
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
1015114
0.27
--
10
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.27
--
10
ND
ND
-
-
-
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
--
ND
ND
ug/L
1010]115
0.27
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/i6
0.27
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.27
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.27
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12117
0.27
--
10
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
0.27
--
10
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/2]/18
0.27
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02119
0.27
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19/19
0.27
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Methylene chlande
ug/L
03/05/90
--
--
--
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
--
-
--
--
--
--
--
ND
--
NC2L=5 ug/L
ug/L
OM1191
-
-
-
_
_
_
_
_
_
_
_
_
_
_
_
_ _ ..
..
..
..
-
..
..
..
..
..
ND
--
EPA MCL=5uglL
ug/L
ON10192
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
--
-
--
--
--
--
--
ND
--
ug/L
04/20/95
-
-
-
_
_
-
-
_
_
_
_
_
_
_
_
_ _ ..
..
..
-
-
..
..
..
..
..
ND
--
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04/10/01
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04/18/02
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04/09/03
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04/26104
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04/04105
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04/28/06
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u9/L
04/24107
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u9/L
10/30107
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u9/L
04/23/08
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0.67 J
u9/L
10/06/08
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04/13/09
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10/15109
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04/26/10
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10/19/10
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04/18/11
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10/10/11
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10/09/12
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04/15/13
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09/30/13
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04/16/14
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04/15/15
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11/30/16
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04/11/17
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12/12/17
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omo/18
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04/02/19
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,> GOLDER

Page 15 d 20
Project No. 19127453
TABLE 4
Summary of Hl,terical Groundwater Monitoring Result, (D-eted Conetlt... t,)
Water Quality Monitering Report, 2019 Second Seml-Annual Sampling Event
Moor. County Landfill, NC Solld We- Permit No. 83-01
Aberdeen, Moore County, North Carolina
r'r..1.tl,1...d .-it.rimg' j
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u9/L
10/30/07
-
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100
ND
ND
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04/23I08
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100
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ND
ND
ND
ND
-
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1010(il08
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17 J
14 J
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04/13109
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10/15109
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04/ 10
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10/ 910
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04/18/11
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-
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10/ 011
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04/1]/12
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10/09/12
-
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04/15113
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09KI 113
-
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100
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-
-
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ND
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2.6 J
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ug/L
04/1 N14
--
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100
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ND
ND
ND
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-
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ND
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2.4 J
1.3 J
13 J
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101 &14
1.3
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04/15115
1.3
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1010]115
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04/11116
1.3
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100
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-
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ND
ND
ND
ND
-
-
-
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ND - --
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ND
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28 J
1.0 J
4.2 J
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--
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11KI 116
1.3
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ND
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-
-
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1.4 J
ND
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6.4 J
--
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ND
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ug/L
04/11/17
1.3
--
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-
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-
-
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ND
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ND
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24 J
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12/12117
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-
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ND
ND
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ug/L
O6/20/18
1.3
-
100
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-
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ND
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-
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-
-
ND
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ND
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ND
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--
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11/2]/18
1.3
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-
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ND
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ND
ND
ND
ND
ND
--
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ND
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ug/L
04/02119
1.3
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ND
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-
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21
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11/19/19
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5.7
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10/30/07
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ND
ND
ND
ND
ND
ND
ND
--
ND
ND
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2L IMAC=100 ug/L
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04/23108
-
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100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
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ug/L
10/06/08
-
-
100
ND
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-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
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ND
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0.73 J
ND
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ug/L
04/13/09
-
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100
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ND
ND
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-
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ND
ND
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ND
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--
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ug/L
10/15/09
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100
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04/26/10
-
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100
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-
-
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ND
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10/19/10
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100
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ND
ND
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-
-
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ND
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ND
ND
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ND
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ND
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--
ND
ND
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ug/L
04/18/11
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
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ug/L
10/10/11
-
-
100
ND
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-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
--
ND
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--
ND
ND
ND
ug/L
04/17112
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09112
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15113
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
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--
ND
ND
ND
ug/L
09/30/13
-
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16114
--
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/15114
1.1
-
100
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
1.1
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
1.1
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/i6
1.1
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
1.1
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/1]
1.1
--
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12/17
1.1
-
100
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
1.1
-
100
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/27/18
1.1
5
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02/19
1.1
5
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
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11/19/19
1.1
5
-
ND
-
ND
ND
ND
-
ND
-
ND
-
-
ND
- ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Naphthalene
ugtL
03/05/90
-
-
-
ND
NC2L=6 ug/L
ug/L
03/21/91
--
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
--
--
--
--
--
--
--
ND
--
ug/L
03/10/92
.-
-
-
_
_
_
-
_
_
_
_
_
_
_
_
_ _ ..
..
..
..
..
..
..
..
..
..
ND
--
ug/L
04/20/95
.-
-
-
_
_
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-
_
_
_
_
_
_
_
_
_ _ ..
..
..
..
..
..
..
..
..
..
ND
--
U61
06127/95
ND
ND
ND
ND
ND
ND
ND--
ND
ND
2.5
ND
--
ND
ND
--
ug/L
09/22/95
--
--
--
ND
ND
ND
ND
-
ND
ND
-
ND
ND
ND
- - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
U61
OM8196
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29196
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
UGV
MIOW97
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29197
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
Uw
M/30198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/14198
--
--
--
ND
ND
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
Uw
M�7199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/21/99
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
Uw
ON14100
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10117100
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/10/01
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10111101
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/18/02
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
-
ND
ND
ND
ND
--
ND
ND
--
uw
10108102
ND
ND
ND
ND
ND
ND
ND
ND
N D
ND
ND
N D
ND
ND
ug/L
04/09/03
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10113103
ND
ND
ND
ND
ND
ND
ND
ND ---
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/26104
--
--
--
ND
ND
--
ND
ND
ND
-
ND
-
-
-
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
1 M51M
ND
ND
ND
ND
ND
ND
ND ---
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/04105
--
--
--
ND
ND
--
ND
ND
ND
-
ND
-
-
-
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10104105
ND
ND
ND
ND
ND
_
_ --
_
_
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/28106
--
--
--
ug/L
10/09106
-
-
-
-
-
--
ug/L
04/24107
--
ND
ND
--
--
--
--
ND
ug/L
11/2]118
0.11
1
-
ND
-
-
-
-
-
-
-
ND
-
-
ND
- - --
--
--
--
--
--
--
--
--
--
--
ND
ug/L
04/02119
0.11
1
-
ND
-
-
-
-
-
-
-
ND
-
-
0.40 J
- - --
--
--
--
--
--
--
--
--
--
--
ND
ug/L
11/19119
0.11
1
-
ND
-
--
--
-
--
-
-
ND
-
-
ND
- - --
--
--
--
--
--
--
--
--
--
--
ND
C> GOLDER

Page 16 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Result, (Det.ded Con.tlt... t,)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
Ati,,
•
C&D M,,it.ri,g
W,11,
•
.•
Ati- C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
M-it.rimg W.11.
Cl-d MSW M..Rri.g
We 1. &
MNA Peff--e
M-it.,mg Well.
Cl ... d MSW
Offsit'
Styrene
ug/L
O6/2195
-
-
-
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
--
ND
ND
--
EPA MCL=100 ug/L
ug/L
0MW96
--
--
--
ND
-
-
-
-
-
-
-
-
-
-
-
-
- --
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
10129196
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
12
--
ND
ND
--
ug/L
04/08/97
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
10129197
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/30/98
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
10114198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/21/99
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
10121199
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
OW14100
--
--
--
ND
ND
-
ND
ND
-
ND
ND
-
ND
ND
ND
-
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
Wigloo
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/17/00
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10111101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
WIW02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/0903
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1 03
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/2604
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/2 04
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/0405
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0405
-
-
-
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/2 O6
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
---
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0906
-
-
-
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
---
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/2407
-
-
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
---
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/30/07
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/23108
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/06108
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/13/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/15/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/26/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/19/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/18111
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
10/10/11
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
ug/L
04/17112
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/09112
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15/13
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
09/30/13
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/16114
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
dry
--
ND
ND
ND
ug/L
10/15114
0.11
-
1
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
04/15115
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
ug/L
10/07/15
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11116
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
11/30/16
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
04/11/17
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
12/12/17
0.11
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ug/L
O6/20/18
0.11
-
1
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ND
ug/L
11/27/18
0.11
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u91
04/02119
0.11
1
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
u L
11/19119
0.11
1
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Tetrechloroethene
uWL
03/05/90
--
--
-
_
_
_
_
_
_
_
_
_
_
_
_
_
_ ..
..
..
..
..
..
..
..
..
..
ND
--
NC2L=0.]ug/L
uWL
03/21/91
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
EPA MCL=5 ug/L
uWL
03/10/92
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
ug/L
04/20/95
ND--
--
--
ND
ND
--
ug/L
09/22I95
-
-
-
ND
_
._
_
_
_
ND
_
_
_
-
_
_
_ --
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
-
12
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
6
-
ND
ND
-
-
ND
-
ND
]
ND
-
- --
--
-
-
ND
ND
ND
8
..
ND
ND
--
UW
W08/97
ND
ND
ND
ND
ND
ND
ND
ND
N D
ND
ND
8
ND
ND
uw
10/29197
--
--
--
ND
15
--
ND
ND
-
-
ND
-
ND
15
ND
-
- --
--
--
--
9.2
ND
ND
9.1
--
ND
ND
--
ND
ND
uw
10/14/98
--
--
--
ND
12.]
--
ND
ND
-
-
ND
-
ND
8.7
ND
-
- --
--
--
--
ND
ND
ND
5
--
ND
ND
--
ND
ND
uw
10/21/99
--
--
--
ND
8.6
--
ND
ND
-
-
ND
-
ND
6.5
ND
-
- --
--
--
--
ND
ND
ND
7.6
--
ND
ND
--
UW
ON14100
ND
ND
ND
ND
ND
ND
6
ND--
ND
ND
ND
ND
ND
ND
3
--
ND
ND
--
ug/L
04/19/00
--
--
--
ND
10
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
-
-
ND
ND
ND
ND
ND
ND
ND
ND
uw
04/10/01
--
--
--
ND
8.5
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
8.1
ND
ND
ND
--
ND
ND
--
UW
10111101
ND
8A
ND
ND
ND
ND
ND
ND
uw
04/18/02
--
--
--
ND
7.3
--
ND
ND
-
-
ND
-
ND
5.9
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ND
ND
uw
04/09/03
--
--
--
ND
5.3
--
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ND
ND
uw
04/26I04
--
--
--
ND
5.2
--
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ND
ND
uw
04/04/05
--
--
--
ND
ND
--
ND
ND
ND
-
ND
-
-
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10104105
ND
ND
ND
ND
ND
ND
-
ND
ND
ND
ND
---
ND
ND
ND
ND
--
ND
ND
--
uw
04/28/06
--
--
--
ND
ND
--
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
uw
04/24107
--
--
--
ND
4 J
--
ND
ND
3
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ND
-
-
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- --
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ND
ND
ND
ND
ND
ND
--
ND
ND
--
uw
10/30107
-
-
1
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3.1 J
-
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0.43 J
0.49 J
0.35 J
ND
-
-
-
0.52 J
0.71
J - --
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ND
ND
ND
ND
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0.38 J
--
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uw
04/23/08
-
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2.8
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ND
ND
-
-
-
0.40 J
0.54
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ND
ND
ND
ND
ND
ND
--
ND
ND
ND
uw
10/06/08
-
-
1
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2.0
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ND
ND
ND
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-
-
-
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0.49
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ND
ND
ND
ND
ND
ND
0.49 J
--
ND
ND
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uw
04/13/09
-
-
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2.9
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0.48 J
0.84 J
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ND
ND
ND
ND
ND
0.49 J
--
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ND
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uw
10/15/09
-
-
1
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2.7
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0.44 J
ND
ND
ND
-
-
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0.53
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ND
ND
ND
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0.50 J
--
ND
ND
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4
04/26/10
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-
1
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2.9
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0.52 J
0.46 J
ND
ND
-
-
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ND
- --
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ND
ND
ND
ND
ND
DA7 J
--
ND
ND
ND
4
10/19/10
-
-
1
ND
2.7
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ND
0.41 J
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
0.52 J
--
ND
ND
ND
4
04/18/11
-
-
1
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1.8
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ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
--
ND
ND
ND
ND
--
ND
Dry
ND
ND
ND
ug/L
04/17112
-
--
1
ND
2.0
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ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
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ND
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ND
ug/L
10/09112
--
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1
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2.5
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ND
ND
ND
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ND
ND
ND
ND
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--
ND
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ug/L
04/15113
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1
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ND
ND
ND
ND
-
-
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ND
ND
- --
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ND
ND
ND
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--
ND
ND
ND
ug/L
09/30113
--
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1
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1.5
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ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
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--
ND
ND
ND
ug/L
04/16114
--
--
1
ND
2.2
-
ND
ND
0.57 J
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
4
10/15114
0.17
--
1
Dry
1.8
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ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
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ND
ND
ND
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--
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ug/L
04/15I15
0.17
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1.]
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ND
ND
-
-
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ND
ND
- --
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ND
ND
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4
10/07115
0.17
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- --
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ND
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4
04/11116
0.17
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11/30116
0.17
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04/11117
0.17
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12/1211]
0.17
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11/27118
0.17
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04/02119
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ND
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-
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11,19/19
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C> GOLDER

Page 17 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.)
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
th,d J"WIMB,ck,r
... d
•
Ati,,
•
C&D M,,it.ri,g
W,11,
•
.•
Adw. C&D
M-it.rmg W.11.
& MNA P.ff.r.-e
M-it.rimg W.11.
Cl-d MSW M..Rri.g
We 1.
& MNA Peff--e
M-it.,mg Well.
Cl ... d MSW
�Sit'
Toluene
uw
03I05/90
--
--
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
-
-
-
-
-
--
--
ND
--
NC2L=600 ug/L
ug/L
OM1191
-
-
-
_
_
-
-
-
_
_
-
-
_
_
_
- _ ..
..
..
..
..
-
-
-
..
..
ND
--
EPA MCL=1000 ug/L
uWL
03/10/92
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- - --
--
--
--
--
--
--
--
--
--
ND
--
ug/L
04/20/95
ND--
ug/L
06/2] 95
-
-
-
-
-
--
ND
ND
ND
--
--
ND
ND
--
ug/L
09/22I95
-
-
-
ND
_
-
_
_
_
ND
_
_
_
_
_
- _ --
ND
ND
ND
ND
ND
ND
--
--
ND
ND
--
--
ND
ND
--
ND
ND
ND
--
--
ND
ND
--
ug/L
10/29/96
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ND
-
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/29/97
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/30/98
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
15
--
ND
ND
--
.WL
1011 198
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/2]199
--
--
--
ND
ND
--
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/2199
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
03/1400
-
-
-
ND
ND
-
ND
ND
-
2
ND
-
ND
ND
ND
- ---
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1900
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1700
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/1001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/ 1101
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
Wl 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/0 02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/0903
-
-
-
ND
ND
-
ND
ND
-
-
NO
-
ND
ND
NO
- - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/1 03
-
-
-
ND
ND
-
ND
ND
ND
-
NO
-
-
-
NO
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
--
ND
ND
ND
ND
--
ND
ND
--
u9/L
10/25104
--
--
--
ND
ND
-
ND
ND
-
-
ND
-
-
-
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
.WL
M/0 105
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ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
--
ND
ND
--
u9/L
10/04105
--
--
--
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
ND
ND - --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
.WL
W2 /06
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ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
u9/L
10/09/06
--
--
--
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
.WL
W2 107
ND
ND
ND
ND
ND
ND
ND
ND
ND--
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
--
u9/L
10/30/07
--
--
1
ND
ND
-
ND
ND
ND
ND
0.52 J
-
-
-
0.31 J
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
04/23108
-
-
1
ND
ND
-
ND
0.44
J ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
1010 /08
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
04/13/09
-
-
1
ND
ND
-
ND
ND
ND
ND
0.56 J
-
-
-
0.53 J
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
10/15/09
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
04/26/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.47 J
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
10/19/10
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
04/18/11
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
u9/L
10/10111
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND - --
ND
ND
ND
ND
--
ND
Dry
--
ND
ND
ND
u9/L
04/17/12
-
-
1
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.4] J
ND - --
ND
ND
ND
ND
ND
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04/19/00
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04/18/02
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04/24/07
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04/18/11
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09/30/13
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10/07/15
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11/30/16
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12/12/17
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11/27/18
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04/02119
0.12
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11/19119
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C> GOLDER

Page 18 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
Trichloro hens
u9/L
03/OS/90
-
-
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--
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--
--
--
--
--
--
--
--
ND
--
NC2L=3 uc/L
uWL
OM1191
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
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--
--
-
-
--
-
-
--
--
ND
--
EPA MCL = 5 a9/L
ug/L
03/10192
--
--
--
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--
--
--
--
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04/20/95
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ug/L
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3.6
ND
ND
--
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ND
ND
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ug/L
09/2 95
-
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-
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-
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ND
ND
ND
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--
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ND
ND
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ug/L
03/28196
--
--
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--
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-
--
-
-
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-
-
-
-
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ND
--
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ND
ND
--
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ND
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10/2996
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ND
ND
-
-
ND
-
ND
ND
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-
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--
--
--
ND
ND
ND
5
--
ND
ND
--
ug/L
04/08197
--
--
--
ND
9
--
ND
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--
-
ND
-
ND
6
ND
-
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--
--
--
ND
ND
ND
ND
--
ND
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ug/L
10/29/97
-
-
-
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8.9
-
ND
ND
-
-
ND
-
ND
6.5
ND
-
- --
--
--
--
ND
ND
ND
5.9
--
ND
ND
--
ug/L
04/30198
--
--
--
ND
9.8
--
ND
ND
--
-
ND
-
ND
6A
ND
-
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--
--
--
ND
ND
ND
5.4
--
ND
ND
--
ug/L
10/1498
-
-
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8A
ND
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-
-
ND
-
ND
ND
ND
-
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--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/27199
--
--
--
ND
7.2
--
ND
ND
--
-
ND
-
ND
ND
ND
-
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--
--
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ND
ND
ND
ND
--
ND
ND
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10/2 99
-
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6.2
-
ND
ND
-
-
ND
-
ND
ND
ND
-
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--
--
--
ND
ND
ND
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--
ND
ND
--
ug/L
03/14100
--
--
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ND
6
--
ND
ND
--
ND
ND
-
ND
ND
ND
-
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ND
ND
ND
ND
ND
ND
3
--
ND
ND
--
ug/L
04/ 900
-
-
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ND
7.6
-
ND
ND
-
-
ND
-
ND
ND
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-
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--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/17100
--
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ND
5.1
--
ND
ND
--
-
ND
-
ND
ND
ND
-
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--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/ 001
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
5.2
ND
ND
ND
--
ND
ND
--
ug/L
10/11101
--
--
--
ND
5.6
--
ND
ND
--
-
ND
-
ND
ND
ND
-
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--
--
--
ND
ND
ND
ND
--
ND
ND
--
ZWIW02
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
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--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
10/08102
--
--
--
ND
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09/22/95
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04/26/04
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10/09/06
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10/30/07
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04/02/19
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,> GOLDER

Page 19 d 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Det.ded Con.tlt... t.
Water Quality Monitering Report, 2019 Second S.ml-Annual Sampling Event
Moor. County Landfill, NC Solld W.- Permit No. 83-01
Aberdeen, Moore County, North Carolina
Vinyl chloride
ug/L
03I05/90
-
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--
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- --
--
--
--
--
--
--
--
--
--
ND
--
NC2L=0.03 ug/L
uwL
0M1191
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
- --
--
--
--
--
--
-
-
--
--
ND
--
EPA MCL = 2 ugIL
ug/L
03/10192
--
--
--
--
-
--
--
--
--
-
-
--
-
-
-
-
- --
--
--
--
--
--
--
--
--
--
ND
--
udL
04/20/95
-
-
-
-
-
--
ug/L
O6/27195
--
--
--
-
-
--
-
-
--
-
-
--
-
-
--
-
- --
--
--
--
5.3
9.4
15.9
--
--
40.3
ND
--
udL
09/2 95
-
-
-
ND
-
-
-
-
-
ND
-
-
-
-
-
-
---
ND
ND
ND
ND
ND
20
--
--
45
ND
--
ug/L
03/28196
--
--
--
ND
-
--
-
-
--
-
-
-
-
-
--
-
- --
ND
13
--
ND
ND
ND
--
--
12
ND
--
udL
10/2996
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/08197
--
--
--
ND
ND
-
ND
ND
--
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
udL
10/2997
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/30198
--
--
--
ND
ND
-
ND
ND
--
-
ND
-
ND
ND
ND
-
- --
--
--
--
ND
10
ND
ND
--
ND
ND
--
udL
10/1498
-
-
-
ND
ND
-
ND
ND
-
-
ND
13
ND
35
-
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
04/27199
--
--
--
ND
ND
-
ND
ND
--
-
ND
-
ND
ND
58
-
- --
--
--
--
18
ND
ND
ND
--
ND
ND
--
udL
1MI199
-
-
-
ND
ND
-
ND
ND
-
-
ND
-
ND
ND
28
-
- --
--
--
--
21
ND
ND
17
--
ND
ND
--
ug/L
03/14100
--
--
--
ND
8
-
3
ND
--
ND
7
-
ND
8
16
-
- --
ND
B
ND
15
5
ND
9
--
4
ND
--
udL
04/ 900
-
-
-
ND
16
-
ND
ND
-
-
19
-
ND
ND
ND
-
- --
--
--
--
25
21
ND
11
--
ND
ND
--
ug/L
10/17100
--
--
--
ND
ND
-
ND
ND
--
--
18
-
14
ND
40
-
- --
--
--
--
14
ND
13
ND
--
28
ND
--
udL
04/ 001
-
-
-
ND
13
-
ND
ND
-
-
21
13
14
35
-
- --
--
--
--
25
16
11
16
--
ND
ND
--
ug/L
10/11I01
--
--
--
ND
ND
--
ND
ND
--
--
26
-
14
ND
12
-
- --
--
--
--
15
12
ND
ND
--
28
ND
--
udL
WIW02
-
-
-
ND
ND
-
ND
ND
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25.9
-
ND
ND
ND
-
- --
--
--
--
13
10.8
ND
ND
--
17.7
ND
--
udL
04/09103
-
ND
ND
-
ND
ND
-
26.1
-
ND
ND
16.5
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
ug/L
1D/131D3
--
--
--
ND
ND
--
ND
ND
ND
--
15.8
--
-
-
12.5
ND
- --
--
--
--
ND
ND
11A
ND
--
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ND
--
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04/2604
-
-
-
ND
ND
-
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ND
ND
-
9.
-
-
-
5.9
ND
- --
--
--
--
ND
ND
ND
ND
--
19A
ND
--
--
ND
ND
ND
ND
--
13.3
ND
--
udL
04/04/05
-
ND
ND
-
ND
ND
ND
-
ND
-
ND
ND
- --
--
--
--
ND
ND
ND
ND
--
ND
ND
--
uw
10/04/05
--
--
--
ND
ND
-
ND
ND
ND
-
11.9
--
ND
ND
ND
ND
- --
--
--
--
11.7
ND
ND
ND
--
12.8
ND
--
--
ND
ND
ND
14.2
ND
ND
ND
--
ND
ND
--
uw
10/09106
--
--
--
ND
ND
-
ND
ND
ND
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18.9
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ND
- --
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ND
ND
ND
ND
ND
ND
--
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--
--
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ND
ND
ND
ND
--
ND
--
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ND
--
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10/30107
--
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1
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2.6
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0.43 J
0.30 J
8.3
-
-
-
2.8
ND
- --
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2.7
ND
3.6
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1.2
ND
--
4.2
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ND
uw
04/23I08
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1.6
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9.1
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1.4
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3.0
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--
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ND
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10/06108
--
--
1
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3.3
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0.59 J
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11
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0.18
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1.2
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3.4 J
2.1
1.9
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ND
ND
ND
uw
04/13I09
-
-
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0.59 J
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ND
uw
10/l5I09
--
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2.7
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0.62 J
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-
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1.4
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0.92 J
2.1
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4.0
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1.1
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04Mlo
-
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0.84 J
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0.81 J
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uw
lo/19110--
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04/18I11
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5.7
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0.91 J
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0.78 J
0.90 J
0.71 J
2.2
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1.0
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uw
10/10111
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2.2
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ND
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5.0
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3.1
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0.86 J
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3.7
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0.79 J
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10/09
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04/15I13
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6.2
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0.61 J
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0.41 J
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1.6
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2.3
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3.1
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04/1fi114
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0.43 J
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ND
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uw
10/15114
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1
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0.77 J
ND
0.42 J
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0.62 J
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2.2
1.5
0.55 J
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0.57 J
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.w
04/15I15
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0.51 J
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04/11/16
0.32
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2.5
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0.61 J
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0.71 J
0.42 J
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0.48 J
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11/30116
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0.40 J
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0.62 J
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1.3
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0.48 J
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0.64 J
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uw
04/11/17
0.32
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0.73 J
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1.1
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3.9
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0.48 J
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0.67 J
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11/27118
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0.55 J
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0.50 J
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04/02I19
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0.97 J
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ND
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2.4
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11/19119
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ND
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03/05/90
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03/21191
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03/10/92
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09/22195
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03/28196
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10/29196
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10/29197
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-
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10.2
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10/14198
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10/21199
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04/19100
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04/10101
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uw
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uw
04/28I06
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10/30/07
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5
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0.41 J
0.98 J
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10/15I09
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10/19/10
-
-
5
ND
ND
-
ND
ND
ND
ND
D.47 J
-
-
-
0.48 J
ND
- --
ND
ND
ND
ND
ND
0.41 J
ND
--
0.4] J
ND
ND
U./L
D4/18111
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
uw
10/10/ll
-
-
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
U./L
04/17112
-
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.56 J
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
uw L
10/09112
-
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
0.45 J
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
udL
04/15/13
--
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
uw L
D9130113
--
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
udL
04/16/14
--
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
uw L
1DI15114
0.45
--
5
Dry
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
0.60 J
ND
ND
u15/15
dL
04/
0.45
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
Dry
--
ND
ND
ND
uw L
10/07115
0.45
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
0.93 J
ND
ND
udL
04/11/16
0.45
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
uw L
11/30116
0.45
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
0.81 J
ND
ND
udL
04/11/17
0.45
--
5
ND
ND
-
ND
ND
ND
ND
ND
-
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
--
1.3 B
ND
1.3 J
uw L
1M2117
0.45
--
5
ND
ND
ND
ND
ND
ND
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
ND
1.2 J
ND
ND
udL
06/20/18
0.45
--
5
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
0.99 J
--
ND
uNL
11/27118
0.45
3
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
- --
ND
ND
ND
ND
ND
ND
--
ND
ND
ND
ND
ug/L
04/02I19
0.45
3
-
ND
-
ND
ND
ND
ND
ND
-
ND
-
-
ND
ND
ND
ND
ND
ND
ND
0.45 J
--
ND
ND
ND
ND
ug/L
11/19119
0.45
3
ND
ND
ND
ND
ND
ND
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
2.2 J
ND
ND
,> GOLDER

Page 20 of 20
Project No. 19127453
TABLE 4
Summary of Historical Groundwater Monitoring Results (Detached Consult ... oi)
Water Quality Monitoring Report, 2019 Second Saml-Annual Sampling Event
Moor. County Landfill, NC Solid We- Permit No. 83-01
Aberdeen, Moore County, North Carolina
Notes:
1.1 uNL = Micrograms par liter
2.) ND = Not detected at the stated raportina limit
3.1 NM = Not measured
4.1 J = Estimated concentration reported below Solid Waste Section Limit
5.) --= No data available
8.) Blanks = Field, trip, and method blanks
].I Reanalysis = Reanalysis result in parenthesis nett to the original result (e.g., reanalysis was performed for arsenic in January 2017)
7.) Dissolved= Dissolved sample in brackets fe.o. a dissolved sample was anal d for MW-9 for the Febuary 2017 verification event!
9.)Bold= Concentration above the current NC 2L Grcundwatan Standard a NC 2L IMAC Groundwater Standard
10.1 Shedd and Bold = Concentration above the current NC 2L Groundwater Standard or NC 2L IMAC Groundwater Standard and EPA MCL
11.) EPA MCL = US Environmental Protection Agency Madmum Contaminant Laval
12.1 SW S GSP = Sdid Win Section Groundwater Protection Standard
13.) SW S Reporting Limit = NCPQL or lab-specitic reporting limit prior to October 2007 and NCSW SL starliiyl in October 2007 and ending June 1, 2018
14.) - = EPA MCL is an action level
15.1"= EPA MCL is a secondary standard
16.) Historical data pda to 10/30/07 provided by HDR Enaineaninq of the Carolinas. Inc.
17.) Samples collected uslnq low -flow hume and sample techniques.
18.) The followino dilutions wane noted for m the November 2019 samplinq event: Anlimonv and Thallium by 2X for -4 MW. MW 5. MW-11 SR. MW-11 DR. MW-13D. MW-13S. MW-14. MW-17S. MW-17D. 8 Field Blank: Alkalinity by 2X for MW MW-2. MW-14. MW-6. 8 -11 SR: SX in MW-11 DR: 1OX in MW-9. Mehane t1OX in MW-8: MMW W-9. -14. 8 MW-15SR: 5X in MW-7: Sulfate 2X in MW-17S: Nitrate 5X in MW 4 Chloride 2X in MW-9
19.) PQL = Practical ouantltatlon limit - lab specific limit
20.) The Blake Wall not sampled in June 2018 as the paver was out at the residence and no sample could Ira p tained.
,> GOLDER

February 2020 Page 1 of 3 Project No. 19127453
TABLE 5
Summary of Historical Groundwater Field Parameters
Water Quality Monitoring Report, 2019 Second Semi -Annual
Sampling Event
Moore
County Landfill, NC Solid Waste Permit
No. 63-01
ive
:r Monitoring
Wells & MNA
Aberdeen, Moore County, North Carolina
Performance Monitoring Wells
Closed MSW
Offiste Private
Parameter
pH (field)
Reporting
I"
Units
S.U.
04/28/06
r
4.70
Active
r'
--
r Monitoring
--
Wells
r
5.40
r
4.70
L
5.10
6.30
for the Closed
--
MSW Landfill
5.90
4.70
5.00
6.10
Closed
5.00
MSW Monitoring
4.90
Wells & MNA Performance
5.90
Monitoring
5.90
Wells
6.40
5.50
-
Monito '
Well mg
6.10
Well
5.00
Blanks
-
S.U.
10/09/06
4.70
--
6.10
5.30
4.90
5.20
6.40
--
6.00
4.60
5.10
6.10
4.90
4.70
5.80
5.90
6.50
5.60
-
6.10
4.50
-
S.U.
04/24/07
5.10
--
6.10
5.10
4.70
4.60
6.20
--
5.80
4.60
5.30
6.00
4.80
5.00
5.60
6.00
6.30
5.60
-
6.00
5.60
-
S.U.
11/01/07
4.73
--
5.87
4.92
4.63
5.04
6.40
--
5.96
5.28
4.59
6.08
4.65
4.53
5.82
5.89
6.43
5.53
-
5.99
5.03
-
S.U.
04/23/08
5.85
--
8.16
6.55
4.98
6.07
7.78
--
8.00
6.59
5.55
7.20
5.89
5.63
7.19
7.62
7.50
7.46
-
7.62
5.46
-
S.U.
10/08/08
4.53
--
7.22
5.13
4.69
4.82
6.16
--
5.96
5.56
4.52
5.83
3.66
4.00
5.65
6.00
6.36
5.27
-
5.75
4.27
-
S.U.
04/13/09
5.31
--
5.62
5.10
4.13
5.05
6.23
--
5.92
6.02
4.76
6.08
4.65
4.52
5.70
5.70
6.38
5.42
-
5.55
3.71
-
S.U.
10/17/09
4.90
--
5.99
5.11
5.08
5.46
6.39
--
6.06
6.28
5.69
6.17
4.61
4.46
6.06
5.78
6.49
5.66
-
6.16
7.28
-
S.U.
04/26/10
5.10
--
5.41
4.54
4.99
4.42
6.05
--
5.68
5.65
4.53
5.74
4.28
4.20
5.62
6.02
6.23
5.48
-
5.31
4.33
-
S.U.
10/19/10
4.99
--
6.03
5.05
5.38
5.01
6.35
--
6.01
5.88
4.66
6.03
4.41
4.32
5.83
5.93
6.39
5.56
-
5.92
4.71
-
S.U.
04/18/11
4.63
--
5.62
5.00
5.18
4.72
6.13
--
5.62
5.87
4.39
5.59
4.17
4.11
5.36
5.68
6.04
5.41
-
5.55
5.13
-
S.U.
10/10/11
6.08
--
6.21
5.25
7.13
6.79
7.15
--
6.24
7.91
6.12
7.41
6.59
4.96
6.23
-
6.38
Dry
-
6.24
5.78
-
S.U.
04/17/12
4.69
--
5.38
4.68
4.62
3.91
5.86
--
5.74
5.92
5.33
5.56
3.88
3.46
5.76
5.80
6.38
Dry
-
5.57
5.76
-
S.U.
10/09/12
4.74
--
5.70
4.67
5.32
5.22
6.07
--
6.04
5.73
5.58
6.19
4.85
4.98
6.14
5.57
6.49
Dry
-
6.06
5.17
-
S.U.
04/15/13
5.28
--
5.77
4.70
5.52
4.71
6.67
--
6.04
6.07
5.19
6.26
4.02
4.28
5.95
6.12
6.57
Dry
-
6.04
5.31
-
S.U.
09/30/13
5.33
--
6.24
5.67
5.73
5.31
6.14
--
6.16
6.13
4.83
6.22
4.74
4.72
6.14
6.23
6.48
Dry
-
6.02
4.97
-
S.U.
04/16/14
6.19
--
6.72
6.07
6.50
6.16
6.70
--
6.47
6.61
5.28
6.46
5.14
5.00
6.41
6.64
6.77
Dry
-
6.29
6.23
-
S.U.
10/15/14
5.85
--
6.65
5.73
6.66
6.12
7.06
--
6.58
7.13
5.63
6.59
5.30
Dry
6.55
6.62
7.07
Dry
-
6.73
5.60
-
S.U.
04/15/15
5.56
--
6.74
5.93
6.33
5.93
5.86
--
6.48
6.57
4.61
6.09
4.40
3.01
6.33
6.44
6.97
Dry
-
6.36
5.54
-
S.U.
10/07/15
4.44
--
5.52
4.12
5.94
4.70
5.60
--
4.52
4.80
4.38
5.29
3.51
3.59
6.07
4.11
6.32
4.37
-
5.32
6.46
-
S.U.
04/11/16
4.87
--
5.07
4.87
5.58
4.94
6.42
--
6.29
6.32
4.81
5.78
3.82
3.75
5.66
5.70
6.41
5.61
-
5.27
4.74
-
S.U.
11/30/16
5.82
--
5.70
5.33
6.26
5.98
6.55
--
5.87
6.55
4.48
5.82
4.05
4.95
6.23
6.23
6.28
5.22
-
6.20
6.59
-
(Verification Event)
S.U.
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
6.38
-
-
-
-
-
S.U.
04/11/17
5.62
--
6.15
5.53
6.15
5.75
6.47
--
6.01
6.33
4.83
6.16
4.70
4.86
5.90
5.86
6.54
5.32
-
6.27
5.27
-
S.U.
12/12/17
5.55
--
6.12
4.99
5.99
6.00
6.35
--
6.13
6.29
5.32
6.13
4.28
4.48
6.07
5.45
6.40
5.70
-
6.19
4.45
-
S.U.
06/20/18
--
6.12
5.99
5.34
6.14
6.01
--
6.29
5.95
5.93
3.79
5.79
3.83
4.67
6.00
5.76
6.34
-
5.71
5.93
-
-
S.U.
11/27/18
--
5.77
6.2
5.67
6.15
5.97
--
6.44
6.38
5.9
4.12
5.59
3.82
4.61
6.45
6.46
5.51
-
6.11
5.51
4.57
-
S.U.
04/02/19
--
6.35
6.26
5.92
6.09
6.02
--
6.49
6.29
6.07
4.59
6.18
4.59
4.49
6.22
6.24
6.44
-
5.98
5.95
4.87
-
S.U.
11/19/19
--
6.19
6.26
5.31
--
6.29
--
6.32
3.6
--
5.33
6.00
4.39
4.33
6.16
6.01
6.50
-
5.95
6.32
5.30
-
erification Event
S.U.
01/08/20
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
-
-
5.76
-
-
-
Specific Conductance (field)
US/cm
04/28/06
56
--
--
60
77
27
1144
--
370
194
88
697
31
21
398
267
1788
241
-
728
28
-
(lab prior to Oct. 07)
us/cm
10/09/06
48
--
348
45
74
120
1206
--
447
147
103
635
34
20
398
328
1577
332
-
622
31
-
uS/cm
04/24/07
74
--
273
47
61
98
957
--
430
172
105
621
43
19
323
479
1362
271
-
594
27
-
uS/cm
11/01/07
66
--
338
47
91
132
1790
--
499
556
103
779
41
27
445
472
2170
300
-
723
26
-
uS/cm
04/23/08
90
--
330
48
120
82
1532
--
502
476
90
705
32
20
179
499
2163
264
-
403
26
-
uS/cm
10/08/08
105
--
999
215
684
90
1330
--
457
529
80
554
30
17
316
505
1773
245
-
328
17
-
uS/cm
04/13/09
178
--
258
76
148
123
1323
--
563
1160
92
791
38
13
373
369
2214
315
-
530
28
-
uS/cm
10/17/09
81
--
436
45
184
216
1981
--
584
1115
239
879
44
22
623
437
2270
403
-
854
21
-
uS/cm
04/26/10
139
--
331
56
177
148
1645
--
624
425
76
717
40
15
379
653
2184
286
-
551
21
-
uS/cm
10/19/10
97
--
387
74
207
129
1953
--
679
670
78
729
46
20
523
502
2199
384
-
682
22
-
uS/cm
04/18/11
98
--
410
81
235
142
1802
--
710
1406
89
802
49
21
478
452
2395
392
-
869
21
-
uS/cm
10/10/11
64
--
418
47
302
265
1452
--
671
898
281
855
53
24
699
-
2342
Dry
-
1041
24
-
uS/cm
04/17/12
69
--
357
49
123
118
791
--
620
869
202
807
39
21
619
383
2328
Dry
-
698
24
-
uS/cm
10/09/12
58
--
341
56
212
25
926
--
572
627
152
821
37
20
642
406
2092
Dry
-
698
20
-
uS/cm
04/15/13
52
--
313
60
206
75
963
--
532
930
71
694
34
18
645
405
2176
Dry
-
697
20
-
uS/cm
09/30/13
144
--
391
106
359
102
1014
--
673
1227
77
491
43
21
725
761
2303
Dry
-
550
22
-
uS/cm
04/16/14
227
--
422
158
684
99
1103
--
690
797
95
534
54
58
769
697
2292
Dry
-
671
60
-
uS/cm
10/15/14
105
--
420
91
810
148
1186
--
710
2260
120
580
88
Dry
920
640
2360
Dry
-
1150
45
-
uS/cm
04/15/15
191
--
263
107
846
398
728
--
494
2030
87
576
40
23
523
300
1835
Dry
-
455
17
-
uS/cm
10/07/15
180
--
361
82
633
118
1638
--
739
670
69
588
47
23
907
495
2381
373
-
1085
28
-
uS/cm
04/11/16
243
--
261
133
759
351
1804
--
625
1326
53
467
53
19
818
521
1803
280
-
564
36
-
uS/cm
11/30/16
263
--
321
102
811
314
2095
--
780
1274
53
454
46
19
917
516
2002
334
-
850
23
-
(Verification Event)
us/cm
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
2070
-
-
-
-
-
uS/cm
04/11/17
234
--
366
92
703
251
1925
--
806
1426
55
641
51
20
890
298
2217
312
-
1140
23
-
uS/cm
12/12/17
208
--
429
49
526
324
1443
--
779
807
160
756
64
20
891
460
2200
401
-
984
19
-
uS/cm
06/20/18
--
781
346
80.6
604
399
--
1233
820
449
61
784
54
23.0
840
590
220.2
-
268
989
-
-
uS/cm
11/27/18
--
786
287
131
529
451
--
1604
863
299
51.8
467
43.9
19.6
922
560
237
-
266
561
24.1
-
uS/cm
04/02/19
--
800
257
164
581
445
--
1978
729
380
51.4
453
52
445
888
976
2016
-
359
597
23.1
-
uS/cm
11/19/19
--
684
439
60.2
--
477
--
1421
958
--
155
548
69.4
22.7
626
366
1376
-
356
1064
24.8
-
(Verification Event)
uS/cm
01/08/20
--
--
--
--
--
I --
--
--
--
--
I --
--
--
-
-
-
-
-
264
-
I -
I -
G:�PROJEGlS\Howe C-ty-127453-Moore-Env Sentcee FY19-20%P100-WQM&Rep-g%DD GALGULNTIO W02-2-15 WQMR- 4 G O L D E R

February 2020 Page 2 of 3 Project No. 19127453
TABLE 5
Summary of Historical Groundwater Field Parameters
Water Quality Monitoring Report,
2019 Second Semi -Annual
Sampling
Event
Moore
County Landfill,
NC Solid Waste Permit
No. 63-01
ive
:r Monitoring
Wells & MNA
Aberdeen, Moore County, North Carolina
Performance Monitoring Wells
Closed MSW
'
Offiste Private
Parameter
Temperature (field)
Reporting
I"
Units
Celsius
04/28/06
r
18.00
Active
r'
--
r Monitoring
--
Wells
r
14.00
r
16.00
L
16.00
18.00
for the Closed
--
MSW Landfill
17.00
16.00
16.00
15.00
Closed
14.00
MSW Monitoring
16.00
Wells & MNA Performance
17.00
Monitoring
17.00
Wells
18.00
19.00
-
Monito
Well mg
13.00
Well
15.00
Blanks
-
(lab prior to Oct. 07)
Celsius
10/09/06
20.00
--
21.00
19.00
21.00
20.00
21.00
--
19.00
21.00
20.00
19.00
19.00
20.00
19.00
20.00
20.00
18.00
-
20.00
18.00
-
Celsius
04/24/07
17.00
--
16.00
16.00
17.00
19.00
19.00
--
16.00
19.00
18.00
17.00
17.00
17.00
17.00
18.00
20.00
18.00
-
16.00
19.00
-
Celsius
11/01/07
19.27
--
22.63
20.36
20.70
19.54
19.57
--
18.73
21.79
18.31
19.20
19.70
19.48
19.18
23.88
20.17
18.67
-
20.66
18.79
-
Celsius
04/23/08
17.56
--
16.92
17.97
19.26
16.55
16.83
--
16.55
18.28
14.84
15.59
14.80
14.83
16.52
16.28
17.82
17.33
-
16.61
18.49
-
Celsius
10/08/08
20.25
--
21.33
20.11
23.46
19.48
20.29
--
19.63
21.52
15.72
18.90
18.81
18.79
19.77
19.84
19.23
19.27
-
19.20
16.55
-
Celsius
04/13/09
16.64
--
14.52
15.95
17.69
15.24
16.47
--
16.11
17.99
14.94
14.91
14.86
14.55
15.82
16.55
18.62
17.43
-
14.09
16.35
-
Celsius
10/17/09
18.76
--
20.43
19.24
22.62
18.80
17.57
--
18.22
20.40
17.45
18.56
18.18
17.80
18.77
17.82
18.79
17.98
-
19.38
16.38
-
Celsius
04/26/10
18.63
--
16.30
17.85
20.91
15.66
16.52
--
16.85
18.44
14.40
15.51
14.85
16.23
17.05
18.24
18.45
17.25
-
16.05
16.89
-
Celsius
10/19/10
18.13
--
19.53
17.94
19.78
18.22
18.97
--
20.51
21.33
20.26
19.20
18.21
18.68
20.55
19.28
20.74
18.97
-
21.16
16.72
-
Celsius
04/18/11
18.09
--
15.69
17.59
22.01
16.10
17.19
--
17.16
19.67
17.39
15.45
15.45
15.48
16.95
19.00
21.49
19.89
-
15.23
17.15
-
Celsius
10/10/11
18.65
--
19.40
17.70
23.08
20.55
19.52
--
18.65
23.36
19.55
19.66
20.27
18.69
19.13
-
19.20
Dry
-
19.40
19.07
-
Celsius
04/17/12
18.06
--
17.34
19.68
21.08
16.25
18.15
--
17.29
20.47
17.55
16.39
16.11
16.60
18.01
16.55
19.29
Dry
-
16.42
19.85
-
Celsius
10/09/12
18.68
--
19.67
18.48
22.26
20.14
20.62
--
19.04
22.11
18.77
18.76
18.85
18.13
20.17
20.54
19.14
Dry
-
19.57
16.24
-
Celsius
04/15/13
18.63
--
15.72
16.97
19.35
14.23
18.08
--
16.64
19.06
15.28
14.26
14.04
14.23
16.92
17.86
19.24
Dry
-
16.11
17.65
-
Celsius
09/30/13
19.60
--
19.20
17.90
22.10
20.40
20.60
--
20.10
22.20
20.70
19.30
19.50
19.00
19.90
20.70
20.10
Dry
-
20.80
17.80
-
Celsius
04/16/14
17.30
--
14.60
16.40
17.10
14.00
15.80
--
14.80
14.80
13.20
13.70
13.60
12.90
15.20
16.80
17.10
Dry
-
13.80
15.50
-
Celsius
10/15/14
18.20
--
17.20
17.80
20.00
20.00
18.80
--
18.10
20.80
18.80
18.50
19.10
Dry
18.40
19.80
19.40
Dry
-
19.50
18.30
-
Celsius
04/15/15
16.40
--
13.65
15.35
16.12
13.52
14.29
--
13.47
15.42
13.71
13.38
13.45
13.69
14.21
14.37
16.53
Dry
-
12.66
15.45
-
Celsius
10/07/15
19.78
--
20.46
18.60
23.64
21.15
19.76
--
20.04
22.92
20.40
19.01
19.57
19.20
19.99
21.67
20.46
17.64
-
20.61
18.76
-
Celsius
04/11/16
16.88
--
14.93
16.25
20.15
13.71
14.90
--
14.61
15.73
14.06
14.90
15.70
15.60
16.20
16.30
16.65
17.80
-
13.72
14.90
-
Celsius
11/30/16
18.41
--
19.70
18.30
20.60
17.77
19.51
--
19.40
20.16
18.50
17.80
16.80
17.49
20.28
20.90
20.7
17.50
-
18.89
14.10
-
(Verification Event)
Celsius
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
17.80
-
-
-
-
-
Celsius
04/11/17
18.21
--
16.6
18.43
20.27
15.93
17.61
--
17.2
18.41
16.34
15.51
15.34
16.13
17.6
18.77
19.59
18.7
-
16.62
18.66
-
Celsius
12/12/17
17.9
--
18.5
17.8
16.9
14.2
15.7
--
18.0
18.9
16.2
16.0
15.1
15.0
18.2
13.9
18.0
17.8
-
17.5
9.2
-
Celsius
06/20/18
--
21.0
21.3
21.0
22.50
22.7
--
19.6
19.79
22.38
21.13
19.88
20.45
19.9
22.57
23.06
21.46
-
23.20
18.9
-
-
Celsius
11/27/18
--
17.1
18.7
16.9
19.1
15.5
--
19.0
18.9
20.4
15.9
16.3
15.5
16.2
18.8
18.6
19.5
-
17.60
15.7
16.5
-
Celsius
04/02/19
--
15.9
16.4
15.5
13.9
13.7
--
15.0
16.2
16.2
14.6
15.1
14.3
11.9
18.8
17.9
17.3
-
21.8
15.4
15.9
-
Celsius
11/19/19
--
18.9
18.6
18.2
--
17.4
--
19.7
19.0
--
18.1
17.5
16.8
17.2
19.4
18.6
19.4
-
18.9
18.5
15.1
-
erification Event
Celsius
01/08/20
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
-
-
17.4
-
-
-
Turbidity (field)
NTU
04/28/06
NM
--
NM
NM
NM
5.1
290
--
20
7.2
70
7.8
12
7.4
55
86
240
35
-
NM
NM
-
(lab prior to Oct. 07)
NTU
10/09/06
NM
--
NM
NM
NM
120
850
--
500
--
65
55
34
13
210
500
330
75
-
NM
NM
-
NTU
04/24/07
NM
--
NM
NM
NM
6
700
--
300
1.5
2.2
11
2.4
3.1
45
700
350
400
-
NM
NM
-
NTU
11/01/07
204
--
243
415
116
330
>1000
--
95.1
137
39.4
96.3
99.1
116
116
105
155
111
-
151
156
-
NTU
04/23/08
2.34
--
20.2
45.1
3.33
12.2
369
--
3.91
12.4
2.71
8.15
4.35
21.7
9.36
29.2
67.9
15.8
-
7.07
2.11
-
NTU
10/08/08
5.68
--
46.6
6.21
2.11
5.77
286
--
8.06
20.1
3.94
1.03
1.11
2.46
7.37
47.9
90.4
30.4
-
4.75
4.12
-
NTU
04/13/09
9.91
--
9.42
13.7
2.33
6.49
38.2
--
12.6
28.8
3.98
17.6
15.8
2.26
-
69.4
16.7
81.5
-
15.6
5.20
-
NTU
10/17/09
2.32
--
25.0
2.89
3.20
52.8
85.4
--
5.96
24.0
13.3
4.02
3.52
3.17
4.18
207
30.8
36.8
-
7.79
12.7
-
NTU
04/26/10
5.83
--
18.2
5.54
7.09
6.69
648
--
2.67
17.7
6.23
4.92
4.20
5.07
13.0
37.4
61.0
32.9
-
10.9
11.6
-
NTU
10/19/10
0.43
--
39.2
6.73
2.54
52.9
87.6
--
<100
8.94
10.3
36.1
2.44
17.8
12.8
71.3
23.0
8.36
-
<100
1.61
-
NTU
04/18/11
100
--
20.0
26.1
22.1
35.4
145
--
12.1
35.8
32.1
13.0
78.9
30.2
8.57
83.7
19.0
12.1
-
12.8
9.13
-
NTU
10/10/11
57.7
--
10.6
26.4
76.7
15.8
52.8
--
66
15.6
35.8
6.70
5.13
35.9
15.2
-
11.5
Dry
-
18.7
5.13
-
NTU
04/17/12
51.2
--
21.5
26.8
18.1
64.0
84.9
--
80.4
95.4
76.6
74.0
7.35
31.6
25.8
97.6
91.5
Dry
-
22.5
11.80
-
NTU
10/09/12
5.77
--
2.04
18.8
24.7
64.7
47.3
--
9.06
19.3
32.7
2.57
2.25
20.1
14.7
82.0
17.8
Dry
-
41.7
1.28
-
NTU
04/15/13
14.6
--
15.60
44.3
30.9
71.5
200
--
12.7
26.1
46.5
9.02
7.47
15.8
129
55.4
33.9
Dry
-
57.9
14.4
-
NTU
09/30/13
26.4
--
8.75
13.7
51.3
52.5
44.6
--
16.3
12.1
33.1
9.06
7.12
12.1
36.7
30.5
61.0
Dry
-
24.7
32.1
-
NTU
04/16/14
30.1
--
13.8
17.4
52.5
58.8
82.6
--
18.5
24.1
51.2
8.42
19.1
24.2
46.5
47.5
19.0
Dry
-
16.9
11.1
-
NTU
10/15/14
24.7
--
17.2
13.6
39.9
62.7
93.6
--
10
51
53
2.06
3.81
Dry
18.6
46.6
66.2
Dry
-
7.03
1.6
-
NTU
04/15/15
26.1
--
13.2
24.9
142
18.8
48.5
--
18.4
29.0
21.0
4.76
1.21
35.7
22.3
31.1
11.8
Dry
-
36.9
5.32
-
NTU
10/07/15
10.1
--
30.1
45.5
3.83
39.5
724
--
9.19
11.0
25.4
0.99
0.78
4.85
19.3
32.6
8.6
25.20
-
1.81
6.16
-
NTU
04/11/16
4.38
--
3.7
11.8
39.2
18.1
148
--
15.8
5.9
10.4
2.23
0.77
3.67
16.5
10.7
22.60
94.1
-
1.34
5.81
-
NTU
11/30/16
1.05
--
5.6
10.8
4.71
8.64
32.8
--
3.11
13.1
23.3
1.80
1.21
6.9
11.7
64.3
8.54
60.0
-
5.62
1.92
-
(Verification Event)
NTU
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
-
--
-
7.59
-
-
-
-
-
NTU
04/11/17
5.43
--
4.85
9.97
25.4
33.3
220
--
4.48
8.26
11.7
2.03
0.72
7.89
8.47
19.0
8.31
34.2
-
6.31
0.88
-
NTU
12/12/17
4.33
-
4.79
4.68
8.62
40.8
28.3
--
15.5
10.8
28.8
4.74
0.13
5.14
7.36
5.97
6.76
19.7
-
8.12
6.74
-
NTU
06/20/18
--
6.36
9.22
9.91
8.13
9.38
--
4.97
820
7.93
9.98
7.76
7.08
6.11
9.89
5.98
7.63
-
6.34
5.01
-
-
NTU
11/27/18
--
9.87
6.83
7.05
6.25
8.00
--
4.49
2.11
9.69
9.80
7.64
1.41
2.40
9.99
6.79
9.95
-
6.34
5.01
2.59
-
NTU
04/02/19
--
2.09
9.69
5.26
132
8.52
--
3.62
5.28
2.51
8.50
5.74
3.92
9.14
8.26
16.4
9.58
-
9.60
18.8
6.38
-
NTU
11/19/19
--
1.40
2.83
6.10
--
17.0
--
0.54
3.89
--
19.4
3.74
1.73
1.36
9.36
20.4
8.14
-
9.98
7.01
4.04
-
Verification Event
NTU
01/08/20
--
-
--
--
--
I --
--
--
--
--
I --
--
--
-
-
-
-
-
7.90
-
I -
I -
G:�PROJEGlS\Howe C-ty-127453-Moore-Env Sentces FY19-20%P100-WQM&Rep-g%DD GALGULNTIO W02-2-15 WQMR- 4 G O L D E R

February 2020 Page 3 of 3 Project No. 19127453
TABLE 5
Summary of Historical Groundwater Field Parameters
Water Quality Monitoring Report, 2019 Second Semi -Annual
Sampling
Event
Moore
County Landfill, NC Solid Waste Permit
No. 63-01
ive
:r Monitoring
Wells & MNA
Aberdeen, Moore County, North Carolina
Performance Monitoring Wells
Closed MSW
'
Offiste Private
Parameter
Oxidation Reduction Potential
Reporting
I"
Units
mV
04/28/06
r
NM
Active
r'
--
r Monitoring
NM
Wells
r
NM
r
NM
L
239
-46
for the Closed MSW
--
Landfill
31
265
258
79
Closed
254
MSW Monitoring
286
Wells & MNA Performance
2
Monitoring
9
Wells
-43
128
-
Monito
Well mg
NM
Well
NM
Blanks
-
(field)
mV
10/09/06
NM
--
NM
NM
NM
194
-68
--
7
252
2.4
32
220
232
4
-2
-4
-7
-
NM
NM
-
(lab prior to Oct. 07)
mV
04/24/07
NM
--
NM
NM
NM
198
-77
--
9
224
168
32
220
190
-8
-38
-60
22
-
NM
NM
-
mV
11/01/07
NM
--
NM
NM
NM
180
-171
--
-87
18
332
-48
331
252
-84
-119
-123
-72
-
NM
NM
-
mV
04/23/08
65.2
--
-89.5
50.4
134.8
45.7
-101.6
--
-58.2
31.1
21.4
4.7
67.1
60.9
-112.5
-113.5
-81.7
-133.5
-
-90.9
NM
-
mV
10/08/08
164
--
-119
89
179
217.6
-72.1
--
45.3
66.1
228
66.1
309.3
223.0
-106.6
-65.1
-94.4
-60.7
-
-32.1
NM
-
mV
04/13/09
92.5
--
-22.8
119.4
332.2
214.4
-87.8
--
-25.1
-16.3
283.5
-8.3
292.0
285.2
-73.6
-28.5
-90.9
-27.0
-
-17.9
363.2
-
mV
10/17/09
192.7
--
-62.6
134.8
182.0
117.6
-92.5
--
48.3
48.4
36.9
-18.1
255.8
296.9
-54.6
-24.6
-94.3
-16.4
-
-59.9
NM
-
mV
04/26/10
83.5
--
-52.3
118.0
145.7
200.1
-86.7
--
48.5
54.4
172.8
28.0
173.3
221.0
-98.0
42.7
-85.9
-77.9
-
-15.6
NM
-
mV
10/19/10
104.9
--
-51.8
155.3
132.6
208.2
-83.7
--
44.0
71.1
148.0
82.9
198.7
282.2
-81.7
-22.4
-94.8
-109.6
-
48.9
NM
-
mV
04/18/11
208.7
--
11.8
121.3
151.4
214.4
-62.8
--
-30.9
-2.2
223.4
45.2
220.0
267.0
-16.8
44.7
-79.4
-5.1
-
12.8
207.0
-
mV
10/10/11
138.6
--
-70.1
87.4
61.8
97.3
47.6
--
-85.1
-25.9
23.3
15.7
142.6
80.9
-86.3
-
-102.4
Dry
-
-75.4
109.7
-
mV
04/17/12
141.7
--
-5.4
126.4
187.8
163.0
-27.9
--
-53.9
16.3
67.2
138.4
180.8
244.8
-61.1
1.90
-111.8
Dry
-
-24.4
NM
-
mV
10/09/12
85.8
--
-32.2
111.0
60.8
89.8
-58.9
--
-76.4
13.1
70.0
19.4
101.4
106.2
-79.3
-32.1
-98.0
Dry
-
-53.2
NM
-
mV
04/15/13
170.1
--
-33.9
106.8
116.7
133.0
-86.8
--
-74.4
4.7
193.0
86.5
214.9
198.6
-38.7
-60.7
-113.4
Dry
-
-72.5
NM
-
mV
09/30/13
138.6
--
-33.2
104.8
81.0
213.2
41.6
--
-34.6
-3.3
308.5
128.0
332.6
286.1
45.7
43.9
-64.6
Dry
-
-16.4
NM
-
mV
04/16/14
40.4
--
-62.2
88.3
31.3
232.2
-95.8
--
-60.0
4.9
282.2
142.5
338.4
338.3
-59.3
-55.0
42.2
Dry
-
-39.8
NM
-
mV
10/15/14
209.1
--
-56.2
177.5
25
187.1
-77.9
--
-38.6
-81.9
245.9
58.8
394.5
Dry
-56.1
-21.9
-103
Dry
-
-60.7
336.9
-
mV
04/15/15
61.4
--
-52.6
6.8
16.5
-22.1
-9.1
--
-63.3
-53.7
90.4
-20.8
65.1
339.9
-55.9
-19.8
-97.2
Dry
-
-36.6
119.2
-
mV
10/07/15
3.8
--
-20.9
27.1
-116.5
40.5
-182.9
--
-61.1
-77.2
18.1
-61.9
20.2
115.6
-73.1
-96.2
-135.7
-
-
-100
45.5
-
mV
04/11/16
50.4
--
-29.2
40.7
8
64
-70.3
--
-55.3
-29.09
189.7
105
354.2
373.4
41.8
24.7
-70.4
-
-
-14.6
177.9
-
mV
11/30/16
34.9
--
46
74
-18.0
58.6
-86.6
--
-73.8
-65.1
379
66.8
345
230
-75.8
-58.4
-79.1
-27.60
-
-56.7
310
-
(Verification Event)
mV
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
-92.9
-
-
-
-
-
mV
04/11/17
68.2
--
-35.9
85.5
9.6
120
-85.6
--
45.8
-29.1
262
49.1
200
175
-38.5
56.4
-61.4
11.8
-
45.3
138
-
mV
12/12/17
80.8
--
1.7
211
17.2
62.0
-75.0
--
-87.9
-32.8
150
129
328
385
-66.3
-
-65.4
-1.8
-
42.5
337
-
mV
06/20/18
--
-16.0
-20.3
109
15.3
156
--
-66.1
-52.4
67.1
196
178
166
417
-22.4
3.2
-69.9
-
42.2
-29.0
-
-
mV
11/27/18
--
-72.5
-29.9
42.6
12.1
132
--
-81.8
-70.8
56.8
257
59.4
287
298
-146
-90.6
-103
-
-81.8
-65.7
175
-
mV
04/02/19
--
-78.0
-65.7
14.4
6.9
90
--
-94.6
-80.9
190.2
194
98.8
419
270
48
-77.2
-78
-
-17.6
-30.9
344
-
mV
11/19/19
--
-79.9
-73.5
138.5
--
42.0
--
-105.6
-12.1
--
38.4
43.3
56.8
369.3
-133.4
-97.6
-131.1
-
-123.1
-124.6
-31.0
-
erification Event
mV
01/08/20
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
-
-
-157.7
-
-
-
Dissolved Oxygen (field)
mg/L
04/28/06
NM
--
NM
NM
NM
7.79
1.02
--
0.32
0.49
7.02
0.59
4.19
7.98
0.63
0.44
0.47
0.37
-
NM
NM
-
(lab prior to Oct. 07)
mg/L
10/09/06
NM
--
NM
NM
NM
0.50
0.41
--
0.35
0.25
1.32
0.38
2.23
6.59
0.36
0.55
0.87
1.49
-
NM
NM
-
mg/L
04/24/07
NM
--
NM
NM
NM
4.26
0.99
--
0.91
0.84
6.37
5.25
4.26
10.02
0.90
1.19
0.75
1.41
-
NM
NM
-
mg/L
11/01/07
NM
--
NM
NM
NM
2.17
0.40
--
1.08
0.59
7.26
0.64
4.93
8.02
0.75
0.33
0.47
0.41
-
NM
NM
-
mg/L
04/23/08
1.69
--
2.29
2.49
2.43
4.50
1.55
--
1.48
1.58
5.66
1.53
6.74
9.65
1.78
1.66
2.20
1.60
-
2.24
NM
-
mg/L
10/08/08
2.28
--
0.67
0.54
0.79
1.67
0.72
--
0.98
2.15
5.41
0.81
3.84
7.12
0.49
0.86
6.29
1.46
-
0.85
NM
-
mg/L
04/13/09
1.49
--
0.68
2.06
2.00
2.65
1.12
--
1.30
1.45
5.55
1.40
5.52
8.29
0.67
1.38
0.78
1.66
-
1.31
NM
-
mg/L
10/17/09
0.88
--
0.89
1.37
0.95
1.80
0.85
--
1.04
1.15
1.84
1.23
4.89
9.10
0.74
0.55
1.05
3.97
-
2.05
NM
-
mg/L
04/26/10
1.23
--
0.43
0.99
1.21
1.06
0.28
--
1.05
1.28
4.23
0.91
5.52
7.96
0.54
1.98
0.70
0.96
-
1.08
NM
--
mg/L
10/19/10
0.54
--
0.25
1.96
1.13
2.07
0.60
--
0.60
0.47
4.77
0.27
4.52
7.77
0.31
1.50
0.31
0.36
-
0.50
NM
--
mg/L
04/18/11
0.46
--
0.89
0.97
0.89
1.90
0.25
--
0.55
0.62
4.94
0.59
5.15
8.02
0.65
2.38
0.59
0.72
-
0.77
8.89
--
mg/L
10/10/11
0.60
--
0.63
0.53
1.07
0.86
0.79
--
0.62
0.65
1.09
0.64
4.53
6.78
0.87
-
0.93
Dry
-
1.09
6.60
--
mg/L
04/17/12
1.00
--
0.24
1.78
2.73
1.44
1.31
--
0.91
1.01
1.58
0.68
5.64
9.09
0.29
7.01
0.88
Dry
-
1.07
NM
--
mg/L
10/09/12
0.23
--
0.48
0.39
0.32
4.86
0.23
--
0.23
0.24
0.56
0.49
2.98
6.36
0.43
6.38
0.57
Dry
-
0.44
NM
--
mg/L
04/15/13
0.86
--
0.83
0.89
1.21
2.97
1.04
--
0.81
0.82
5.34
0.73
6.64
8.50
1.13
40.5
0.41
Dry
-
0.54
NM
--
mg/L
09/30/13
0.32
--
0.42
0.47
0.61
0.70
0.68
--
0.42
0.27
1.95
0.40
2.48
7.46
2.29
0.70
0.34
Dry
--
0.37
NM
-
mg/L
04/16/14
0.33
--
0.77
0.49
1.79
7.87
0.49
--
0.53
1.79
6.04
0.39
5.89
8.20
1.05
1.55
0.36
Dry
--
0.48
NM
-
mg/L
10/15/14
0.57
--
0.90
0.71
0.65
1.07
0.85
--
0.68
0.60
0.95
0.58
1.93
Dry
0.67
1.27
0.88
Dry
--
0.41
6.14
-
mg/L
04/15/15
0.89
--
0.84
0.86
0.68
0.53
0.61
--
0.86
0.59
3.19
0.59
4.00
7.24
0.96
1.72
0.69
Dry
-
0.75
9.88
-
mg/L
10/07/15
0.93
--
1.24
2.00
0.81
1.90
0.40
--
0.38
0.49
3.61
1.65
2.76
5.45
0.59
0.35
5.13
-
-
0.72
8.02
-
mg/L
04/11/16
1.85
--
0.87
1.16
1.30
1.17
1.01
--
0.53
0.58
3.42
0.87
3.93
7.77
0.92
1.21
0.54
-
-
0.82
8.24
-
mg/L
11/30/16
0.20
--
0.33
0.18
0.22
0.10
0.05
--
0.71
0.13
2.78
0.28
4.11
7.26
0.22
1.34
1.12
0.42
-
0.18
7.35
-
(Verification Event)
mg/L
02/09/17
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
0.88
-
-
-
-
-
mg/L
04/11/17
0.30
--
0.18
0.18
0.51
1.52
0.18
--
0.56
0.16
3.83
0.45
3.99
7.02
0.34
1.17
0.41
0.67
-
0.37
8.09
-
mg/L
12/12/17
0.23
0.25
0.25
0.45
0.84
0.24
--
0.24
0.25
1.71
0.39
2.38
6.79
0.26
-
0.38
0.41
0.35
8.35
-
mg/L
06/20/18
--
0.19
0.24
0.23
0.44
0.19
--
0.47
0.21
0.69
3.71
0.23
7.08
7.45
1.39
0.15
0.26
-
0.26
0.24
-
-
mg/L
11/27/18
--
0.36
0.19
0.28
0.23
0.22
--
0.17
0.21
1.45
2.80
0.42
3.17
6.34
0.2
0.26
0.1
-
0.25
0.38
-
-
mg/L
04/02/19
--
0.12
0.04
0.11
0.28
1.12
--
0.27
0.11
2.76
2.34
0.12
3.21
6.62
0.2
0.27
0.24
-
0.18
0.2
10.88
-
mg/L
11/19/19
--
0.21
0.14
0.10
--
0.8
--
0.20
0.21
--
1.00
0.30
2.2
6.26
0.44
-97.6
0.24
-
0.28
0.36
11.21
-
(Verification Event
me L
01 OS 20
--
--
--
--
--
--
--
--
--
--
--
--
--
-
-
-
-
-
0.30
-
-
--
Notes:
1.) mg/L = milligrams per liter
2.) ND = not detected at or above the laboratory reporting limit
3.) NM = not measured
4.) uS/cm = microseimens per centimeter
5.) NTU = Nephelometric Turbidity Units
6.) S.U. = Standard Units
7.) Samples collected using low -flow purge and sample techniques (when possible)
G:�PROJEGlS\Howe C-ty-127453-Moore-Env Sentcee FY19-20%P100-WQM&Repro g\500 GALQULNTI W020-02-15 WQMR Ta 4 G O L D E R

Febntary 2020 Page 1 of 5 Project No. 19127453
TABLES
Summaryof Historical Surface Water Monitoring Results (Detected Constituents)
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Arsenic
ug/L
03I05/90
-
-
ND
NO
-
-
-
SW Standard = 10 ug1L
ug/L
0M1191
-
-
ND
ND
-
--
-
ug/L
03/10/92
--
-
ND
ND
-
-
-
uglL
04/20195
-
-
ND
ND
--
--
-
ug/L
O6/27/95
---
ND
ND
-
-
-
uglL
09/22195
-
-
ND
ND
--
-
-
ug/L
03128/96
--
-
ND
ND
-
-
-
uglL
10/29196
-
-
ND
ND
-
-
-
ug/L
04/08/97
---
ND
ND
-
-
-
uglL
10/29197
-
-
ND
ND
--
-
-
ug/L
04/30/98
---
ND
ND
-
-
-
uglL
10/14198
-
-
ND
ND
--
-
-
ug/L
04/27/99
---
ND
ND
-
-
-
uglL
10/21199
-
-
ND
ND
-
-
-
ug/L
03/14/00
---
ND
ND
-
-
-
uglL
04/19/00
-
-
ND
ND
--
-
-
ug/L
10/17/00
--
-
ND
ND
-
-
-
uglL
04/10/01
-
-
ND
ND
--
-
-
ug/L
10/11/01
--
-
ND
ND
-
-
-
uglL
04/18/02
-
-
ND
ND
-
-
-
ug/L
10/08/02
--
-
ND
ND
-
-
-
uglL
04/09/03
-
-
ND
ND
-
-
-
ug/L
10/13/03
--
-
ND
ND
-
-
-
uglL
04/26/04
-
-
ND
ND
-
-
-
ug/L
10/25/04
--
-
ND
ND
-
-
-
uglL
04/04/05
-
-
ND
ND
-
-
-
ug/L
10/04/05
--
-
ND
ND
-
-
-
uglL
04/28/06
-
-
ND
ND
-
-
-
ug/L
10/09/06
--
--
ND
ND
-
-
-
ug1L
04/24/07
-
-
ND
ND
-
-
-
ug/L
11/01/07
--
10
ND
ND
-
-
ND
ug1L
04/23/08
-
10
ND
ND
-
-
ND
ug/L
10/06/08
--
10
ND
ND
-
-
ND
ug1L
04/13/09
-
10
ND
ND
-
-
ND
ug/L
10/13/09
--
10
4.46
J
2.85 J
-
-
ND
ug1L
04/26/10
-
10
ND
ND
-
-
ND
ug/L
10/19/10
--
10
ND
ND
-
-
ND
ug1L
04/18/11
-
10
6.69
B
IN B
-
-
3.37 J
ug/L
10/10/11
--
10
ND
ND
-
-
ND
ug1L
04/17/12
-
10
ND
ND
--
-
5.70 J
ug/L
10/09/12
--
10
ND
ND
ND
ND
ND
ug1L
04/15/13
-
10
ND
3.57 B
ND
ND
3.34 J
ug/L
09/30/13
--
10
ND
ND
ND
ND
ND
ug1L
04/16/14
-
10
ND
ND
ND
ND
ND
ug/L
10/15/14
5.4
10
ND
7.20 d
9.37 J
ND
ND
ug1L
04/15/15
5.4
10
ND
ND
ND
ND
ND
ug/L
10/07/15
5.4
10
ND
ND
Dry
ND
ND
ug1L
04/12/16
5.4
10
ND
ND
Dry
ND
ND
ug/L
11/30/16
6.8
10
ND
ND
ND
ND
ND
ug1L
04/11/17
6.8
10
ND
ND
Dry
ND
ND
ug/L
12/12/17
6.8
10
7.17
J
ND
Dry
ND
ND
ug1L
O6/20/18
7.6
10
ND
ND
ND
ND
ND
ug/L
11/28/18
7.6
--
ND
ND
ND
ND
ND
ug1L
04/02/19
7.6
-
ND
ND
ND
ND
ND
u /L
11/19/19
7.6
ND
9.27 J
ND
ND
ND
Barium
ug1L
03/05/90
-
-
ND
ND
-
-
-
SWStandard =1000 ug/L
ug/L
03/2l/91
-
-
21
NO
-
-
-
ug1L
03/10M2
-
-
ND
ND
-
-
-
ug/L
04/20/95
---
ND
NO
-
-
-
ug/L
06/2]M5
-
-
ND
ND
-
-
-
4L
09/22195
--
-
ND
ND
-
-
-
ug/L
03/28196
-
-
ND
ND
-
-
-
4L
10/29196
--
-
ND
ND
-
-
-
ug/L
04A) 7
-
-
ND
ND
-
-
-
4L
10/29197
--
-
ND
ND
-
-
-
ug/L
04/30/98
-
-
ND
ND
-
-
-
4L
10/14/98
--
-
ND
ND
-
-
-
ug/L
04/2]/99
-
-
ND
ND
-
-
-
ug/L
10/21199
--
-
ND
ND
-
-
-
ug/L
ON 4/00
-
-
ND
ND
-
-
-
ug/L
04/19/00
--
-
ND
ND
-
-
-
ug/L
10/17/00
-
-
ND
ND
-
-
-
ug/L
04/10/01
--
-
ND
ND
-
-
-
ug/L
10/11/01
-
-
ND
ND
-
-
-
ug/L
04/18/02
--
-
ND
NO
-
-
-
ug/L
10/08/02
-
-
ND
ND
-
-
-
ug/L
04/09/03
--
--
ND
NO
-
-
-
ug/L
10/13/03
-
-
ND
ND
-
-
-
ug/L
04/26/04
--
-
ND
ND
-
-
-
ug/L
10/25/04
-
-
ND
ND
-
-
-
ug/L
04/04/05
--
-
ND
ND
-
-
-
ug/L
10/04/05
-
-
ND
ND
-
-
-
4L
04/28I06
--
-
ND
ND
-
-
-
ug/L
two /06
-
-
ND
ND
-
-
-
4L
04/24/07
--
--
ND
ND
-
-
-
ug/L
11/01/07
-
100
29.1
3
10.3 3
-
-
1.10 d
ug/L
04/23108
--
100
27.9
1
13.9 1
-
-
0.20 d
ug/L
two /08
-
100
29.5
3
12.5 3
-
-
ND
ug/L
04/13/09
--
100
28.0
1
14.2 1
-
-
ND
ug/L
10/13/09
-
100
29.6
3
11.6 3
-
-
1.02 d
ug/L
04/26/10
--
100
28.4
d
13.8 d
-
-
ND
ug/L
1019110
--
100
19.3
1
13.3 1
-
-
ND
ug/L
04/18/11
--
100
24.4
d
27.1 d
-
-
ND
uo/
10/10/11
--
100
23.6
1
11.7 1
-
-
ND
ug/L
04/17/12
--
100
24.0
d
1TS d
--
-
ND
ug/L
10/09/12
--
100
26.2
1
12.7 1
32.4 1
26.0 J
1.07 J
ug/L
04/15/13
--
100
28.0
d
12.5 d
32.1 d
24.2 1
ND
ug/L
09/30/13
--
100
26.5
1
10.9 1
22.0 1
41.0 J
ND
ug/L
04/16/14
--
100
22.5
d
18.3 d
196
25.7 1
ND
ug/L
1015/14
1
100
19.5
1
15.1 1
630
30.5 J
ND
ug/L
04/15 5
1
100
21.2
d
18.9 d
80.2 d
33.2 1
ND
ug/L
10/07/15
1
100
20.1
d
12.6 1
Dry
29.8 J
ND
ug/L
04/12/16
1
100
18.6
d
14.7 1
Dry
36.2 J
ND
ug/L
11/30/16
1
100
16.0
B
12.6 B
20.1 B
25.4 B
7.92
ug/L
0411117
1
100
23.0
1
13.0 1
Dry
22.2 1
ND
ug/L
12/12/17
1
100
17.0
d
9.82 1
Dry
19.9 J
ND
ug/L
O6/20/18
1
100
20.6
d
19.5 d
27.4 1
29.2 J
ND
ug/L
11/28/18
1
-
16.1
12.9
19.2
20.9
ND
ug/L
211:
00/19/
1
153
3.6
13
18.7
198
ND
. IL
1.1
22.1
20.0
ND
GOLDER

February 2020 Page 2 of 5 Project No. 19127453
TABLES
Summaryof Historical Surface Water Monitoring Results (Detected Constituents)
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Cadmium
ug/L
03I05/90
-
-
ND NO
- -
-
SW Standard
ug/L
OM1191
-
-
ND NO
- -
-
Acute = 0.82 ug/L
ug/L
03/10/92
-
-
NO NO
- -
-
Chronic = 0.15 ugl
ugIL
04/20195
-
-
NO NO
- --
-
ug/L
O6/27/95
--
-
NO NO
- -
-
uglL
09/22195
-
-
NO NO
- -
-
ug/L
03128/96
--
-
NO NO
- -
-
uglL
10/29196
-
-
NO NO
- -
-
ug/L
04/08/97
--
-
NO NO
- -
-
uglL
10/29197
-
-
NO NO
- -
-
ug/L
04/30/98
---
NO NO
- -
-
uglL
10/14198
-
-
NO NO
- -
-
ug/L
04/27/99
---
NO 7
- -
-
uglL
10/21199
-
-
NO NO
- -
-
ug/L
03/14/00
--
-
NO NO
- -
-
uglL
04/19/00
-
-
NO NO
- -
-
ug/L
10/17/00
--
-
NO NO
- -
-
uglL
04/10/01
-
-
NO NO
- -
-
ug/L
10/11/01
--
-
NO NO
- -
-
uglL
04/18/02
-
-
NO NO
- -
-
ug/L
10/08/02
--
-
NO 1
- -
-
uglL
04/09103
-
-
4 5
- -
-
ug/L
10/13/03
---
NO NO
- -
-
uglL
04/26104
-
-
NO 4
- -
-
ug/L
10/25/04
---
NO NO
- -
-
uglL
04/04105
-
-
NO 4
- -
-
ug/L
10/04/05
---
NO 1
- -
-
ug1L
04/28/06
-
-
NO NO
- -
-
ug/L
10/09/06
--
-
NO 1
- -
-
ug1L
04/24/07
-
-
NO NO
- -
-
ug/L
11/01/07
--
1
NO NO
- -
NO
ug1L
04/23/08
-
1
NO NO
- -
NO
ug/L
10/06/08
--
1
NO NO
- -
NO
ug1L
04/13/09
-
1
NO NO
- -
NO
ug/L
10/13/09
--
1
NO NO
- -
NO
ug1L
04/26/10
-
1
NO NO
- -
NO
ug/L
10/19/10
--
1
NO NO
- -
NO
ug1L
04/18/11
-
1
NO NO
- -
NO
ug/L
10/10/11
--
1
NO NO
- -
NO
ug1L
04/17/12
-
1
NO NO
- -
NO
ug/L
10/09/12
--
1
NO NO
NO NO
NO
ug1L
04/15/13
-
1
NO NO
NO NO
NO
ug/L
09/30/13
--
1
NO NO
NO NO
NO
ug1L
04/16/14
-
1
NO NO
NO NO
NO
ug/L
10/15/14
0.36
1
NO NO
NO NO
NO
ug1L
04/15/15
0.36
1
NO NO
NO NO
NO
ug/L
10/07/15
0.36
1
NO NO
Dry NO
NO
ug1L
04/12/16
0.36
1
NO NO
Dry NO
NO
ug/L
11/30/16
0.36
1
NO NO
NO NO
NO
ug1L
04/11/17
0.36
1
NO NO
Dry NO
NO
ug/L
12/12/17
0.36
1
NO NO
Dry NO
NO
ug1L
O6/20/18
0.36
1
NO NO
NO 0.36 B
0.38 d
ug/L
11/28/18
0.36
-
NO NO
NO NO
NO
ug1L
04/02/19
0.36
-
NO NO
NO NO
NO
u /L
11/19/19
0.36
OAS J NO
NO NO
NO
Chromium
ug1L
03/05/90
-
--
NO NO
- -
-
SW Standard
ug/L
03/2l/91
-
--
NO NO
- -
-
Acute = 16 uglL
ug1L
03/10/92
-
-
NO NO
- -
-
Chmolc = 11 ug/L
ug/L
04/20195
--
-
NO NO
- -
-
ug/L
O6/27/95
-
-
NO NO
- -
-
ug/L
09/22195
--
-
NO NO
- -
-
ug/L
03/28196
-
-
NO NO
- -
-
ug/L
10/29196
--
-
NO NO
- -
-
ug/L
04/08197
-
-
NO NO
- -
-
ug/L
10/29197
--
-
NO NO
- -
-
ug/L
04/30/98
-
-
NO NO
- -
-
ug/L
10/14/98
--
-
NO NO
- -
-
ug/L
04/2]/99
-
-
NO NO
- -
-
ug/L
10/21199
--
-
NO NO
- -
-
ug/L
ON 4/00
-
-
NO NO
- -
-
ug/L
04/19/00
--
-
NO NO
- -
-
ug/L
10/17/00
-
-
NO NO
- -
-
ug/L
04/10/01
--
-
NO NO
- -
-
ug/L
10/11/01
-
-
NO NO
- -
-
ug/L
04/18/02
--
-
NO NO
- -
-
ug/L
10/08/02
-
-
NO NO
- -
-
ug/L
04/09/03
--
-
NO NO
- -
-
ug/L
10/13/03
-
-
NO NO
- -
-
ug/L
04/26/04
--
-
NO NO
- -
-
ug/L
10/25/04
-
-
NO NO
- -
-
ug/L
04/04/05
--
-
NO NO
- -
-
ug/L
two /05
-
-
NO NO
- -
-
ug/L
04/28/06
--
--
NO NO
- -
-
ug/L
10/09/06
-
-
NO NO
- -
--
ug/L
04/24/07
--
-
NO NO
- -
--
ug/L
11/01/07
-
10
NO NO
- -
NO
ug/L
04/23108
--
10
NO NO
- -
NO
ug/L
two /08
-
10
NO NO
- -
NO
ug/L
04/13/09
--
10
NO NO
- -
NO
ug/L
10/13/09
-
10
NO NO
- -
NO
ug/L
04/26/10
--
10
NO NO
- -
NO
ug/L
101 9110
--
10
NO NO
- -
NO
ug/L
04/18/11
--
10
NO 1.19 1
- -
NO
ug/L
1010/11
--
10
NO NO
- -
NO
ug/L
04/1 ]112
--
10
NO NO
- -
NO
ug/L
10/09/12
--
10
NO NO
NO NO
NO
ug/L
04/1 S113
--
10
NO 1.47 B
NO NO
1.70 d
ug/L
09/30/13
--
10
NO NO
NO NO
NO
ug/L
04/16/14
--
10
NO NO
NO NO
NO
ug/L
101 5/14
1A
10
NO NO
NO NO
NO
ug/L
04/15115
1A
10
NO NO
NO NO
NO
ug/L
10/071 5
1A
10
NO NO
Dry NO
NO
ug/L
04/12/16
1A
10
NO NO
Dry NO
NO
ug/L
11/30/16
1A
10
NO NO
NO NO
NO
ug/L
04/11/17
1A
10
NO NO
Dry NO
NO
ug/L
12112/17
1A
10
NO NO
Dry NO
NO
ug/L
O6/20118
1A
10
NO NO
NO NO
NO
ug/L
11128I18
1A
-
NO NO
NO NO
NO
uglL
04/02119
1 4
--
NO NO
ND NO
NO
u IL
11/19119
1 4
ND NO
ND NO
NO
GOLDER

February 2020 Pag.3 of 5 Project No. 19127453
TABLES
Summaryof Historical Surface Water Monitoring Results (Detected Constituents)
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Lcad
ug/L
03I05/90
-
-
ND NO
- -
-
SW Standard
ug/L
0M1191
-
-
ND ND
- -
-
Acute = 14 ug(L
ug/L
03/10/92
-
-
ND ND
- -
-
Chronic = 0.54 ug1L
ugIL
04/20195
-
-
ND ND
- --
-
ug/L
O6/27/95
---
ND ND
- -
-
uglL
09/22195
-
-
ND ND
- -
-
ug/L
03128/96
--
-
ND ND
- -
-
uglL
10/29196
-
-
ND ND
- -
-
ug/L
04/08/97
---
ND ND
- -
-
uglL
10/29197
-
-
ND ND
- -
-
ug/L
04/30/98
---
ND ND
- -
-
uglL
10/14198
-
-
ND ND
- -
-
ug/L
04/27/99
---
ND ND
- -
-
uglL
10/21199
-
-
ND ND
- -
-
ug/L
03/14/00
---
ND ND
- -
-
uglL
04/19/00
-
-
ND ND
- -
-
ug/L
10/17/00
--
-
ND ND
- -
-
uglL
04/10/01
-
-
ND ND
- -
-
ug/L
10/11/01
--
-
ND ND
- -
-
uglL
04/18/02
-
-
ND ND
- -
-
ug/L
10/08/02
--
-
ND ND
- -
-
uglL
04/09103
-
-
ND ND
- -
-
ug/L
10/13/03
---
ND ND
- -
-
uglL
04/26104
-
-
ND ND
- -
-
ug/L
10/25/04
---
ND ND
- -
-
uglL
04/04105
-
-
ND ND
- -
-
ug/L
10/04/05
---
ND ND
- -
-
ug1L
04/28/06
-
-
ND ND
- -
-
ug/L
10/09/06
--
--
ND ND
- -
-
ug1L
04/24/07
-
-
ND ND
- -
-
ug/L
11/01/07
--
10
ND ND
- -
ND
ug1L
04/23/08
-
10
ND ND
- -
ND
ug/L
10/06/08
--
10
ND ND
- -
ND
ug1L
04/13/09
-
10
ND ND
- -
ND
ug/L
10/13/09
--
10
ND ND
- -
ND
ug1L
04/26/10
-
10
ND ND
- -
ND
ug/L
10/19/10
--
10
ND ND
- -
ND
ug1L
04/18/11
-
10
ND 6.77 J
- -
ND
ug/L
10/10/11
--
10
ND ND
- -
ND
ug1L
04/17/12
-
10
ND 2.00 J
- -
ND
ug/L
10/09/12
--
10
ND ND
2.38 1 ND
ND
ug1L
04/15/13
-
10
ND ND
ND ND
ND
ug/L
09/30/13
-
10
ND ND
ND 2.88 J
ND
ug1L
04/16/14
-
10
ND ND
18.3 ND
ND
ug/L
10/15/14
2.1
10
ND ND
15.3 ND
ND
ug1L
04/15/15
2.1
10
ND ND
ND ND
ND
ug/L
10/07/15
2.1
10
ND ND
Dry ND
ND
ug1L
04/12/16
2.1
10
ND ND
Dry ND
ND
ug/L
11/30/16
3.1
10
ND ND
ND ND
ND
ug1L
04/11/17
3.1
10
NO ND
Dry ND
ND
ug/L
12/12/17
3.1
10
ND NO
Dry ND
ND
ug1L
O6/20/18
3.1
10
NO ND
ND ND
ND
ug/L
11/28/18
3.1
-
ND ND
ND ND
ND
ug1L
04/02/19
3.1
-
NO ND
ND ND
ND
u /L
11/19/19
3.1
ND ND
ND ND
ND
Mercury
ug1L
03/05/90
-
--
ND ND
- -
-
SW Standard=0.012 ug/L
ug/L
03/2l/91
-
--
ND NO
- -
-
ug1L
03/10M2
-
-
ND ND
- -
-
ug/L
04/20/95
--
-
ND ND
- -
-
ug/L
O6/2]/95
-
-
ND ND
- -
-
ug/L
09/22/95
--
-
ND ND
- -
-
ug/L
03/28196
-
-
ND ND
- -
-
ug/L
10/29/96
--
-
ND ND
- -
-
ug/L
04/08197
-
-
ND ND
- -
-
ug/L
10/29/97
--
-
ND ND
- -
-
ug/L
04/30/98
-
-
ND ND
- -
-
ug/L
10/14/98
--
-
ND ND
- -
-
ug/L
04/2]/99
-
-
ND ND
- -
-
ug/L
10/21/99
--
-
ND ND
- -
-
ug/L
ON 4/00
-
-
ND ND
- -
-
ug/L
04/19/00
--
-
ND ND
- -
-
ug/L
10/17/00
-
-
ND ND
- -
-
ug/L
04/10/01
--
-
ND ND
- -
-
ug/L
10/11/01
-
-
ND ND
- -
-
ug/L
04/18/02
--
-
ND ND
- -
-
ug/L
10/08/02
-
-
ND ND
- -
-
ug/L
04/09/03
--
-
ND ND
- -
-
ug/L
10/13/03
-
-
ND ND
- -
-
ug/L
04/26/04
--
-
ND ND
- -
-
ug/L
10/25/04
-
-
ND ND
- -
-
uglL
04/04/05
--
-
ND ND
- -
-
uglL
10/04/05
--
-
ND ND
- -
-
ug/L
04/28/06
-
-
ND ND
- -
-
ug/L
10/09/06
--
--
ND ND
- -
-
ug/L
04/24/07
-
-
NO ND
- -
-
ug/L
11/01/07
--
0.2
ND ND
- -
ND
ug/L
04/23/08
--
0.2
ND ND
- -
ND
ug/L
two /08
-
D.2
NO ND
- -
ND
ug/L
04/13/09
--
0.2
ND ND
- -
ND
ug/L
10/13/09
-
0.2
NO ND
- -
ND
ug/L
04/26/10
--
0.2
ND ND
- -
ND
ug/L
101 9/10
--
0.2
ND ND
- -
ND
ug/L
04/18/11
--
0.2
ND ND
- -
ND
ug/L
101 0/11
--
0.2
ND ND
- -
ND
ug/L
04/1 ]/12
--
0.2
ND ND
- -
ND
ug/L
10/09/12
--
0.2
ND ND
ND ND
ND
ug/L
04/15/13
--
0.2
ND ND
ND ND
ND
ug/L
09/30/13
-
0.2
ND ND
ND ND
ND
ug/L
04/16/14
-
0.2
ND ND
0.190 1 ND
ND
ug/L
101 5/14
0.17
0.2
ND ND
0.411 (ND) ND
ND
ug/L
04/15I15
0.17
0.2
ND ND
0.0593 1 ND
ND
ug/L
10/071 5
0.17
0.2
ND ND
Dry ND
ND
ug/L
04/12/16
0.17
0.2
ND ND
Dry ND
ND
ug/L
11/30/16
0.17
0.2
ND ND
ND ND
ND
ug/L
04/11/17
0.17
0.2
ND ND
Dry ND
ND
ug/L
12/12/17
0.099
0.2
ND ND
Dry ND
ND
ug/L
O6120118
0.15
0.2
ND ND
ND ND
ND
ug/L
11/28/18
0.15
-
ND ND
ND ND
ND
ug/L
0112111
0.15
--
ND ND
ND ND
ND
u IL
11/19119
0.15
ND ND
ND ND
ND
GOLDER

February 2020 Page 4 of 5 Project No. 19127453
TABLES
Summaryof Historical Surface Water Monitoring Results (Detected Constituents)
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, INC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
LftD . t.ec ti.e.d.11,11 o an 1 t o r i n
Selenium
Reporting
u9IL
Sampi
04Y /0
Method Detection
-
SW
Lim fill
-
ND ND
- -
-
SW Standard = 5 ug/L
u.1L
10/0910:
-
-
ND NO
-- -
--
u9IL
04/24/07
-
-
NO NO
- -
--
uglL
11/01107
-
10
NO 2.2 J
- --
NO
u9IL
04/23/08
--
10
NO NO
- -
NO
u9IL
10/0fi108
-
10
NO NO
- -
NO
u9IL
04/13/09
--
10
59 B NO
- -
3.9 J
4L
10/13109
-
10
NO NO
- -
3.03 J
u9IL
04/28/10
--
10
NO NO
- -
NO
4L
to/19/10
-
10
NO NO
- -
NO
u9IL
04/18/11
--
10
NO NO
- -
NO
4L
to/10/11
-
10
NO NO
- -
NO J
u9IL
04/17/12
--
10
NO NO
- -
NO
4L
10/09/12
-
10
NO NO
NO NO
NO
u9IL
04/1&13
--
10
NO NO
NO NO
NO
4L
09/30/13
-
10
NO NO
NO NO
NO
u9IL
04/16/14
--
10
NO NO
NO NO
NO
4L
10/1&14
5
10
NO NO
NO NO
NO
u9IL
04/151 5
5
10
NO NO
NO NO
NO
4L
10/07/15
5
10
NO NO
Dry NO
NO
u9IL
04/12/16
5
10
NO NO
Dry NO
NO
4L
11M 16
6.2
10
NO NO
NO NO
NO
u9IL
04/11/17
6.2
10
NO NO
Dry NO
NO
4L
12/12/17
6.2
10
NO NO
Dry NO
NO
u9IL
06/20/18
6.2
10
NO NO
NO NO
NO
u9IL
11/2&18
6.2
-
NO NO
NO NO
NO
u9IL
04/02/19
6.2
--
NO NO
NO NO
NO
, IL
11/19/19
6.2
NO NO
NO NO
NO
Sit-
u9IL
04/28/06
--
--
NO NO
- -
-
SW Standard
u9IL
10/09/06
-
--
NO NO
- -
-
Acuts = 30 uglL
u9IL
04/24/07
--
-
NO ND
- -
-
Chronic 0.06 ug&
ugl
11/01/07
-
10
NO NO
- -
NO
u9IL
04/23/08
--
10
NO NO
- -
2.1 J
ug'
10/0fi/08
-
10
NO NO
- -
2.0 J
4L
04/13/09
--
10
NO NO
- -
NO
ugl
10/13/09
-
10
NO NO
- -
NO
u9IL
04/28/10
--
10
NO NO
- -
NO
ugl
10/19/10
-
10
NO NO
- -
NO
u9IL
04/18/11
--
10
NO NO
- -
NO
ugl
10/10/11
-
10
NO NO
- -
NO
u9IL
04/17/12
--
10
NO NO
- -
NO
ugl
10/09/12
-
10
NO NO
NO NO
NO
u9IL
04/1&13
--
10
NO NO
NO NO
NO
ugl
09/30/13
-
10
NO NO
NO NO
NO
u9IL
04/1 W14
--
10
NO NO
NO NO
NO
ugl
10/1&14
1.9
10
NO NO
NO NO
NO
u9IL
04/151 5
19
10
NO NO
NO NO
NO
ugl
1OV0715
1.9
10
NO NO
Dry NO
NO
u9IL
04/121 6
19
10
NO NO
Dry NO
NO
ugl
11/30/16
1.9
10
NO NO
NO NO
NO
u9IL
04/11/17
19
10
NO NO
Dry NO
NO
ugl
12I12/17
1.9
10
NO NO
Dry NO
1.95 J
u9IL
O6/20/18
19
10
NO NO
NO NO
NO
ugl
1la 18
1.9
-
NO NO
NO NO
NO
u9IL
04/02/19
19
-
NO NO
NO NO
NO
. IL
11/19/19
1.9
-
NO NO
NO NO
NO
Acetone
u9IL
11/01/07
--
100
NO NO
- -
NO
SW Standard 2000 ug/L
u9IL
04/23/O8
-
100
NO NO
- -
NO
u9IL
10/0108
--
100
48 B 4.0 B
- -
5.0 J
ugl
04/13/09
-
100
NO NO
- -
NO
u9IL
10/13/09
--
100
NO NO
- -
NO
ugl
04/26/10
-
100
NO NO
- -
NO
uglL
10/19/10
--
100
NO NO
- -
NO
ugl
04/1&11
-
100
NO NO
- -
NO
uglL
10/10/11
--
100
NO NO
- -
NO
ugl
04/1]/12
-
100
NO NO
- -
NO
uglL
10/09/12
--
100
NO NO
NO NO
NO
ugl
04/1&13
-
100
NO NO
NO NO
NO
uglL
09/30/13
--
100
NO NO
NO NO
NO
ugl
04/i 6/14
-
100
NO NO
NO NO
NO
uglL
10/1&14
1.2
100
NO NO
13 J NO
NO
ugl
04/15/15
1.2
100
NO NO
7.4 J 6.0 J
NO
uglL
10/071 5
1.2
100
NO NO
Dry NO
NO
ugl
04/12/16
1.2
100
NO NO
Dry NO
NO
uglL
11/30/16
10
100
NO NO
NO NO
NO
ugl
04/11/17
10
100
NO NO
Dry NO
NO
u9IL
1211217
10
100
NO NO
Dry NO
NO
ugl
O6/20/18
10
100
NO NO
NO NO
15
uglL
07/301 8
10
100
NO --
NO --
NO
ugl
11/28/18
10
-
NO NO
NO NO
NO
uglL
04/02/19
10
-
NO NO
NO NO
NO
. IL
1 11/19/19
10
1
NO NO
NO NO
NO
Chlombenzene
uglL
04/28/O6
-
-
NO NO
- -
--
SW Standard = 140 ug&
u9IL
10/09/06
-
-
NO NO
- -
--
uglL
04/24/07
-
-
NO NO
- -
--
uglL
11/01/07
-
3
0.88 J NO
- -
NO
uglL
04/23108
--
3
0.61 J NO
- -
NO
ugl
two /08
-
3
0.60 J NO
- -
NO
uglL
04/13/09
--
3
0.72 J NO
- -
NO
ugl
10/13/09
-
3
0.74 J NO
- -
NO
u9IL
04/26/10
--
3
0.71 J NO
- -
NO
u9IL
101 9110
--
3
NO NO
- -
NO
u9IL
04/18/11
--
3
NO NO
- -
NO
u9IL
101 0/11
--
3
NO NO
- -
NO
u9IL
04/1 112
--
3
NO NO
- -
NO
u9IL
10/09/12
--
3
0.76 J NO
NO NO
NO
u9IL
04/1&13
--
3
0.88 J NO
NO NO
NO
u9IL
09/30/13
-
3
0.70 J NO
NO NO
NO
u9IL
04/16/14
-
3
0.67 J NO
NO NO
NO
u9IL
101 5/14
0.17
3
NO NO
NO NO
NO
u9IL
04/1&15
0.17
3
NO NO
NO NO
NO
u9IL
10/0715
0.17
3
NO NO
Dry NO
NO
u9IL
04/12/16
0.17
3
NO NO
Dry NO
NO
u9IL
11/30/16
0.17
3
NO NO
0.42 J NO
NO
u9IL
04/11/17
0.17
3
0.86 J NO
Dry NO
NO
u9IL
12/14/17
0.17
3
0.43 J NO
Dry NO
NO
u9IL
06120/18
0.17
3
0.42 J NO
0.58 J NO
NO
u9IL
07/30/18
0.17
3
NO --
NO --
NO
u9IL
11/2&18
0.17
--
NO NO
NO NO
NO
uglL
06/02/19
0.17
-
NO ND
NO NO
NO
u IL
11/19/19
0.17
0.57 J ND
NONO
NO
GOLDER

Febuary 2020 Page 5 of 5
Project No. 19127453
TABLES
Summaryof Historical Surface Water Monitoring Results (Detected Constituents)
Water Quality
Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Detected Monitoring
Constituent/Para meter
cis-1,2-Dichloroethan.
Rcp.rting
Unim
ug/L
Sample
Data
04/28I0
Method Detection ReS.
'MI �SW-2
Liomit
it
- - ND
SW
SW Standard = 60 u9d.
uglL
10/0910:
- - NO
NO
-
-
--
ug/L
04/24/07
- - NO
NO
-
-
--
uglL
11/01107
- 5 0.33 J
NO
-
--
NO
ug/L
04/23/08
-- 5 NO
NO
-
-
NO
uglL
10/0fi108
- 5 NO
NO
-
-
NO
ug/L
04/13/09
-- 5 NO
NO
-
-
NO
uglL
10/13109
- 5 NO
NO
-
-
NO
ug/L
04/28/10
-- 5 NO
NO
-
-
NO
uglL
to/19/10
- 5 NO
NO
-
-
NO
ug/L
04/18/11
-- 5 NO
NO
-
-
NO
uglL
to/10/11
- 5 NO
NO
-
-
NO
ug/L
04/17/12
-- 5 NO
NO
-
-
NO
uglL
10/09/12
- 5 NO
NO
NO
NO
NO
ug/L
04/15/13
-- 5 NO
NO
NO
NO
NO
uglL
09/30/13
- 5 NO
NO
NO
NO
NO
ug/L
04/16/14
-- 5 NO
NO
NO
NO
NO
uglL
10/15/14
0.15 5 NO
NO
NO
NO
NO
ug/L
04/15/15
0.15 5 NO
NO
NO
NO
NO
uglL
10/0]/15
0.15 5 NO
NO
Dry
NO
NO
ug/L
04/12/16
0.15 5 NO
NO
Dry
NO
NO
uglL
11/30/16
0.15 5 NO
NO
NO
NO
NO
ug/L
04/11/17
0.15 5 NO
NO
Dry
NO
0.54 J
uglL
12/12/17
0.15 5 NO
NO
Dry
NO
NO
ug/L
06/20/18
0.15 5 NO
NO
NO
NO
NO
uglL
07/30/18
0.15 5 NO
-
NO
-
NO
ug/L
11/28/18
0.15 -- NO
NO
NO
NO
NO
uglL
04/02/19
0.15 - NO
NO
NO
NO
NO
cm-
I 11/19/19
0.15 NO
ND
NO
NO
ND
Tduene
uglL
11/01/07
-
1
NO
ND
-
-
ND
SW Standard = 11 ug/L
uglL
04/23/08
-
1
NO
ND
-
-
ND
(freshwater standard)
ugd-
10/0 /08
--
1
NO
ND
-
-
ND
ug/L
04/13/09
--
1
NO
ND
-
-
ND
ug/L
10/13/09
--
1
NO
ND
-
-
ND
ug/L
04/28/10
--
1
NO
ND
-
-
ND
ug/L
10/19/10
--
1
NO
ND
-
-
ND
ug/L
04/18/11
--
1
NO
ND
-
-
ND
ug/L
10/10/11
--
1
NO
ND
-
-
ND
ug/L
04/17/12
--
1
NO
ND
-
-
ND
ug/L
10/09/12
--
1
NO
ND
095 J
ND
ND
ugd-
04/15/13
--
1
NO
ND
ND
ND
ND
ug/L
09/30/13
--
1
NO
ND
ND
ND
ND
ugd-
04/16/14
--
1
NO
ND
ND
ND
ND
ug/L
10/15/14
0.14
1
NO
ND
ND
ND
ND
ug/L
04/15/15
0.14
1
NO
ND
ND
ND
ND
ug/L
10/07/15
0.14
1
NO
ND
Dry
ND
ND
ug/L
04/12/16
0.14
1
NO
ND
Dry
ND
ND
ug/L
11/30/16
0.14
1
NO
ND
NO
ND
ND
ug/L
04/11/17
0.14
1
NO
ND
Dry
ND
0.80 J
ug/L
12/12/17
0.14
1
NO
ND
Dry
ND
ND
ugd-
06/20/18
0.14
1
NO
NO
NO
NO
ND
ug/L
07/30/18
0.14
1
NO
--
NO
--
ND
ug/L
11/28/18
0.14
-
NO
NO
ND
0.57 J
ND
(Ver0lcatlan Sample)
ug/L
02/13/19
0.14
--
-
--
--
NO
--
19
04/02/19
0.14
--
NO
NO
NO
NO
ND
u IL
11/19/19
0,14
NO
NO
NO
NO
ND
1,4Dloxane'N. P�[e 11. = 0.35 ug/L
uglL
11/28/18
1.2
--
NO
NO
2.7
NO
ND
(Verification Sample)
uglL
02/13/19
1.2
-
-
--
2.7
Is
--
--
ZL
04/02/19
1.2
-
NO
NO
2.2
NO
ND
u IL
11/19/19
1.2
1.3 J
NO
1.0 J
ND
Notes'
1.) mglL = milligrams per lter
2.) u91L = micrograms per liter
3.) NO = Not detected at the staled reporting limit
4.) J = Estimated value
5 ) --= No available data
6.) SW S Reporting Limit = NC PQL or lab -specific reporting limit prior to October 2007 and NCSW SL starting in October 2007.
7.)Sheded = Constituent exceeds applicable Surface Water Standard
eJ Blanks =Field, trip and method blanks
9J Surface Water Standards based on W S-ll, High Quality Water Classlfcation for Horse Creek and 0s tributary per 15A NCAC 2B.
10.)SW Standard for lead is a Narrative Standard per 2B.0211
11.) Upstream and downstream designations based on inspection of site cond0lons and flow regimes. Reports prior to October 2009 had the designations inadvertently switched.
12.1 For standards with both acute and chronic listed. a cute = highlighted and chronic = bolded
GOLDER

February 2020 Page 1 of 2 Project No. 19127453
TABLE 7
Summary of Historical Surface Water Field Parameters
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63.01
Aberdeen, Moore County, North Carolina
Detected Monitoring
Constituent/Parameter
pH (field)
Reporting
Units
S.U.
Sample
Date
04/28/06
_0 Upstream
A&_ SW-2
6.40 5.10
Downstream
SW-3 SW-4
-- --
Blanks
--
S.U.
10/09/06
6.50 4.80
-- --
--
S.U.
04/24/07
6.60 6.10
-- --
S.U.
11/01/07
5.58 5.56
-- --
S.U.
04/23/08
7.65 6.46
-- --
S.U.
10/06/08
6.29 5.61
-- --
S.U.
04/13/09
6.01 5.30
-- --
S.U.
10/13/09
5.98 7.31
-- --
S.U.
04/26/10
5.99 6.21
-- --
S.U.
10/19/10
5.45 3.92
-- --
S.U.
04/18/11
5.85 3.54
-- --
S.U.
10/10/11
6.59 5.90
-- --
S.U.
04/17/12
5.93 4.88
-- --
-
S.U.
10/09/12
6.71 5.57
6.94 5.57
-
S.U.
04/15/13
6.72 5.72
6.27 5.93
-
S.U.
09/30/13
6.34 5.85
6.03 6.41
-
S.U.
04/16/14
6.97 5.67
6.29 6.75
-
S.U.
10/15/14
5.88 8.19
5.91 6.52
-
S.U.
04/15/15
5.54 5.17
5.16 5.93
-
S.U.
10/09/15
3.02 4.30
Dry 4.18
-
S.U.
04/11/16
5.76 6.50
Dry 6.04
-
S.U.
11/30/16
6.03 7.40
5.64 6.88
-
S.U.
04/11/17
6.48 6.48
Dry 6.40
-
S.U.
12/14/17
5.71 5.97
Dry 6.32
-
S.U.
06/20/18
6.01 5.05
6.09 5.79
-
(verification event)
S.U.
07/30/18
5.71 -
5.91 -
-
S.U.
11/28/18
5.70 7.99
4.67 6.71
-
(verification event)
S.U.
02/13/19
- -
6.87 6.95
-
S.U.
04/02/19
5.83 6.37
6.51 6.63
-
S.U.
11/21/19
6.85 6.65
6.43 6.51
Specific Conductance
us/cm
04/28/06
175 43
-- --
(lab prior to Nov 07 event)
us/cm
10/09/06
164 49
-- --
--
us/cm
04/24/07
173 37
-- --
-
us/cm
11/01/07
175 25
-- --
-
us/cm
04/23/08
161 27
-- --
-
us/cm
10/06/08
186 49
-- --
-
us/cm
04/13/09
171 31
-- --
-
us/cm
10/13/09
154 23
-- --
-
us/cm
04/26/10
161 25
-- --
-
us/cm
10/19/10
99 41
-- --
-
us/cm
04/18/11
157 53
-- --
-
us/cm
10/10/11
104 36
-- --
-
us/cm
04/17/12
87 24
-- --
-
uS/cm
10/09/12
146 18
99 111
-
uS/cm
04/15/13
126 32
100 238
-
uS/cm
09/30/13
141 27
108 104
-
uS/cm
04/16/14
174 65
108 214
-
uS/cm
10/15/14
112 75
143 241
-
uS/cm
04/15/15
80 37
85 177
-
uS/cm
10/09/15
84 41
Dry 217
-
uS/cm
04/11/16
67 44
Dry 165
-
uS/cm
11/30/16
105 33
159 339
-
uS/cm
04/11/17
172 36
Dry 164
-
uS/cm
12/14/17
117 35
Dry 176
-
uS/cm
06/20/18
99.2 590
163 236
-
(verification event)
us/cm
07/30/18
49.1 -
68.2 -
-
uS/cm
11/28/18
90.5 34.7
71.1 189
-
(verification event)
US/cm
02/13/19
- -
152 182
-
uS/cm
04/02/19
86.6 39.2
151 153
-
uS/cm
11/21/19
341 41.7
96.1 158
Temperature
Celsius
04/28/06
16.00 15.00
-- --
(lab prior to Nov 07 event)
Celsius
10/09/06
18.00 19.00
-- --
--
Celsius
04/24/07
17.00 18.00
-- --
-
Celsius
11/01/07
17.20 16.49
-- --
-
Celsius
04/23/08
17.46 18.33
-- --
-
Celsius
10/06/08
16.42 18.07
-- --
-
Celsius
04/13/09
14.48 14.66
-- --
-
Celsius
10/13/09
17.60 17.92
-- --
-
Celsius
04/26/10
17.17 21.71
-- --
-
Celsius
10/19/10
16.08 14.95
-- --
-
Celsius
04/18/11
18.61 17.55
-- --
-
Celsius
10/10/11
16.99 17.13
-- --
-
Celsius
04/17/12
15.75 17.52
-- --
-
Celsius
10/09/12
15.31 15.58
14.40 16.68
-
Celsius
04/15/13
18.07 18.37
16.25 16.64
-
Celsius
09/30/13
18.20 16.50
20.50 16.00
-
Celsius
04/16/14
16.20 12.30
18.60 12.20
-
Celsius
10/15/14
17.80 20.40
21.3 18.90
-
Celsius
04/15/15
15.47 18.59
16.95 16.89
-
Celsius
10/09/15
17.59 20.46
Dry 19.59
-
Celsius
04/11/16
14.60 16.90
Dry 16.10
-
Celsius
11/30/16
14.30 16.60
13.00 16.34
-
Celsius
04/11/17
17.89 22.61
Dry 21.59
-
Celsius
12/14/17
11.20 6.40
Dry 8.90
-
Celsius
06/20/18
19.7 23.06
21.6 22.3
-
(verification event)
Celsius
07/30/18
20.8 -
24.9 -
-
Celsius
11/28/18
12.5 7.8
10.8 9.7
-
(verification event)
Celsius
02/13/19
- -
13.1 13.7
-
Celsius
04/02/19
15.1 17.8
16.5 19.6
-
Celsius
1 11/21/19
1 14.7 10.5
1 13.4 13.3
GOLDER

February 2020 Page 2 of 2 Project No. 19127453
TABLE 7
Summary of Historical Surface Water Field Parameters
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63.01
Aberdeen, Moore County, North Carolina
L...t'.'ctu.d M onitoring
Co.. " MIParameter
Turbidity (field)
Reporting
Units
NTU
Sample
Date
11/01/07
_0 Upstream
JR.- SW-2
200 250
Downstream
SW-3 SW-4
-- --
Blanks
--
NTU
04/23/08
9.81 3.62
-- --
--
NTU
10/06/08
13.0 3.13
-- --
-
NTU
04/13/09
12.1 9.69
-- --
-
NTU
10/13/09
12.3 9.50
-- --
-
NTU
04/26/10
12.1 6.99
-- --
-
NTU
10/19/10
12.5 5.94
-- --
-
NTU
04/18/11
32.1 28.5
-- --
-
NTU
10/10/11
8.30 6.49
-- --
-
NTU
04/17/12
17.1 24.8
-- --
-
NTU
10/09/12
7.00 19.5
78.7 39.7
-
NTU
04/15/13
16.9 4.63
33.3 11.7
-
NTU
09/30/13
16.0 5.99
35.1 738
-
NTU
04/16/14
12.6 5.23
14.8 28.2
-
NTU
10/15/14
9.7 1.65
23.5 20.8
-
NTU
04/15/15
71.0 7.47
128 13.2
-
NTU
10/09/15
10.2 7.79
Dry 26.7
-
NTU
04/11/16
60.8 1.31
Dry 194
-
NTU
11/30/16
4.66 1.76
11.0 19.2
-
NTU
04/11/17
16.4 4.50
Dry 12.6
-
NTU
12/14/17
1.76 1.04
Dry 2.94
-
NTU
06/20/18
12.1 5.98
107 22.3
-
(verification event)
NTU
07/30/18
28.0 -
4.57 -
-
NTU
11/28/18
5.89 3.30
21.1 9.19
-
(verification event)
NTU
02/13/19
- -
19.2 14.5
-
NTU
04/02/19
5.49 -
23.4 13.4
-
NTU
11/21/19
4.10 7.31
20.3 8.59
Oxidation Reduction Potential
mV
11/01/07
-15.0 107
-- --
mV
04/23/08
-16.5 67.1
-- --
--
mV
10/06/08
-40.0 144
-- --
-
mV
04/13/09
-12.7 182
-- --
-
mV
10/13/09
-27.6 66.8
-- --
-
mV
04/26/10
-5.5 43.5
-- --
-
mV
10/19/10
-108 168
-- --
-
mV
04/18/11
-6.7 232
-- --
-
mV
10/10/11
-2.5 105
-- --
-
mV
04/17/12
-9.3 139
-- --
-
mV
10/09/12
-44.6 74.8
58.0 29.4
-
mV
04/15/13
3.1 93.7
17.8 -40.8
-
mV
09/30/13
6.8 165
89.2 34.3
-
mV
04/16/14
-29.0 222
111 8.4
-
mV
10/15/14
96.1 200
251 247
-
mV
04/15/15
45.9 181
112 61.0
-
mV
10/09/15
157 73.0
Dry 78.9
-
mV
04/11/16
70.1 129.5
Dry 13.3
-
mV
11/30/16
40.5 59.2
13.7 -43.7
-
mV
04/11/17
-8.1 11.8
Dry 17.6
-
mV
12/14/17
149.3 172.7
Dry 57.1
-
mV
06/20/18
104.5 402.9
62.9 346.7
-
(verification event)
mV
07/30/18
171.0 -
73.4 -
-
mV
11/28/18
22.7 79.2
100 9.0
-
(verification event)
mV
02/13/19
- -
61.6 90
-
mV
04/02/19
63.9 119.8
181.8 134.1
-
mV
11/21/19
-148.8 -68.6
-43.4 -43.0
Dissolved Oxygen (field)
mg/L
11/01/07
9.02 9.36
-- --
mg/L
04/23/08
7.61 7.91
-- --
--
mg/L
10/06/08
10.2 11.2
-- --
--
mg/L
04/13/09
8.58 7.87
-- --
-
mg/L
10/13/09
9.27 9.20
-- --
-
mg/L
04/26/10
7.38 7.45
-- --
-
mg/L
10/19/10
8.35 3.19
-- --
-
mg/L
04/18/11
5.75 2.45
-- --
-
mg/L
10/10/11
7.48 7.24
-- --
-
mg/L
04/17/12
8.79 6.91
-- --
-
mg/L
10/09/12
7.77 4.90
3.97 6.23
-
mg/L
04/15/13
4.35 4.35
2.88 3.79
-
mg/L
09/30/13
5.82 3.58
6.15 5.60
-
mg/L
04/16/14
6.76 6.15
3.51 8.71
-
mg/L
10/15/14
6.04 3.59
2.11 3.20
-
mg/L
04/15/15
6.36 3.57
4.77 5.70
-
mg/L
10/09/15
5.96 5.06
Dry 6.07
-
mg/L
04/11/16
8.44 5.65
Dry 7.61
-
mg/L
11/30/16
6.28 6.19
8.93 6.87
-
mg/L
04/11/17
6.21 7.07
Dry 6.77
-
mg/L
12/14/17
5.99 8.35
Dry 9.18
-
mg/L
06/20/18
5.36 0.15
7.24 6.89
-
(verification event)
mg/L
07/30/18
6.09 -
3.52 -
-
mg/L
11/28/18
7.10 9.8
2.15 8.74
-
(verification event)
mg/L
02/13/19
- -
8.98 7.72
-
mg/L
04/02/19
7.66 8.55
8.16 6.28
-
m /L
1 11/21/19
1 0.44 10.4
1 8.53 8.35
Notes:
1.) mg/L = milligrams per liter
2.) S.U. = Standard Units
3.) NTU = Nephelometric Turbidity Units
4.) uS/cm = Microsiemens per centimeter
5.) mV = Millivolts
6.) -- = No data available
7.) Upstream and downstream designations based on inspection of site conditions and flow regimes. Reports prior to
October 2009 had the designations inadvertently switched.
GOLDER

February 2020 Page 1 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Parameter
Acetic Acid
Reporting
Unit.
mg/L
Sample
Date
04/28/O6
Method
Detection
Limit
0.07
SwS
Reporting
Limit
--
Background
Monitoring Well
ND
r
NM
Active
--
C&D Monitoring
NM
Wells
NM
NM
ND
Active
0.646
C&D Monitoring
for
--
Wells & MNA Performance
the Closed MSW
ND
Monitoring Wells
Landfill
�w
ND --
--
ND
ND
Closed MSW
ND
Monitoring Wells
0.106
& MNA Performance
ND
Monitoring Wells
0.189
ND
--
MClo ad MSW
onitoring Well
NM
Blanks
--
mg/L
10/09/06
-
--
0.09
NM
--
NM
NM
NM
0.09
0.14
-
0.13
0.13 --
--
0.121
0.11
0.1
0.18
0.15
0.16
0.13
--
NM
--
mg/L
04/24/07
-
--
--
NM
--
NM
NM
NM
--
--
-
-
-- --
--
-
-
--
-
-
-
-
--
NM
--
mg/L
10/31/07
0.065
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/21/08
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.083
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
4.6 -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/10/11
0.040
--
0.69
NM
--
NM
NM
NM
0.69
NO
-
NO
1.4 -
--
NO
NO
0.83
2.6
-
NO
Dry
--
NM
NO
mg/L
04117/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
mg/L
10I09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
mg/L
09/30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04,16114
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
to"5/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/07/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/11/16
--
--
ND
NM
--
NM
NM
NM
ND
ND
-
2.3
ND --
--
ND
3.0
ND
18
13
ND
5.5
--
NM
ND
mg,
11/30/16
0.16
--
ND
NM
--
NM
NM
NM
ND
7.6
-
4.10
ND --
--
ND
4.2
ND
5.4
1.2
12.0
10
--
NM
ND
mg/L
04/1 1/1 7
0.16
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.16
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
-
NM
NM
mg/L
06I20/18
0.16
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
-
NM
NM
mg/L
11/27/18
0.16
--
NM
--
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
mg/L
04/02/19
0.16
--
NM
--
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.16
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
Butryic Acid
mg/L
04/28/06
0.07
--
NO
NM
--
NM
NM
NM
NO
0.181
--
NO
NO --
--
NO
0.113
NO
NO
NO
0.328
NO
-
NM
--
mg/L
10I09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
ND
NO
NO
NO
NO
NO
--
NM
--
mg/L
04124/07
-
--
--
NM
--
NM
NM
NM
--
--
-
-
-- -
-
-
-
--
-
-
-
-
--
NM
--
mg/L
10131/07
0.1
--
NO
NM
--
NM
NM
NM
ND
ND
-
NO
ND -
-
NO
NO
ND
NO
NO
NO
NO
--
NM
NO
mg/L
04121/08
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.16
--
NO
NM
--
NM
NM
NM
NO
1.10
-
NO
NO --
--
NO
ND
ND
NO
NO
NO
NO
--
NM
ND
mg/L
10/10/11
0.024
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
ND
ND
NO
-
NO
Dry
--
NM
NO
mg/L
04/17/12
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
09/30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/16/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/15/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
101 7/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
0411/16
-
--
ND
NM
--
NM
NM
NM
ND
ND
-
ND
ND -
--
ND
ND
ND
ND
ND
ND
ND
--
NM
ND
mg/L
11/30/16
0.089
--
ND
NM
--
NM
NM
NM
ND
ND
-
NO
ND -
--
NO
NO
ND
NO
NO
NO
NO
--
NM
ND
mg/L
04/11/17
0.089
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.089
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
06/20/18
0.089
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
11/27/18
0.089
--
NM
--
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
mg/L
04/02/19
0.089
--
NM
--
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.089
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
Hexanoic Acid
mg/L
04/28/06
0.1
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
NO
NO
NO
--
NM
--
mg/L
10I09/06
-
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
0.12 --
--
ND
NO
NO
NO
NO
NO
NO
--
NM
--
mg/L
04124/07
--
--
--
NM
--
NM
NM
NM
--
--
-
-
-- --
--
-
-
--
-
-
-
-
--
NM
mg/L
10/31/07
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/21/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.23
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
NO --
--
NO
ND
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/10/11
0.087
--
NO
NM
--
NM
NM
NM
ND
NO
-
0.26
NO --
--
NO
ND
NO
NO
-
NO
Dry
--
NM
NO
mg/L
04/17/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
09/30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/16/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/15/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/07/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/11/16
--
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
11/30/16
0.26
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
NO --
--
NO
NO
ND
NO
NO
NO
NO
--
NM
NO
mg/L
04,11"7
0.26
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.26
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
06120M8
0.26
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
-
NM
NM
mg/L
11/27/18
0.26
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
mg/L
04/02/19
0.26
--
NM
--
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.26
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
GOLDER

February 2020 Page 2 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
LaotloAad
mg/L
04/28/06
0.1
--
NO
NM
-
NM
NM
NM
ND
NO
-
NO
ND -
-
NO
ND
NO
NO
0.121
ND
ND
-
NM
--
mg/L
10/09/06
--
--
NO
NM
--
NM
NM
NM
NO
0.14
-
0.12
0.11 -
-
0.2
0.17
0.11
0.16
0.14
0.18
0.13
-
NM
--
mg/L
04/24/07
--
--
--
NM
--
NM
NM
NM
--
--
-
-
-- -
--
-
-
--
-
-
-
-
-
NM
--
mg/L
10131/07
0.092
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/21/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10,06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
--
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.44
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
ND
NO
NO
NO
NO
ND
--
NM
NO
mg/L
10/10/11
0.062
--
0.15
NM
--
NM
NM
NM
NO
NO
-
4.7
NO -
-
0.62
ND
0.18
1.6
-
2.7
Dry
--
NM
NO
mg/L
04/17/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
09/30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/16/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10115/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
101 7/15
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
0411/16
-
--
0.15
NM
--
NM
NM
NM
ND
1.70
-
ND
2.8 -
--
ND
2.9
ND
ND
ND
ND
ND
--
NM
ND
mg/L
11/30/16
0.095
--
NO
NM
--
NM
NM
NM
NO
3.10
-
NO
NO -
-
NO
3.10
NO
3.0
1.3
15.0
NO
--
NM
NO
mg/L
04,11"7
0.095
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.095
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
O6I20Ma
0.095
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
11/27/18
0.095
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
mg/L
04/02/19
0.095
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM -
--
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.095
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
Pentanoic Acid
mg/L
04/28/06
0.07
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
NO
NO
NO
--
NM
mg/L
10I09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
0.16
--
NM
--
mg/L
04/24/07
--
--
--
NM
--
NM
NM
NM
--
--
-
-
-- --
--
-
-
--
-
-
-
-
--
NM
mg/L
10/31/07
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/21/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.27
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
ND
ND
NO
NO
NO
NO
--
NM
NO
mg/L
10/10/11
0.048
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
0.59
NO
NO
--
NO
Dry
--
NM
NO
mg/L
04/17/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04115/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NMNM
NM
NM
NM
Dry
--
NM
NM
mg/L
09I30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04116/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10115/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
1 017/15
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/11/16
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
ND --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
11/30/16
0.11
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04111/17
0.11
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.11
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
-
NM
NM
mg/L
06/20M8
0.11
--
NM
NM
--
NM
NM
NM
NM
NM
--
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg
27 8
0.11NIVI--
--
NM
NM
NM --
--
NM
NM
NM
NM
NM
NM
--
NM
NM
NM
mg/L
04/02/19
0.11
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.11
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
i-Pentanoic Acid
mg/L
04/28/06
0.07
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
NO
NO
NO
-
NM
--
mg/L
10I09/06
--
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
NO
NO
0.16
-
NM
--
mg/L
04/24/07
--
--
--
NM
--
NM
NM
NM
--
--
-
-
-- -
-
-
-
--
-
-
-
-
--
NM
mg/L
10/31/07
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/21/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0,26
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
ND
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/10/11
0.062
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
ND
NO
NO
-
NO
Dry
--
NM
NO
mg/L
04/17/12
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04115/13
--
--
NM
NM
--
NM
NM
NM
NM
NM-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
09I30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM-
NM
NM-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
0416/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10;15/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/07/15
--
--
NM
NM
--
NM
NM
NM
NM
NM
--
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/11/16
--
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
2.1
--
NM
NO
mg/L
11/30/16
0.18
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04111/17
0.18
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12/17
0.18
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
06/20M8
0.18
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
11/27/18
0.18
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM -
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
mg/L
04/02/19
0.18
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM-
-
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.18
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
GOLDER

February 2020 Page 3 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Propionic Acid
mg/L
04/28/06
0.07
--
NO
NM
--
NM
NM
NM
NO
0.212
-
NO
NO
-
-
NO
ND
NO
NO
NO
ND
ND
-
NM
--
mg/L
10/09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
-
-
NO
NO
NO
NO
NO
ND
NO
-
NM
--
mg/L
04/24/07
-
--
--
NM
--
NM
NM
NM
--
--
-
-
--
-
-
-
-
--
-
-
-
-
-
NM
--
mg/L
10/31/07
0.057
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
-
-
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/21/08
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
--
--
NM
NM
--
NM
NM
NM
NM
NM
--
NM
NM
--
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10115/09
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/26/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/19/10
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/18/11
0.18
--
ND
NM
--
NM
NM
NM
ND
7.1
-
1.7
8.5
-
--
NO
4.6
ND
NO
NO
21
NO
--
NM
ND
mg/L
10/10/11
0.057
--
0.22
NM
--
NM
NM
NM
0.22
5.6
-
1.8
2.5
-
--
NO
5.7
ND
1.3
-
23
Dry
--
NM
ND
mg/L
04/17/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10/09/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
09/30/13
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04116/14
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10115/14
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg
04/15/15
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
101 7/15
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
--
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
0411/16
-
--
NO
NM
--
NM
NM
NM
ND
7.2
-
5.9
9.0
-
--
NO
3.4
NO
5.8
3.5
28.0
NO
--
NM
NO
mg/L
11/30/16
0.065
--
NO
NM
--
NM
NM
NM
NO
13.0
-
5.7
NO
-
-
NO
3.0
NO
4.9
0.12
17.0
NO
--
NM
NO
mg/L
04,11"7
0.065
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12/12'17
0.065
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
06I20M8
0.065
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
-
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
11/27/18
0.065
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM
--
--
NM
NM
NM
NM
NM
NM
--
NM
NM
NM
mg/L
04/02/19
0.065
--
NM
-
NM
NM
NM
NM
NM
--
NM
NM
NM
-
--
NM
NM
NM
NM
NM
NM
-
NM
NM
NM
m /L
11/19/19
0.065
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
Sulfide
mg/L
04/28/06
1
--
ND
NM
--
NM
NM
NM
ND
ND
-
NO
ND
-
--
NO
NO
ND
NO
NO
NO
NO
--
NM
--
NC 2L= 1.0 mg/L
mg/L
10I09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
-
--
NO
NO
NO
NO
NO
NO
NO
--
NM
--
No EPA MCL
mg/L
0%4/07
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
-
--
NO
NO
NO
1.64
NO
NO
3.57
--
NM
--
mg/L
10/31/07
0.45
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
NO
-
--
NO
NO
NO
NO
NO
1.7
NO
--
NM
NO
mg/L
04/21/08
0.1
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
-
--
ND
NO
NO
0.87
J
NO
NO
NM
--
NM
NO
mg/L
10/06/08
0.02
--
NO
NM
--
NM
NM
NM
ND
0.07
J -
0.03
J
NO
-
--
ND
ND
ND
0.70
J
0.28
J
0.04
J 2.3
--
NM
NO
mg/L
04/13/09
0.031
--
NO
NM
--
NM
NM
NM
ND
NO
-
NO
NO
-
--
NO
NO
NO
ND
NO
NO
NO
--
NM
NO
mg/L
10/15/09
0.031
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO
--
--
ND
ND
ND
ND
NO
NO
NO
--
NM
NO
mg/L
04/26/10
0.031
--
NO
NM
--
NM
NM
NM
ND
NO
-
0.068
J
NO
-
--
NO
NO
NO
0.63
J
0.24
J
0.14
J 3.4
--
NM
NO
mg/L
10/19/10
0.010
--
0.017 J
NM
--
NM
NM
NM
0.029
J 0.020
J -
0.083
J
NO
-
--
NO
NO
NO
0.55
J
0.33
J
0.092
J 1.2
--
NM
NO
mg/L
04118/11
0.010
--
NO
NM
--
NM
NM
NM
NO
NO
-
0.021
J
NO
-
--
NO
NO
NO
0.42
J
NO
0.024
J 0.28
J
--
NM
NO
mg/L
10I10/11
0.010
--
NO
NM
--
NM
NM
NM
NO
0.067
J -
0.021
J
NO
-
--
NO
NO
NO
0.16
J
0.12
J
0.1
J Dry
--
NM
NO
mg/L
04/17/12
0.01
--
NO
NM
--
NM
NM
NM
ND
NO
--
NO
NO
--
--
NO
NO
NO
0.029
J
0.019
J
0.045
J Dry
--
NM
NO
mg/L
10/09/12
1
--
NO
NM
--
NM
NM
NM
ND
0.056
J --
0.02
J
NO
--
--
NO
NO
NO
0.046
J
0.076
J
0.1
J Dry
--
NM
NO
mg/L
04/15/13
1
--
NO
NM
--
NM
NM
NM
NO
NO
-
0.032
J
NO
-
--
NO
NO
NO
0.25
J
0.2
J
0.1
J Dry
--
NM
NO
mg/L
09/30/13
1
--
NO
NM
--
NM
NM
NM
NO
NO
--
0.039
J
NO
--
--
NO
NO
NO
0.062
J
0.03
J
0.18
J Dry
--
NM
NO
mg/L
04116/14
1
--
NO
NM
--
NM
NM
NM
NO
4.4
-
0.032
J
NO
-
--
NO
NO
NO
0.14
J
NO
0.19
J NM
--
NM
NO
mg/L
10/15/14
0.01
--
Dry
NM
--
NM
NM
NM
NO
0.026
J -
0.067
J
0.08
J -
--
NO
NO
NO
0.058
J
0.24
J
0.23
J Dry
--
NM
NO
mg/L
04/15/15
0.01
1
NO
NM
--
NM
NM
NM
NO
0.012
J --
NO
0.05
J --
--
NO
NO
NO
0.17
J
0.23
J
0.11
J Dry
--
NM
NM
mg/L
10/07/15
0.01
1
ND
NM
--
NM
NM
NM
ND
ND
--
0.07
J
0.03
J --
--
NO
NO
ND
0.084
J
0.37
J
0.14
J 0.48
J
--
NM
ND
mg/L
04/11/16
0.01
1
ND
NM
--
NM
NM
NM
ND
0.02
J --
0.04
J
0.29
J --
--
NO
NO
ND
0.11
J
0.10
J
0.11
J 1.30
--
NM
ND
mg/L
11/30/16
0.01
1
ND
NM
--
NM
NM
NM
ND
ND
-
NO
ND
-
--
NO
NO
ND
0.04
J
0.052
J
0.12
J 2.6
--
NM
ND
mg/L
04/11/17
0.01
1
ND
NM
--
NM
NM
NM
ND
0.019
J -
NO
0.035
J -
--
NO
NO
ND
0.089
J
0.082
J
0.077
J 1.0
--
NM
ND
mg/L
12/12/17
0.01
1
ND
NM
--
NM
NM
NM
ND
0.09
J -
0.05
J
0.02
J -
--
NO
NO
ND
0.110
J
0.130
J
0.27
J 0.66
J
-
NM
ND
mg/L
06I20M8
0.01
1
ND
--
ND
0.038 J
NO
ND
ND
--
NO
0.05
J
ND
-
-
NO
NO
ND
0.13
J
NO
0.27
J -
NO
NM
ND
mg
11/27/18
0.01
--
NO
--
NM
0.017 J
NM
NM
NO
--
0.043
J 0.06
J
NO
-
-
NO
NO
NO
0.097
J
0.320
0.140
-
NO
NM
NO
mg/L
04/02/19
0.01
--
--
--
--
0.15
-
--
NO
--
0.11
0.046
J
NO
-
-
NO
NO
NO
0.065
J
0.057
J
0.17
-
0.021 J
NM
NO
m /L
11/19/19
0.01
--
NO
--
--
0.036
NM
--
ND
--
0.061
J 0.036
J
--
-
-
NO
NO
NO
0.097
J
0.079
J
0.17
-
0.37
NM
NO
Chloride
mg/L
04/28/06
--
--
18
NM
--
NM
NM
NM
20
34
-
9
31
-
-
17
79
19
4
7
189
3
-
NM
--
NC2L=250 mg/L
mg/L
10/09/06
--
--
12
NM
--
NM
NM
NM
24
11
-
9
27
-
-
14
70
15
2
2
108
2
-
NM
--
EPA MCL = 250 mg/L
mg/L
04/24/07
--
--
39
NM
--
NM
NM
NM
14
32
-
101
20
-
-
5
48
28
NO
3
101
2
--
NM
--
mg/L
10/31/07
2
--
NO
NM
--
NM
NM
NM
8.8
42
-
7.3
23
-
--
NO
57
NO
2.5
12
110
NO
--
NM
NO
mg/L
04/21/08
0.48
--
3.5 B
NM
--
NM
NM
NM
9.4
B 31
-
12
20
--
--
4.2
B
61
4.0
B
3.1
B
4.6
B
140
NM
--
NM
2.0 J
mg/L
10/06/08
0.5
--
1.5 J
NM
--
NM
NM
NM
11.0
34
-
14
30
-
--
2.2
J
48
2.4
J
2.6
J
9.1
110
1.9
J
--
NM
NO
mg/L
04/13/09
0.018
--
3.2 J
NM
--
NM
NM
NM
11
43
-
15
30
-
--
3.8
J
48
4.5
J
2.4
J
4.1
J
110
5.8
--
NM
NO
mg/L
10/15/09
0.018
--
3.7 J
NM
--
NM
NM
NM
16
35
-
12
24
-
--
8.5
52
5.0
6.4
11
98
3.9
J
-
NM
NO
mg/L
04/26/10
0.018
--
3.1 B
NM
--
NM
NM
NM
9.4
B 30
-
19
17
-
--
3.8
B
44
4.6
B
5.0
B
5.0
B
110
4.7
B
-
NM
2.0 J
mg/L
10/19/10
0.018
--
3.0 B
NM
--
NM
NM
NM
9.4
36
-
16
15
-
--
3.4
B
52
4.8
B
5.1
B
5.0
B
98
3.5
B
-
NM
1.8 J
mg/L
04/1 8/1 1
0.047
--
3.2 B
NM
--
NM
NM
NM
8.7
B 29
-
17
38
-
--
3.4
B
50
4.8
B
5.5
B
8.4
B
110
3.3
B
-
NM
1.9 J
mg/L
10/10/11
0.047
--
3.4 B
NM
--
NM
NM
NM
13
25
-
18
20
--
--
10
63
4.6
B
10
11
110
Dry
--
NM
1.5 J
mg/L
04/17/12
0.43
--
3 J
NM
--
NM
NM
NM
11
19
-
23
31
--
--
10
77
4
J
11
7.6
110
Dry
--
NM
NO
mg
10/09/12
0.43
--
3.3 B
NM
--
NM
NM
NM
2.5
B 17
-
22
23
--
--
11
73
3.8
B
13
4.7
B
120
Dry
--
NM
1.5 J
mg/L
04/15/13
0.043
--
3.3 B
NM
--
NM
NM
NM
7.4
B 17
--
18
34
--
--
3.0
B
72
3.6
B
11
5.6
B
110
Dry
--
NM
1.5
mg/L
09/30/13
0.044
--
3.0 J
NM
--
NM
NM
NM
6.8
24
-
17
47
-
-
4.0
J
36
4.1
J
14
5.6
100
Dry
--
NM
NO
mg/L
04/16/14
2.2
--
2.8 J
NM
--
NM
NM
NM
2.5
J 11
-
16
34
-
-
2.6
J
34
3.1
J
14
5.1
99
NM
--
NM
NO
mg/L
10/15/14
2.2
--
Dry
NM
--
NM
NM
NM
7.7
38
-
19
60
-
-
4.8
J
34
5.3
28
9.2
84
Dry
--
NM
NO
mg/L
04/15/15
2.2
-
3.1 J
NM
--
NM
NM
NM
18
35
-
22
54
-
-
5.6
44
4.6
J
15
3.8
J
99
Dry
--
NM
NM
mg/L
101 7/1 5
2.2
-
2.6 J
NM
--
NM
NM
NM
5.1
36
-
31
21
-
-
3.4
J
42
4.5
J
24
8.4
99
2.9
J
--
NM
NO
mg/L
04/11/16
2.2
250
NO
NM
--
NM
NM
NM
20
28
-
34
61
-
-
NO
25
3.6
J
14
3.3
J
84
2.4
J
--
NM
NO
mg/L
11/30/16
2.2
250
NO
NM
--
NM
NM
NM
20
48
-
39
27
-
-
NO
31
3.6
J
22
8.8
79
2.2
J
--
NM
NO
mg/L
04/11/17
2.2
250
NO
NM
--
NM
NM
NM
12
41
-
42
43
-
-
NO
40
3.7
J
16
2.9
J
95
ND
--
NM
NO
mg/L
12/12/17
2.2
250
2.2 J
NM
--
NM
NM
NM
17
38
-
47
31
-
-
9.9
54
4.1
J
20
14
92
NO
-
NM
NO
mg/L
06I20M8
2.2
250
ND
--
22
NM
4.8 J
17
14
--
28
44
34
-
-
NO
63
2.8
J
15
7.1
110
-
3.1 J
NM
NO
mg/L
11/27/18
2.2
-
NO
--
23
3.90 J
5.2
16
15
--
32
42
20
--
--
NO
30
2.7
J
16
6.3
120
--
NO
NM
NO
mg/L
04/02/19
2.2
--
--
--
23
3.5 J
7.8
20
15
--
40
39
20
--
--
NO
29
38
J
13
5
94
--
ND
NM
NO
m /L
11/19/19
2.2
NO
21
11 J
5.4
18
25
51
24
2.3 J
6.9
55
11
13
22
120
NO
NM
NO
GOLDER

February 2020 Page 4 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Parameter
Nitratas
Rep rting
U.
nit.
mg/L
Sample
04/28/O6
Method
Detection
Lim!
0.04
SwS
ad"A
--
0.48
NM
--
Active C&D Monitoring
NM
Wells
NM
NM
0.23
Active
ND
C&D
Monitoring
-
Wells
& MNA Performance
NO
Monitor!
2.73
ng
- -
2.97
0.59
Closed MSW
0.12
Monitoring Wells
ND
& MNA Performance
ND
Monitoring
ND
Wells
ND
-
Closed MSW
NM
--
NC 2L= 10 mg/L
mg
10/09/06
-
--
0.38
NM
--
NM
NM
NM
0.44
0.19
-
NO
2.06
- -
2.31
NO
0.09
NO
NO
0.13
NO
-
NM
--
EPA MCL = 10 mg/L
mg/L
04/24/07
-
--
0.07
NM
--
NM
NM
NM
0.34
0.14
--
ND
1.93
- --
3.47
NO
0.11
NO
NO
0.11
NO
-
NM
--
mg/L
10131/07
0.007
--
0.44 J
NM
--
NM
NM
NM
0.41
J 0.30
J
-
0.072
J
0.11
- --
4.50
J 0.110
J 0.15
J 0.2
J 0.072
J
0.063
J
0.073
J
--
NM
NO
mg/L
04/21/08
0.01
--
0.32 J
NM
--
NM
NM
NM
0.31
J 0.01
J
-
0.59
J
3.60
- -
3.60
J 2.00
J 0.11
J 0.084
J 0.043
J
0.063
J
NM
--
NM
NO
mg/L
10I06/08
0.01
--
0.25 J
NM
--
NM
NM
NM
0.088
J 0.072
J
--
0.11
J
14l)
-- -
2.40
J 0.096
J 0.079
J 0.13
J 0.076
J
0.081
J
0.3
J
--
NM
NO
mg/L
04/13/09
0.0056
--
0.27 J
NM
--
NM
NM
NM
0.56
J 0.097
J
--
0.10
J
4.10
- -
2.60
J 0.066
J 0.0949
J 0.12
J 0.12
J
0.13
J
0.12
J
--
NM
NO
mg/L
10/15/09
0.0056
--
0.48 J
NM
--
NM
NM
NM
0.17
J 0.051
J
--
0.13
J
0.095
- -
0.17
J 0.27
J NO
0.13
J 0.036
J
0.16
J
0.17
J
--
NM
NO
mg/L
04/26/10
0.0056
--
0.12 J
NM
--
NM
NM
NM
1.30
J 0.059
J
-
0.081
J
6.20
- -
2.00
J 0.13
J 0.12
J 0.095
J 0.10
J
0.057
J
0.13
J
--
NM
NO
mg/L
10/19/10
0.025
--
NO
NM
--
NM
NM
NM
NO
0.025
J
-
0.076
J
8.80
- -
2.20
J NO
0.11
J 0.050
J 0.061
J
0.049
J
0.17
J
--
NM
NO
mg/L
04/18/11
0.025
--
0.36 J
NM
--
NM
NM
NM
0.56
J 0.041
J
-
0.067
J
0.35
- -
2.80
J 1.40
J 0.12
J 0.085
J 0.17
J
0.083
J
0.091
J
--
NM
NO
mg/L
10/10/11
0.025
--
0.60 J
NM
--
NM
NM
NM
1.50
J 0.46
J
-
0.067
J
0.26
- -
0.58
J 3.70
J 0.18
J 0.034
J 0.062
J
0.14
J
Dry
--
NM
NO
mg/L
04/17/12
0.025
--
0.55 J
NM
--
NM
NM
NM
1.40
J 0.140
J
-
0.100
J
0.460
- -
0.28
J 3.10
J 0.11
J 0.088
J 0.120
J
0.110
J
Dry
--
NM
NO
mg/L
10I09/12
10
--
0.58 J
NM
--
NM
NM
NM
0.42
J NO
-
0.064
J
0.59
- -
0.18
J 4.00
J 0.048
J 0.067
J NO
0.059
J
Dry
--
NM
NO
mg/L
04/15/13
10
--
0.46 J
NM
--
NM
NM
NM
1.30
J 0.067
J
-
0.068
J
1.10
- -
1.70
J 6.60
J 0.028
J 0.094
J 0.12
J
1.40
J
Dry
--
NM
NO
mg/L
09/30/13
10
--
0.43 J
NM
--
NM
NM
NM
0.20
J 0.11
J
--
0.073
J
2.60
-- --
1.00
J 0.44
J NO
0.084
J 0.12
J
0.12
J
Dry
--
NM
NO
mg/L
04/16/14
10
-
0.18 J
NM
--
NM
NM
NM
0.25
J NO
-
NO
1.10
- -
0.19
J 0.17
J 0.063
J 0.068
J NO
0.055
J
NM
--
NM
NO
mg/L
10/15/14
0.025
10
Dry
NM
--
NM
NM
NM
0.87
J 2.40
J
--
0.12
J
0.22
-- --
0.96
J 0.58
J 0.39
J 1.10
J 0.094
J
0.11
J
Dry
--
NM
NO
mg/L
04/15/15
0.025
10
0.41 J
NM
--
NM
NM
NM
0.17
J 0.092
J
--
0.098
J
0.13
-- --
0.88
J 0.64
J 0.048
J 0.076
J 0.200
J
0.29
J
Dry
--
NM
NM
mg/L
10/07/15
0.025
10
0.35 J
NM
--
NM
NM
NM
5.30
J 0.079
J
--
0.092
J
0.72
-- --
1.60
J 1.10
J 0.41
J 0.073
J 0.100
J
0.43
J
0.098
J
--
NM
NO
mg/L
04/11/16
0.025
10
0.19 J
NM
--
NM
NM
NM
3.00
J 0.047
J
-
0.049
J
0.150
- -
0.46
J NO
NO
0.059
J 0.076
J
0.054
J
0.079
J
--
NM
NO
mg/L
11/30/16
0.025
10
0.26 J
NM
--
NM
NM
NM
0.73
J ND
-
0.071
J
2.20
- -
1.10
J 0.11
J NO
0.076
J 0.067
J
0.081
J
0.12
J
--
NM
NO
mg/L
04/11/17
0.025
10
0.24 J
NM
--
NM
NM
NM
6.20
J 0.086
J
-
0.100
J
14.0
- -
0.90
J 0.18
J NO
0.077
J 0.160
J
0.140
J
0.18
J
-
NM
NO
mg
12/12/17
0.025
10
0.55 J
NM
--
NM
NM
NM
2.60
J 0.140
J
-
0.130
J
0.280
- -
0.65
J 1.10
J NO
0.140
J 0.140
J
0.120
J
0.160
J
-
NM
NO
mg/L
06/20/18
0.025
10
0.45 J
-
NM
NM
NM
NM
0.81
J --
0.09
J
0.12
J
6.0
- -
0.84
J 1.7
J ND
0.14
J 0.11
J
0.17
J
-
0.14 J
NM
NO
mg/L
11/27/18
0.025
--
0.410
-
NM
NM
NM
NM
3.3
--
0.18
0.17
4.4
- -
1.2
0.05
J NO
0.13
J 0.200
0.200
-
0.240
NM
NO
m /L
11/19/19
0.041
--
0.420
--
NM
NM
NM
--
1.3
--
0.086
J
0.067
J
--
0.30 NM
0.51
0.88
NO
0.067
J 0.067
J
0.100
-
0.065 J
NM
ND
Nitrite as N
mg/L
04/28/06
-
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
- -
NM
NM
NM
NM
NM
NM
NM
-
NM
--
No Standard
mg/L
10/09/06
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
- -
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/24/07
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM
- -
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/31/07
0.006
--
0.014 B
NM
--
NM
NM
NM
0.009
B NO
-
NO
NO
- -
0.016
B NO
NO
0.21
J NO
NO
0.011
B
--
NM
0.016 J
mg/L
04/21/08
0.01
--
NO
NM
--
NM
NM
NM
NO
0.013
B
-
NO
NO
- -
NO
NO
NO
NO
NO
NO
NM
--
NM
0.013 J
mg/L
10/06/08
0.017
--
NO
NM
--
NM
NM
NM
NO
0.072
J
-
NO
NO
- -
NO
NO
0.012
J NO
NO
NO
NO
--
NM
NO
mg/L
04/13/09
0.0056
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
- -
NO
NO
NO
NO
NO
NO
0.014
J
--
NM
NO
mg/L
10/15/09
0.0056
--
0.016 B
NM
--
NM
NM
NM
0.022
B 0.020
B
-
0.0087
B
0.015
- -
0.023
B 0.016
B 0.016
B 0.014
B 0.014
B
0.0099
B
0.0088
B
--
NM
0.013 J
mg
0 26 0
0.0056
--
NO
NM--
NM
NM
NM
NO
NO
--
NO
NO
-- --
0.0085
B NO
NO
NO
NO
NO
NO
--
NM
0.0081 J
mg/L
10/19/10
0.0056
--
0.0067 B
NM
--
NM
NM
NM
0.033
J 0.016
B
-
0.0061
B
0.019
- -
0.0094
B 0.016
B 0.011
B 0.006
B 0.008
B
0.0071
B
0.012
B
--
NM
0.0064 J
mg/L
04/18/11
0.003
--
0.0084 B
NM
--
NM
NM
NM
NO
0.006
B
-
NO
NO
- -
0.0061
B 0.0068
B 0.0056
B NO
NO
NO
0.0048
B
--
NM
0.0042 J
mg/L
10/10/11
0.003
--
0.012 B
NM
--
NM
NM
NM
0.011
B NO
-
NO
0.0036
- -
0.016
B 0.0084
B NO
0.0095
B NO
NO
Dry
--
NM
0.0041 J
mg/L
04117/12
0.003
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
0.010
- -
NO
0.016
J 0.0098
J NO
0.0042
J
NO
Dry
--
NM
NO
mg,
10/09/12
1
--
NO
NM
--
NM
NM
NM
0.0047
B NO
-
NO
0.003
- -
0.0077
B 0.0039
B NO
NO
0.0043
B
NO
Dry
--
NM
0.0063 J
mg/L
04/15/13
1
--
0.0092 B
NM
--
NM
NM
NM
0.019
B NO
-
0.012
B
NO
-- --
0.012
B 0.034
B NO
0.026
B 0.011
B
0.021
B
Dry
--
NM
0.0079 J
mg/L
09/30/13
1
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO
-- --
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg
0 6
--
NM
NM
NM
NO
NO
--
NO
NO
-- --
0.019
J NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
10/15/14
0.017
1
Dry
NM
--
NM
NM
NM
NO
NO
--
NO
NO
-- --
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
04/15/15
0.017
1
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO
- -
NO
NO
NO
NO
NO
NO
Dry
--
NM
NM
mg/L
10I07/15
0.017
1
NO
NM
--
NM
NM
NM
NO
NO
--
NO
0.03
-- --
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/11/16
0.017
1
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO
-- --
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
11/30/16
0.017
1
NO
NM
--
NM
NM
NM
NO
NO
--
NO
0.03
-- --
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg,
04/11/17
0.017
1
NO
NM
--
NM
NM
NM
NO
NO
--
0.019
J
0.03
-- --
NO
NO
NO
0.033
J NO
NO
NO
--
NM
NO
mg/L
12/12/17
0.017
1
NO
NM
--
NM
NM
NM
0.034
J NO
-
NO
NO
- -
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
06/20/18
0.017
1
NO
-
NM
NM
NM
NM
NO
--
NO
NO
NO
- -
NO
NO
NO
NO
NO
NO
-
NO
NM
NO
mg/L
11/27/18
0.017
--
NO
-
NM
NM
NM
NM
NO
--
NO
NO
NO
- -
NO
NO
NO
0.017
J NO
NO
-
NO
NM
NO
mg/L
04/02/19
0.017
--
--
-
NM
NM
NM
--
0.082
J --
NO
0.027
J
NO
- -
ND
ND
NO
0.098
J NO
NO
-
NO
NM
0.017
m /L
11/19/19
0.017
NO
NM
NM
NM
NO
0.038
J
0.018
J
0.035 J NM
NO
NO
NO
NO
0.028
J
0.035
J
NO
NM
NO
Total Dissolved Solids
mg/L
04/02/19
50
--
--
-
260
NO
74
350
280
--
970
270
220
- -
--
-
--
-
-
-
-
--
--
NO
m /L
11/19/19
50
--
NO
-
220
110
NO
--
290
--
590
350
--
400 220
-
-
--
-
-
-
-
--
--
NO
Sulfate
mg/L
04/28/06
5
--
NO
NM
--
NM
NM
NM
NO
63.4
-
27.2
23.5
- -
24.5
9
NO
16.3
19
8.2
38.4
--
NM
--
NC2L=250 mg/L
mg/L
10/09/06
-
--
10.7
NM
--
NM
NM
NM
14.9
88.2
-
32.5
18.5
- -
23
24.6
5.9
20.8
7
18.1
35.4
--
NM
--
No EPA MCL
mg/L
04/24/07
-
--
7.9
NM
--
NM
NM
NM
10.4
76
-
28.3
25.2
- -
17
26.2
8.7
20.8
17.2
15.1
13.7
--
NM
--
mg/L
10/31/07
0.03
--
1.0 J
NM
--
NM
NM
NM
13
J 130
J
-
25
J
160
- -
7.2
J 17
J 2.0
J 13
J 3.0
J
8.2
J
26
J
--
NM
NO
mg/L
04/21/08
0.25
--
1.0 J
NM
--
NM
NM
NM
9.0
93
J
-
27
J
82
- -
13
J 20
J 3.8
J 12
J 6.7
J
9.4
J
NM
--
NM
NO
mg/L
10/06/08
0.05
--
2.4 J
NM
--
NM
NM
NM
11.0
J 66
J
-
24
J
130
- -
12
J 17
J 5.0
J 17
J 3.6
J
6.1
J
43
J
--
NM
NO
mg/L
04/13/09
0.16
--
2.2 J
NM
--
NM
NM
NM
13
J 88
J
-
22
J
160
- -
12
J 17
J 5.2
J 18
J 2.4
J
6.2
J
54
J
--
NM
NO
mg/L
10/15/09
0.16
--
2.1 J
NM
--
NM
NM
NM
26
J 120
J
-
26
J
120
- -
12
J 20
J 5.5
J 18
J 6.1
J
4.7
J
33
J
--
NM
NO
mg/L
04/26/10
0.16
--
2.3 J
NM
--
NM
NM
NM
21
J 77
J
-
26
J
40
- -
12
J 13
J 6.1
J 14
J 2.6
J
4.7
J
20
J
--
NM
NO
mg/L
10/19/10
0.12
--
2.8 J
NM
--
NM
NM
NM
16
J 100
J
-
22
J
66
- -
11
J 16
J 6.2
J 18
J 3.1
J
6.4
J
24
J
--
NM
NO
mg/L
04118/11
0.02
--
2.6 B
NM
--
NM
NM
NM
19
J 96
J
-
21
J
190
- -
11
J 15
J 6.7
B 19
J 4.8
B
6.7
B
37
J
--
NM
1.8 J
mg/L
10/10/11
0.02
--
1.9 J
NM
--
NM
NM
NM
39
J 58
J
-
20
J
99
- -
9.7
J 18
J 6.7
J 14
J 3.8
J
4.9
J
Dry
--
NM
NO
mg/L
04/17/12
0.04
--
1.6 B
NM
--
NM
NM
NM
21
J 46
J
--
19
J
120
-- --
9.8
J 20
J 7.2
J 11
J 2.5
B
4.8
B
Dry
--
NM
1.7 J
mg/L
1019/12
250
--
1.9 J
NM
--
NM
NM
NM
4.5
J 24
J
-
15
J
63
- -
9.6
J 17
J 7.1
J 12
J 2.8
J
5.3
J
Dry
--
NM
NO
mg/L
04/15/13
250
--
1.8 J
NM
--
NM
NM
NM
7.4
J 48
J
-
15
J
150
- -
10
J 12
J 7.1
J 8.2
J 2.4
J
7
J
Dry
--
NM
NO
mg,
09/35/13
250
--
NO
NM
--
NM
NM
NM
13
J 21
J
-
17
J
140
- -
11
J 8.0
J 5.9
J 7.2
J NO
4.5
J
Dry
--
NM
NO
mg/L
04/16/14
250
--
NO
NM
--
NM
NM
NM
4.9
J 94
J
-
19
J
92
- -
10
J 8.0
J 4.9
J 12
J 5.0
J
3.6
J
NM
--
NM
NO
mg/L
10115/14
2.9
250
Dry
NM
--
NM
NM
NM
10
J 64
J
-
17
J
210
- -
10
J 8.9
J 6.5
J 11
J NO
4.6
J
Dry
--
NM
NO
mg
04/15/15
2.9
250
NO
NM
--
NM
NM
NM
34
J 72
J
-
19
J
190
- -
13
J 12
J 8.0
J 11
J NO
6.6
J
Dry
--
NM
NM
mg,
10/07/15
2.9
250
NO
NM
--
NM
NM
NM
7.3
J 49
J
-
18
J
48
- -
8.7
J 14
J 6.9
J 15
J NO
5.8
J
21
J
--
NM
NO
mg/L
04/11/16
2.9
250
3.2 J
NM
--
NM
NM
NM
37
J 58
J
-
17
J
180
- -
11
J 8.0
J 8.3
J 17
J NO
3.6
J
10
J
--
NM
NO
mg/L
11/30/16
2.9
250
NO
NM
--
NM
NM
NM
25
J 84
J
-
14
J
52
- -
8.9
J 9.2
J 8.2
J 11
J NO
3.7
J
24
J
--
NM
NO
mg/L
04/11/17
2.9
250
NO
NM
--
NM
NM
NM
24
J 61
J
-
14
J
98
- -
9.3
J 10.0
J 8.7
J 14
J NO
3.5
J
NO
--
NM
ND
mg/L
12/12/17
2.9
250
NO
NM
--
NM
NM
NM
31
J 33
J
-
11
J
38
- -
10
J 16
J 10
J 8.9
J NO
NO
18
J
--
NM
NO
mg/L
06/20/18
2.9
250
NO
--
19
J NO
NO
44 J
23
J --
3.5
J
9.8
J
22
- -
8.6
J 13
J 9.1
J 7.3
J NO
NO
-
31 J
NM
NO
mg/L
11/27/111
2.9
--
NO
--
20
NO
6.3
43
26
--
4.3
J
8.1
29
- -
7.6
5.2
7.6
9.2
NO
NO
-
11
NM
NO
mg/L
04/02"9
2.9
--
NO
--
18
NO
3.6 J
94
24
--
67
9.2
61
- -
8.2
4.5
J 7.9
16
NO
NO
-
8.7
NM
NO
m /L
11/19/19
2.9
NO
15
NO
NO
26
3.3
J
10
140 48
11
7.7
9.2
13
NO
NO
9.9
NM
NO
GOLDER

February 2020 Page 5 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Parameter
Alkalinity (total)
Rep rting
U.
nit.
mg/L
Sample
04/28/O6
Method
Detection
Lim!
SwS
Id"A
--
2
NM
Active
--
C&D Monitoring
NM
Wells
NM
NM
2
Active
566
C&D Monitoring
-
Wells & MNA Performance
158
Monitor! ngW
I
1 -
-
Closed
258
MSW
2
Monitoring
Wells &
156
MNA Performance
156
Monitoring Wells
878
93
-
Closed MSW
NM
No Standard
mg/L
10/09/06
--
--
1
NM
--
NM
NM
NM
5
729
-
179
1.5 -
-
6
244
NO
20.3
168
946
115
-
NM
--
mg/L
04/24/07
--
--
NO
NM
--
NM
NM
NM
3
650
--
164
7 -
--
NO
267
2
173
194
879
107
-
NM
--
mg/L
10/31/07
5.2
--
NO
NM
--
NM
NM
NM
15
390
--
130
71 -
--
NO
240
NO
160
89
690
130
--
NM
NO
mg/L
04/21/08
4.7
--
NO
NM
--
NM
NM
NM
7.8 J
280
--
110
77 -
--
NO
170
8.5
J
110
81
740
NM
--
NM
NO
mg/L
10/06/08
2.7
--
NO
NM
--
NM
NM
NM
4.5 J
190
--
94
74 --
--
NO
140
NO
88
28
680
82
--
NM
NO
mg/L
04113/09
8.3
--
NO
NM
--
NM
NM
NM
9.9 J
370
-
72
190 --
-
NO
180
NO
88
120
670
81
--
NM
NO
mg/L
10/15/09
8.3
--
9.9 J
NM
--
NM
NM
NM
53
390
-
160
260 --
--
80
210
NO
160
53
680
160
--
NM
NO
mg/L
04/26/10
8.3
--
NO
NM
--
NM
NM
NM
14 J
350
--
150
88 --
--
NO
160
NO
88
130
660
110
--
NM
NO
mg/L
10/19/10
8.0
--
NO
NM
--
NM
NM
NM
9.8 J
760
-
170
170 -
--
NO
260
NO
150
130
890
170
--
NM
NO
mg/L
04/18/11
12
--
NO
NM
--
NM
NM
NM
NO
600
-
120
320 -
--
NO
290
NO
70
79
910
64
--
NM
NO
mg/L
10/10/11
12
--
NO
NM
--
NM
NM
NM
22
360
-
96
280 -
--
110
280
NO
130
49
930
Dry
--
NM
NO
mg/L
04/17/12
12
--
NO
NM
--
NM
NM
NM
NO
350
-
120
260 -
--
83
330
NO
170
100
1100
Dry
--
NM
NO
mg/L
10/09/12
12
--
NO
NM
--
NM
NM
NM
NO
330
-
85
200 -
--
55
340
NO
81
160
930
Dry
--
NM
NO
mg/L
04/15/13
12
--
NO
NM
--
NM
NM
NM
NO
300
-
140
250 -
--
NO
270
NO
23
170
750
Dry
--
NM
NO
mg/L
09/30/13
14
--
NO
NM
--
NM
NM
NM
NO
310
-
160
310 -
--
NO
190
NO
66
140
990
Dry
--
NM
NO
mg/L
04/16/14
14
--
NO
NM
--
NM
NM
NM
NO
260
-
83
210 -
--
NO
130
NO
110
120
820
NM
--
NM
NO
mg/L
10/15/14
14
--
Dry
NM
--
NM
NM
NM
17
550
-
120
820 -
-
15
180
ND
150
88
770
Dry
--
NM
ND
mg/L
04/15/15
14
--
ND
NM
--
NM
NM
NM
120
640
-
130
710 -
-
NO
190
ND
120
96
970
Dry
--
NM
NM
mg,
10/07/15
14
--
ND
NM
--
NM
NM
NM
18
640
-
180
310 -
-
ND
250
14
J
180
130
970
100
--
NM
ND
mg/L
04/11/16
14
--
ND
NM
--
NM
NM
NM
110
550
-
130
640 -
-
NO
170
ND
160
130
1000
100
--
NM
ND
mg/L
11/30/16
14
--
ND
NM
--
NM
NM
NM
82
710
-
170
260 -
-
ND
180
ND
180
160
880
160
--
NM
ND
mg/L
0.11/17
14
--
ND
NM
--
NM
NM
NM
34
810
-
150
470 -
-
ND
230
ND
200
110
920
110
--
NM
ND
mg/L
12/12/17
14
--
ND
NM
--
NM
NM
NM
82
630
-
170
350 -
-
49
290
ND
260
110
1000
130
--
NM
ND
mg/L
06120/18
14
--
ND
--
200
87
24
190
120
--
550
170
94 -
-
ND
310
ND
250
150
1100
-
85
NM
ND
mg/L
11/27/18
14
--
ND
--
160
81
33
170
140
--
610
130
41 -
-
NO
180
ND
240
160
890
-
90
NM
ND
mg/L
04/02/19
14
--
--
--
200
NO
59
140
110
--
750
120
20 -
-
NO
170
ND
NO
NO
710
-
40
NM
ND
m /L
11/19/19
14
ND
240
87
14
190
650
200
64
130
51
250
ND
260
120
970
97
NM
ND
Total Organic Carbon
mg/L
04/28/06
-
--
4.48
NM
--
NM
NM
NM
4.78
3.4
-
6.73
5.88 -
-
23.04
1.43
1.45
NO
NO
36
9.9
--
NM
No Standard
mg/L
1019106
-
--
NO
NM
--
NM
NM
NM
14.67
33.2
-
4.53
7.89 -
-
3.34
7.67
1.33
3.34
6.04
27.09
5.18
--
NM
--
mg/L
04/24/07
-
--
NO
NM
--
NM
NM
NM
8.78
27.78
-
4.41
6.31 -
-
1.63
7.65
1.05
6.63
1405
51.85
17.95
--
NM
--
mg/L
10/31/07
0.3
--
NO
NM
--
NM
NM
NM
13
50
-
4.2
18 -
-
5.4
10
0.47
24
8.8
50
5.9
--
NM
NO
mg/L
04/21/08
0.32
--
NO
NM
--
NM
NM
NM
5.2
27
-
3.9
13 -
-
1.2
8.1
0.62
J
11
15
46
NM
--
NM
NO
mg/L
10/06/08
0.32
--
ND
NM
--
NM
NM
NM
9.4
44
-
4.4
18 -
-
1.3
8.8
NO
10
26
34
11
--
NM
NO
mg/L
04/13/09
0.32
--
ND
NM
--
NM
NM
NM
9.8
41
-
6.2
41 -
-
1.2
10
0.51
J
13
84
41
16
--
NM
NO
mg/L
10/15/09
0.32
--
NO
NM
--
NM
NM
NM
16
32
-
4.6
26 -
-
8.4
8.7
0.54
J
4.2
26
37
4.4
--
NM
NO
mg/L
04/26/10
0.32
--
NO
NM
--
NM
NM
NM
15
29
-
5.9
11 -
-
1.2
9.1
0.54
J
11
23
40
21
--
NM
NO
mg/L
10119/10
0.32
--
NO
NM
--
NM
NM
NM
17
48
--
7.1
20 --
--
2.5
11
0.87
J
11
100
53
12
--
NM
NO
mg/L
04/18/11
0.28
--
NO
NM
--
NM
NM
NM
8.6
32
-
5.6
52 --
-
1.8
8.4
0.81
J
8.2
9.7
40
4.8
--
NM
ND
mg,
10/10/11
0.28
--
ND
NM
--
NM
NM
NM
15
20
-
5.3
23 -
-
8.0
8.8
0.62
5.3
-
44
Dry
--
NM
NO
mg/L
04/17/12
0.001
--
NO
NM
--
NM
NM
NM
8.0
13
-
5.3
26 -
-
5.3
9.5
0.64
J
8.9
90
59
Dry
--
NM
NO
mg/L
10/09/12
0.22
--
NO
NM
--
NM
NM
NM
9.2
17
--
7.7
20 --
-
6.8
11
0.62
J
6.5
84
57
Dry
--
NM
NO
mg/L
04/15/13
0.32
--
NO
NM
--
NM
NM
NM
9.8
13
--
5.2
40 --
-
2.8
8.5
NO
36
29
51
Dry
--
NM
NO
mg/L
09/30/13
0.32
--
NO
NM
--
NM
NM
NM
12
18
--
5.7
53 --
-
2.7
4.8
5.2
J
18
11
53
Dry
--
NM
NO
mg/L
04/16/14
0.32
--
NO
NM
--
NM
NM
NM
9.8
32
-
5.4
36 -
-
3.1
4.6
NO
35
44
41
NM
--
NM
NO
mg/L
10/15/14
0.32
--
Dry
NM
--
NM
NM
NM
12
33
-
7.1
51 -
-
4.2
6.4
0.97
J
21
7
51
Dry
--
NM
NO
mg/L
04/15/15
0.32
--
NO
NM
--
NM
NM
NM
29
40
-
5.2
79 --
--
1.4
6.1
NO
54
34
45
Dry
--
NM
NM
mg/L
10/07/15
0.32
--
NO
NM
--
NM
NM
NM
10
32
--
8.4
39 --
--
3.2
6.1
0.71
J
23
42
44
26
--
NM
NO
mg/L
04/11/16
0.32
--
NO
NM
--
NM
NM
NM
32
37
--
9.4
85 --
--
1.4
5.4
0.73
J
40
48
58
49
--
NM
NO
mg/L
11/30/16
0.32
--
NO
NM
--
NM
NM
NM
24
49
-
9.4
31 -
-
1.6
5.4
0.70
J
41
20
60
47
--
NM
NO
mg/L
04;11'17
0.32
--
NO
NM
--
NM
NM
NM
1.4
33
-
9.2
43 -
-
1.2
9.1
0.78
J
26
13
59
37
--
NM
NO
mg/L
12112/17
0.32
--
NO
NM
--
NM
NM
NM
22
32
--
13
27 --
--
5.2
8.7
9.2
15
7.1
40
14
--
NM
NO
mg/L
O6I20/18
0.34
--
NO
--
NM
NM
NM
NM
21
--
24
12
11 -
-
1.7
12
1.1
19
6.5
66
--
4.8
NM
NO
mg/L
11127/18
0.34
--
0.470 J
-
NM
NM
NM
NM
21
--
28
15
9.3 -
-
1.9
7.8
1.0
25
60
68
-
3.3
NM
NO
mg/L
04/02/19
0.34
--
--
-
NM
NM
NM
--
21
--
66
12
11 -
-
11
6.2
0.95
J
56
94
42
-
4.3
NM
NO
m /L
11/19/19
0.34
NO
NM
NM
NM
27
22
12
21
NM
4.3
8.8
1.1
13
8.5
45
18
NM
NO
Nitrate/Nitrite as N
mg/L
10119/10
0.025
--
NO
NM
--
NM
NM
NM
NO
0.04
J -
0.08
J
8.80 -
-
2.20
NO
0.12
0.06 J
0.08 J
0.06 J
0.19
--
NM
NO
No Standard
mg/L
04/18/11
0.025
--
0.37
NM
--
NM
NM
NM
0.56
0.05
J --
0.07
J
0.35 --
--
2.80
1.40
0.13
0.09 J
0.17
0.08 J
0.10 J
--
NM
NO
mg/L
10/10/11
0.025
--
0.61
NM
--
NM
NM
NM
1.50
0.46
--
0.07
0.26 -
-
0.60
3.70
0.18
0.04
0.06
0.14
Dry
--
NM
NO
mg/L
04/17/12
0.025
--
0.55
NM
--
NM
NM
NM
1.40
0.140
-
0.10
0.47 -
-
0.28
3.10
0.12
0.09 J
0.12
0.110
Dry
--
NM
NO
mg/L
10I09/12
0.025
--
0.58
NM
--
NM
NM
NM
0.42
ND
-
0.06
J
0.59 -
-
0.19
4.00
0.05
J
0.07 J
NO
0.06 J
Dry
--
NM
NO
mg/L
04I15/13
0.025
--
0.47
NM
--
NM
NM
NM
1.30
0.07
J --
0.08
J
1.10 --
--
1.70
6.60
0.03
J
0.12
0.13
1.40
Dry
--
NM
NO
mg/L
09/30/13
0.025
--
0.43
NM
--
NM
NM
NM
0.20
0.11
--
0.07
J
2.60 --
--
1.00
0.44
NO
0.08 J
0.12
0.12
Dry
--
NM
NO
mg/IL
04/16/14
0.082
--
0.18
NM
--
NM
NM
NM
0.25
NO
-
NO
1.10 -
-
0.21
0.17
0.06
J
0.07 J
NO
0.06 J
NM
--
NM
NO
mg/L
10/15/14
0.041
--
Dry
NM
--
NM
NM
NM
0.87
2.40
--
0.12
0.202 --
--
0.96
0.58
0.39
1.10
0.09 J
0.11
Dry
--
NM
NO
mg/L
04/15/15
0.041
--
0.41
NM
--
NM
NM
NM
0.17
0.09
J --
0.10
J
0.13 --
--
0.88
0.64
0.05
J
0.08 J
0.29
0.29
Dry
--
NM
NM
mg/L
10/07/15
0.041
--
0.35
NM
--
NM
NM
NM
5.30
0.08
J --
0.09
J
0.75 --
--
1.60
1.10
0.41
0.07 J
0.11
0.43
0.10 J
--
NM
NO
mg/L
04/11/16
0.041
--
0.19
NM
--
NM
NM
NM
3.00
0.05
J -
0.05
J
0.15 -
-
0.46
NO
NO
0.06 J
0.08 J
0.05 J
0.08 J
--
NM
NO
mg/L
11I30/i6
0.041
--
0.26
NM
--
NM
NM
NM
0.73
ND
-
0.07
J
2.20 --
--
1.10
0.11
ND
0.08 J
0.07 J
0.08 J
0.12
--
NM
ND
mg/L
04111/17
0.041
--
0.24
NM
--
NM
NM
NM
6.20
0.09
J --
0.12
14.0 --
--
0.95
0.18
ND
0.11
0.16
0.14
0.18
--
NM
ND
mg/L
12/12/17
0.041
--
0.55
NM
--
NM
NM
NM
2.60
0.14
--
0.13
0.28 --
--
0.60
1.10
ND
0.14
0.14
0.12
0.16
--
NM
ND
mg/L
O6/20/18
0.041
--
0.45
--
NM
NM
NM
NM
0.81
--
0.09
J 0.12
6.0 --
--
0.84
1.7
ND
0.14
0.11
0.17
--
0.14
NM
ND
mg/L
11/27/18
0.041
--
0.410
-
NM
NM
NM
NM
3.3
--
0.18
0.17
4.4 -
-
1.2
0.05 J
ND
0.150
0.200
0.200
-
0.24
NM
ND
mg/L
04/02/19
0.041
--
--
-
NM
-
-
--
7.6
--
0.11
0.11
3.6 -
-
1.0
0.048 J
ND
0.15
0.08 J
0.1
-
0.12
NM
ND
m /L
11/19/19
0.041
0.42
NM
NM
NM
1.3
0.086
J 0.085
J
0.33
NM
0.51
0.88
ND
0.067 J
0.067 J
0.1
0.065 J
NM
ND
GOLDER

February 2020 Page 6 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Parameter
Ethane
Rep rting
U.
nit.
mg/L
Sample
04/28/O6
Method
Detection
Lim!
0.001
SwS
Id"A
--
ND
NM
Active
--
C&D Monitoring
NM
Wells
NM
NM
ND
Active
ND
C&D Monitoring
-
Wells & MNA Performance
NO
Monitor! -
ng We"
NO -
-
ND
ND
Closed MSW Monitoring
ND
Wells
ND
& MNA Performance
ND
Monitoring Wells
ND
ND
-
Closed MSW
NM
No Standard
mg
10/09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
ND
NO
NO
NO
NO
NO
NO
-
NM
--
mg/L
04/24/07
-
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO -
--
ND
NO
NO
NO
NO
NO
NO
-
NM
--
mg/L
10/31/07
0.0002
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO -
--
ND
ND
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/21/08
0.0009
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO -
--
ND
NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
10I06/08
0.0009
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
ND
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04113/09
0.0009
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO --
--
ND
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/15/09
0.0009
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04,26/10
0.0009
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/19/10
0.0015
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg
0
0.00 5
--
N
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/10/1,
-
--
ND
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
-
NO
Dry
--
NM
NO
mg/L
04/17/12
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
-
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
10I09/12
--
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
04I15/13
--
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
09/30/13
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
04/16/14
-
--
ND
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
10/15/14
0.00047
--
NM
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
04/15/15
0.00047
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
Dry
--
NM
NM
mg/L
10I07/15
0.00047
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/11/16
0.00047
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
11/30/16
0.0013
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04111"7
0.0013
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
12/12'17
0.0013
--
ND
NM
--
NM
NM
NM
ND
ND
--
NO
ND --
--
NO
NO
ND
NO
NO
NO
NO
--
NM
ND
mg/L
O6I20/18
0.0013
--
ND
--
NM
NM
NM
NM
ND
--
NO
NO
ND --
--
NO
NO
ND
NO
NO
NO
--
ND
NM
ND
mg/L
11/27/18
0.0013
--
ND
--
NM
NM
NM
NM
ND
--
NO
NO
ND --
--
NO
NO
ND
NO
NO
NO
-
ND
NM
ND
mg/L
04/02/19
0.0013
--
ND
-
NM
NM
NM
--
ND
--
NO
NO
ND -
--
NO
NO
ND
NO
NO
NO
-
ND
NM
ND
m /L
11/19/19
0.0013
ND
NM
NM
NM
ND
NO
NO
NM
NO
NO
ND
NO
NO
NO
ND
NM
ND
Ethane
mg/L
04/28/06
0.012
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
No Standard
mg/L
10/09/06
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
--
mg/L
04/24/07
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
--
mg/L
10/31/07
0.0003
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/21/08
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
10I06/OS
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mgL
04,13/09
0.001
--
NO
NM
--
NM
NM
NM
ND
ND
--
ND
ND --
--
ND
ND
ND
ND
ND
ND
ND
--
NM
NO
mg/IL
1oil 5/09
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/26/10
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
10/19/10
0.001
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/18/11
0.001
--
NO
NM
--
NM
NM
NM
ND
ND
--
ND
ND --
--
ND
ND
ND
ND
ND
ND
ND
--
NM
NO
mg/L
10/10/11
-
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
--
NO
Dry
--
NM
NO
mg/L
04/17/12
0.0023
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
Dry
--
NM
NO
mg/L
10I09/12
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
ND
NO
Dry
--
NM
NO
mg/L
04I15/13
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
ND
NO
Dry
--
NM
NO
mg/L
09/30/13
-
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
ND
NO
Dry
--
NM
NO
mg/L
04/16/14
-
--
NO
NM
--
NM
NM
NM
ND
ND
-
ND
ND -
--
ND
ND
ND
ND
ND
ND
NM
--
NM
NO
mg/L
10I15/14
0.00062
-
NM
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NM
--
NM
NO
mg/L
04/15/15
0.00062
-
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
ND
ND
Dry
--
NM
NM
mg/L
10I07/15
0:00062
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/11/16
0.00062
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
11/30/16
0.0015
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO --
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
04/11/17
0.0015
--
NO
NM
--
NM
NM
NM
NO
NO
--
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
12/12/17
0.0015
--
NO
NM
--
NM
NM
NM
NO
NO
-
NO
NO -
--
NO
NO
NO
NO
NO
NO
NO
--
NM
NO
mg/L
O6I20/18
0.0015
--
NO
-
NM
NM
NM
NM
NO
--
NO
NO
NO -
--
NO
NO
NO
NO
ND
NO
--
NO
NM
NO
mg/L
11/27/18
0.0015
--
NO
-
NM
NM
NM
NM
NO
--
NO
NO
NO -
--
NO
NO
NO
NO
ND
NO
--
NO
NM
NO
mg/L
04/02/19
0.0015
--
NO
-
NM
NM
NM
--
ND
--
ND
ND
-- --
-
ND
ND
ND
ND
ND
ND
--
ND
NM
NO
m /L
11/19/19
0.0015
NO
NM
NM
NM
NO
NO
NO
NO
NM
NO
NO
NO
NO
ND
NO
NO
NM
NO
Methane
mg/L
04/28/06
0.0072
--
NO
NM
--
NM
NM
NM
0.014
4.8
-
4.7
0.86 -
-
0.0086
1.2
NO
7.2
4.7
5.8
7.7
-
NM
No Standard
mg/L
10I09/06
-
--
NO
NM
--
NM
NM
NM
0.0495
2.12
-
1.48
0.378 -
-
NO
0.237
NO
1.63
1.28
1.53
2.65
--
NM
--
mg/L
04/24/07
-
--
NO
NM
--
NM
NM
NM
0.018
2.8
-
2
0.24 -
-
NO
0.34
NO
2.9
1.9
2.4
1.9
--
NM
--
mg/L
10/31/07
0.0002
--
0.001
NM
--
NM
NM
NM
0.615
5.58
-
2.39
0.881 -
-
0.002
0.632
0.0006
5.36
3.01
4.76
5.9
--
NM
NO
mg
04/21/08
0.0004
--
NO
NM
--
NM
NM
NM
0.010
4.98
-
3.71
0.265 -
-
ND
0.514
0.0009 J
6.64
7.78
9.40
NM
--
NM
NO
mg/L
10/06/08
0.0004
--
0.0009 J
NM
--
NM
NM
NM
0.023
1.92
-
1.68
0.128 -
-
0.0004 J
0.138
ND
3.72
3.22
2.44
3.82
--
NM
NO
mg/L
04/13/09
0.0004
--
0.0006 J
NM
--
NM
NM
NM
0.021
2.65
-
2.16
0.242 -
-
0.002
0.267
0.002
3.43
4.95
4.18
4.99
--
NM
NO
mg/L
10/15/09
0.0004
--
0.0009 J
NM
--
NM
NM
NM
0.412
2.36
-
1.89
0.532 -
-
0.370
0.190
NO
3.48
1.89
2.86
5.397
--
NM
NO
mg/L
04/26/10
0.0004
--
0.001
NM
--
NM
NM
NM
0.057
2.66
-
2.41
0.208 -
-
NO
0.381
NO
3.52
4.09
2.56
ND
--
NM
NO
mg/L
10119/10
0.0004
--
0.00085 J
NM
--
NM
NM
NM
0.0365
2.54
-
1.96
0.442 -
-
0.00676
0.175
ND
4.36
3.46
3.21
3.64
--
NM
NO
mg
04118/11
0.0004
--
NO
NM
--
NM
NM
NM
0.0181
1.89
--
1.49
0.401 --
--
0.00149
0.118
NO
2.54
2.22
0.832
2.70
--
NM
NO
mg/L
10/10/11
0.0007
--
NO
NM
--
NM
NM
NM
0.343
4.08
-
5.1
0.696 -
-
1.19
0.3
0.000834
11A
-
8.6
Dry
--
NM
NO
mg/L
04/17/12
0.072
--
--
NM
--
NM
NM
NM
0.111
3.98
--
7.14
1.13 --
--
1.17
0.272
NO
12
12.9
9.48
Dry
--
NM
NO
mg/L
10I09/12
0.00043
--
NO
NM
--
NM
NM
NM
NO
2.02
--
3.2
0.538 --
--
0.508
0.139
NO
5.03
7.02
3.69
Dry
--
NM
NO
mg
04I15/13
0.00043
--
NO
NM
--
NM
NM
NM
0.00117
2.06
-
2.94
0.428 -
-
0.00685
0.0534
NO
4.87
50
2.73
Dry
--
NM
NO
mg/L
09/30/13
0.0004
--
NO
NM
--
NM
NM
NM
0.0329
1.88
--
2.74
0.389 --
--
0.0264
0.0603
0.00149
3.19
4.67
3.05
Dry
--
NM
NO
mg/L
04/16/14
0.0004
--
NO
NM
--
NM
NM
NM
ND
2.72
--
3.89
0.142 --
--
0.00195
0.0361
NO
5.19
5.67
3.59
NM
--
NM
NO
mg/L
10/15/14
0.0004
--
NM
NM
--
NM
NM
NM
NO
2.95
--
3.67
0.946 --
--
0.0115
0.0532
0.000598 J
4.53
3.36
3.4
Dry
--
NM
NO
mg/L
04/15/15
0.0004
--
NO
NM
--
NM
NM
NM
0.198
2.41
--
1.89
0.815 --
--
0.101
0.132
0.00122
1.42
2.24
3.59
Dry
--
NM
NM
mg/L
10/07/15
0.0004
--
NO
NM
--
NM
NM
NM
0.005 J
1.68
-
6.24
0.30 -
-
NO
0.051
NO
1.68
2.62
3.2
3.20
--
NM
NO
mg/L
0.0004
--
NO
NM
--
NM
NM
NM
0.535
1.33
-
2.1
0.585 -
-
0.000608 J
0.064
NO
3.8
3.59
3.8
2.3
--
NM
NO
mg/L
%11/16
11I30/16
0.00044
--
0.000724
NM
--
NM
NM
NM
0.000459 J
2.4
-
2.62
0.165 -
-
NO
0.0183
NO
3.0
1.26
0.94
1.36
--
NM
NO
mg/L
04111/17
0.00040
--
0.000496 J
NM
--
NM
NM
NM
0.000564 J
2.26
-
5.06
0.372 -
-
0.000636 J
0.0993
ND
6.05
1.56
5.90
5.10
--
NM
NO
mg/L
12/12/17
0:00040
--
0.0006 J
NM
--
NM
NM
NM
0.1870
1.67
-
1.67
0.879 -
-
0.2640
0.01160
NO
1.79
1.62
2.34
3.58
-
NM
NO
mg/L
06/20/18
0.00045
--
NO
-
NM
NM
NM
NM
0.134
--
2.85
3.1
0.154 -
-
NO
0.0409
NO
1.45
2.97
2.35
-
0.397
NM
NO
mg/L
11/27/18
0.00045
--
NO
-
NM
NM
NM
NM
0.0193
--
3.73
1.1
0.095 -
-
NO
0.0185
NO
3.84
4.02
5.654
-
0.958
NM
NO
mg/L
0402//19
45
0.0063
1.96
.
36
0.0386 -
-
0.000566 J
0.0549
NO
4.06
5.93
5.04
2.08
NO
m L
11I
0.04
0
NM
NM
NM0.0591
0.244
8
.
0.321
0.0442
NO
1.12
0.738
1.5
1.08
NM
NM1g19
GOLDER

February 2020 Page 7 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, INC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Ferrous Iron (field)
mg/L
04/28/06
0.0004
--
ND
NM
--
NM
NM
NM
0.168
48.248
-
43.164
ND -
-
ND
5.955
0.12
48.626
45.818
27.48
31.86
-717
NM
(labpriortoOct07)
mg/L
10/09/06
0.0004
--
ND
NM
--
NM
NM
NM
0.297
48.439
-
48.646
1.178 -
-
0165
9.008
0.119
47.664
45.339
24.615
27.974
-NMmg/L
04124/07
0.0004
--
ND
NM
--
NM
NM
NM
0.105
49.628
--
47.716
0.08 -
--
ND
3.116
0.071
35.416
49.731
35.416
25.649
-NMmg/L
10/31/07
0.0004
--
NO
NM
--
NM
NM
NM
1.3
3.0
--
4.6
20 -
--
NO
2.4
NO
2.8
4.4
5.7
2.1
--NMmg/L
04/21/08
-
--
NO
NM
--
NM
NM
NM
0.8
5.26
-
3.3
3.4 -
-
NO
0.8
NO
2.4
2.8
3.7
NM
--NMmg/L
10/06/08
--
--
0.6
NM
--
NM
NM
NM
1.8
4.0
-
4.2
30 --
-
NO
22
08
3.8
3.0
3.2
4.0
--
NMmg/L
04113/09
--
--
NO
NM
--
NM
NM
NM
ND
2.2
-
2.2
1.9 -
-
NO
2.0
NO
1.9
1.8
2.4
3.0
--
NM
--
mg/L
10/15/09
--
--
NO
NM
--
NM
NM
NM
NO
4.2
-
7.1
4.4 -
-
2.6
3.0
NO
>10
NM
3.9
>10
--
NM
--
mg/L
04/26/10
--
--
NO
NM
--
NM
NM
NM
0.2
8.6
-
5.6
4.0 -
-
NO
3.8
NO
>10
5.0
6.2
>10
--
NM
--
mg/L
10119/10
--
--
NO
NO
--
5.5
3.6
2.4
NO
4.0
-
4.0
4.6 -
-
NO
1.4
NO
4.0
4.0
3.5
2.0
--
4.0
--
mg/L
04/18/11
--
--
NO
NO
--
3.4
2.4
1.8
NO
3.0
-
3.4
3.2 -
-
NO
2.0
NO
2.0
2.8
4.8
3.0
--
3.8
--
mg/L
10/10/11
--
--
NO
NM
--
NM
NM
NM
3.0
5.0
-
6.0
5.0 -
-
4.0
2.0
NO
5.0
NM
4.0
Dry
--
NM
--
mg/L
04/17/12
--
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
IN
--
mg/L
10/09/12
--
--
ND
NM
--
NM
NM
NM
NO
3.4
-
3.8
3.2 -
-
1.8
0.6
NO
3.2
2.8
2.8
Dry
--
NM
--
mg/L
04/15/13
--
--
ND
NM
--
NM
NM
NM
NO
2.2
-
2.0
1.6 -
-
0.8
NO
NO
3.0
2.4
4.4
Dry
--
NM
mg,
09/30/13
--
--
NO
NM
--
NM
NM
NM
1.2
2.6
-
3.6
2.4 -
-
0.6
0.2
NO
3.6
2.4
2.2
Dry
--
NM
--
mg/L
04/16/14
--
--
NO
NM
--
NM
NM
NM
NO
2.5
-
1.5
4.0 -
-
NO
0.0
NO
1.5
3.0
1.0
Dry
--
NM
--
mg/L
10/15/14
--
--
Dry
3.6
--
4.4
3.6
5.0
4.2
4.2
-
4.2
5.8 -
-
3.2
4.0
0.8
5.0
4.8
3.6
Dry
--
4.6
--
mg/L
04/15/15
--
--
NO
2.4
--
2.2
1.6
2.8
2.0
3.2
-
3.6
2.8 -
-
NO
1.8
NO
3.0
3.6
2.4
Dry
--
2.8
--
mg/L
10/07/15
--
--
ND
NO
--
NO
NO
ND
ND
0.5
-
5.8
1.8 -
-
NO
2.4
ND
6.5
ND
4.0
Dry
--
ND
--
mg/L
04/11/16
--
--
ND
NM
--
NM
NM
NM
3.1
2.9
--
3.4
2.8 --
--
NO
3.7
ND
3.4
NM
2.0
3.8
--
NM
--
mg/L
11/30/16
--
--
NO
NM
--
NM
NM
NM
1.5
2.5
-
3.0
2.0 -
-
NO
2.2
NM
4.0
2.0
2.8
2.6
--
NM
--
mg/L
04,11/17
--
--
NO
NM
--
NM
NM
NM
NO
4.5
-
4.0
2.8 -
-
NO
2.5
NO
4.2
NM
1.9
3.0
--
NM
--
mg/L
12/12,17
--
--
ND
NM
--
NM
NM
NM
4.9
5.3
-
5.5
4.0 -
-
4.7
2.4
NO
5.5
NM
4.9
5.0
--
NM
--
mg/L
06/20/1a
--
--
ND
--
NM
NM
NM
NM
4.0
--
2.0
5.0
3.0 -
-
ND
1.2
ND
6.0
5.0
3.6
-
5.0
NM
--
mg
127 8
--
--
--
5.5
.5
--
7.0
5.
.5 --
--
NO
0.5
NO
3.3
2.0
4.0
--
3.0
NM
--
mg/L
04/02/19
--
--
--
--
2.5
3.0
2.5
--
--
--
2.5
4.0
2.5 -
-
1.0
2.5
3.5
6.5
6.0
4.3
--
5.8
2.8
--
m /L
11/19/19
-
--
NO
--
4.0
6.5
NM
--
7.0
--
4.5
3.5
-- 5.5
NO
3.5
4.8
NO
3.3
6.0
2.5
-
4.8
NM
--
Hydrogen
nM
10109/06
0.0004
--
1.0
NM
--
NM
NM
NM
1.1
1.0
-
1.2
1.1 -
-
1.1
0.9
1.0
1.4
1.0
1.2
-
--
NM
No Standard
nM
04/24/07
0.0004
--
--
NM
--
NM
NM
NM
--
NM
-
-
-- -
--
-
-
--
-
-
NM
-
--
NM
--
nM
10/31/07
0.0004
--
1.2
NM
--
NM
NM
NM
1.2
1.6
-
1.3
1.3 -
--
1.1
1.2
1.3
1.4
2.9
1.5
1.7
--
NM
--
nM
04/21/08
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
10/06/08
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
04/13/09
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
10/15/09
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
04/26/10
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
10119/10
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
nM
04/18/11
0.0004
--
0.76
NM
--
NM
NM
NM
0.69
1.10
-
1.1
0.81 -
--
1.00
0.88
0.86
1.10
NM
1.10
1.3
--
NM
--
nM
10/10/11
0.0004
--
0.90
NM
--
NM
NM
NM
0.64
0.66
-
3.4
1.6 -
-
0.99
0.41
J 0.72
0.72
NM
0.69
Dry
--
NM
--
nM
04/17/12
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
nM
10I09/12
0.0004
--
NM
NIM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
nM
04I15/13
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
nM
09I30/13
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
nM
04/16/14
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
nM
10/15/14
0.0004
--
Dry
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
nM
04/15/15
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
nM
10I07M5
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
nM
04111/16
0.0004
--
2.8
NM
--
NM
NM
NM
2.3
2.5
-
2.7
2.3 --
--
3.0
1.7
2.2
2.1
NM
2.6
NM
--
NM
NM
nM
11/30/16
0.0004
--
1.7
NM
--
NM
NM
NM
2.0
1.6
-
1.9
1.9 --
--
1.5
1.2
1.3
1.5
1.7
1.3
NO
--
NM
--
nM
11/30/16
0.0004
--
24
NM
--
NM
NM
NM
3.1
2.0
-
2.7
2.6 -
--
1.8
1.7
1.6
31
NM
2.7
0.64
--
NM
NM
nM
04/11/17
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
nM
12112/17
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
nM
O6/20/18
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
nM
11/27/18
0.0004
--
NM
--
NM
NM
NM
--
NM
--
NM
NM
-- --
--
NM
NM
NM
NM
NM
NM
--
NM
NM
NM
Carbon Dioxide
mg
04128/06
0.0004
--
45
NM
--
NM
NM
NM
37
572
--
385
256 --
--
52
280
42
531
431
500
418
--
NM
No Standard
mg,
10/09/06
0.0004
--
35
NM
--
NM
NM
NM
115
700
-
400
151 --
-
84
250
75
552
375
475
405
--
NM
--
mg/L
04/24/07
0.0004
--
17
NM
--
NM
NM
NM
72
622
-
368
155 --
-
35
148
48
480
545
602
409
--
NM
--
mgL
03 07
0.0004
--
30
NM
--
NM
NM
NM
95
>700
-
>100
>100 --
--
25
>100
60
>100
>100
>100
>100
--
NM
--
mg/L
04/21/08
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/06/08
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/13/09
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10/15/09
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04/26/10
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
10119/10
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
--
mg/L
04118/11
0.0004
--
11.8
NM
--
NM
NM
NM
57.5
330
-
231
369 --
-
46.6
161
36
269
164
272
320
--
NM
NO
mg/L
10/10/11
0.0004
--
36.6
NM
--
NM
NM
NM
261
528
-
373
414 --
-
319
500
126
739
NM
768
Dry
--
NM
NO
mg/L
04/17/12
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
-
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
mg/L
10/09/12
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
mg/L
04/15/13
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
--
mg/L
09/30/13
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM --
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/1
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
10115/6/14 14
0.0004
--
Dry
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
--
NM
NM
NM
NM
NM
NM
Dry
--
NM
NM
mg/L
04/15/15
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
10/07/15
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
04/11/16
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
11/30/16
0.0004
--
18.2
NM
--
NM
NM
NM
158
1020
-
589
267 -
-
72.5
151
66.7
814
362
498
497
--
NM
NM
mg/L
04/11/17
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
12112/17
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
mg/L
O6I20/18
0.0004
--
NM
NM
--
NM
NM
NM
NM
NM
-
NM
NM -
-
NM
NM
NM
NM
NM
NM
NM
--
NM
NM
m /L
11127/18
0.0004
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
NM
GOLDER

February 2020 Page 8 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
pH (field)
S.U.
04/28/06
--
--
4.90
4.70
--
--
5.40
4.70
5.10
6.30
-
5.90
4.70 -
-
5.00
6.10
5.00
5.90
5.90
6.40
5.50
-
6.10
--
S.U.
10/09/06
--
--
4.70
4.70
--
6.10
5.30
4.90
5.20
6.40
-
6.00
4.60 -
-
5.10
6.10
4.90
5.80
5.90
6.50
5.60
-
6.10
--
S.U.
04/24/07
--
--
5.00
5.10
--
6.10
5.10
4.70
4.60
6.20
-
5.80
4.60 -
-
5.30
6.00
4.80
5.60
6.00
6.30
5.60
-
6.00
--
S.U.
11/01/07
--
--
4.53
4.73
--
5.87
4.92
4.63
5.04
6.40
--
5.96
5.28 -
--
4.59
6.08
4.65
5.82
5.89
6.43
5.53
-
5.99
--
S.U.
04/23/08
--
--
5.63
5.85
-
8.16
6.55
4.98
6.07
7.78
--
8.00
6.59 -
--
5.55
7.20
5.89
7.19
7.62
7.50
7.46
-
7.62
--
S.U.
10/08/08
--
--
4.00
4.53
--
7.22
5.13
4.69
4.82
6.16
--
5.96
5.56 --
--
4.52
5.83
3.66
5.65
6.00
6.36
5.27
--
5.75
--
S.U.
04/13/09
--
--
4.52
5.31
--
5.62
5.10
4.13
5.05
6.23
-
5.92
6.02 -
-
4.76
6.08
4.65
5.70
5.70
6.38
5.42
-
5.55
--
S.U.
10/17/09
--
--
4.46
4.90
--
5.99
5.11
5.08
5.46
6.39
--
6.06
6.28 --
--
5.69
6.17
4.61
6.06
5.78
6.49
5.66
--
6.16
--
S.U.
04/26/10
--
--
4.20
5.10
--
5.41
4.54
4.99
4.42
6.05
--
5.68
5.65 --
--
4.53
5.74
4.28
5.62
6.02
6.23
5.48
--
5.31
--
S.U.
10/19/10
--
--
4.32
4.99
--
6.03
5.05
5.38
5.01
6.35
--
6.01
5.88 --
--
4.66
6.03
4.41
5.83
5.93
6.39
5.56
--
5.92
--
S.U.
04/18/11
--
--
4.11
4.63
--
5.62
5.00
5.18
4.72
6.13
--
5.62
5.87 --
--
4.39
5.59
4.17
5.36
5.68
6.04
5.41
--
5.55
--
S.U.
10/10/11
--
--
4.96
6.08
--
6.21
5.25
7.13
6.79
7.15
-
6.24
7.91 -
-
6.12
7.41
6.59
6.23
-
6.38
Dry
--
6.24
--
S.U.
04/17/12
--
--
3.46
4.69
--
5.38
4.68
4.62
3.91
5.86
--
5.74
5.92 --
--
5.33
5.56
3.88
5.76
5.80
6.38
Dry
--
5.57
--
S.U.
10/09/12
--
--
4.98
4.74
--
5.70
4.67
5.32
5.22
6.07
--
6.04
5.73 --
--
5.58
6.19
4.85
6.14
5.57
6.49
Dry
--
6.06
--
S.U.
04/15/13
--
--
4.28
5.28
--
5.77
4.70
5.52
4.71
6.67
--
6.04
6.07 --
--
5.19
6.26
4.02
5.95
6.12
6.57
Dry
--
6.04
--
S.U.
09/30/13
--
--
4.72
5.33
--
6.24
5.67
5.73
5.31
6.14
--
6.16
6.13 --
--
4.83
6.22
4.74
6.14
6.23
6.48
Dry
--
6.02
--
S.U.
04/16/14
--
--
5.00
6.19
--
6.72
6.07
6.50
6.16
6.70
-
6.47
6.61 -
-
5.28
6.46
5.14
6.41
6.64
6.77
Dry
--
6.29
--
S.U.
loll 5/14
--
--
Dry
5.85
--
6.65
5.73
6.66
6.12
7.06
--
6.58
7.13 --
--
5.63
6.59
5.30
6.55
6.62
7.07
Dry
--
6.73
--
S.U.
04/15/15
--
--
3.01
5.56
--
6.74
5.93
6.33
5.93
5.86
--
6.48
6.57 --
--
4.61
6.09
4.40
6.33
6.44
6.97
Dry
--
6.36
--
S.U.
10/07/15
--
--
3.59
4.44
--
5.52
4.12
5.94
4.70
5.60
--
4.52
4.80 --
--
4.38
5.29
3.51
6.07
4.11
6.32
Dry
--
5.32
--
S.U.
04/1 1/1 6
--
--
3.75
4.87
--
5.07
4.87
5.58
4.94
6.42
--
6.29
6.32 --
--
4.81
5.78
3.82
5.66
5.70
6.41
5.61
--
5.27
--
S.U.
11/30/16
--
--
4.95
5.82
--
5.70
5.33
6.26
5.98
6.55
-
5.87
6.55 -
--
4.48
5.82
4.05
6.23
6.23
6.28
5.22
--
6.20
--
S.U.
04/11/17
--
--
4.86
5.62
--
6.15
5.53
6.15
5.75
6A7
-
6.01
6.33 --
--
4.83
6.16
4.70
5.90
5.86
6.54
5.32
--
6.27
--
S.U.
12/12/17
--
--
4.48
5.55
--
6.12
4.99
5.99
6.00
6.35
-
6.13
6.29 --
--
5.32
6.13
4.28
6.07
5.45
6.40
5.70
--
6.19
--
S.U.
o6/20/18
--
--
4.67
--
6.12
5.99
5.34
6.14
6.01
--
6.29
5.95
5.93 --
--
3.79
5.79
3.83
6.00
5.76
6.34
-
5.71
5.93
--
S.U.
1 1/27/1 8
--
--
4.61
--
5.77
6.2
5.67
6.15
5.97
--
6.44
6.38
5.9 --
--
4.12
5.59
3.82
6.45
6.46
6.59
-
6.11
5.51
--
S.U.
04/02/19
--
--
4.49
--
6.35
6.26
5.92
6.09
6.02
--
6.49
6.29
6.07 -
-
4.59
6.18
4.59
6.22
6.24
6.44
-
5.98
5.95
--
S.U.
11/19/19
--
--
4.33
--
6.19
6.26
5.31
--
6.29
--
6.32
6.30
-- 6.27
9.08
5.53
6.00
4.39
6.16
6.01
6.50
-
5.95
6.32
--
Specific Conductance (field)
uS/cm
04/28/06
--
--
21
56
--
-
60
77
27
1144
--
370
194 -
-
88
697
31
398
267
1788
241
--
728
--
(lab prior to Oct. 07)
u.m
10I09/06
--
--
20
48
--
348
45
74
120
1206
--
447
147 -
-
103
635
34
398
328
1577
332
--
622
--
um
04124/07
--
--
19
74
--
273
47
61
98
957
-
430
172 -
-
105
621
43
323
479
1362
271
--
594
--
uS/cm
11I01/07
--
--
27
66
--
338
47
91
132
1790
-
499
556 -
-
103
779
41
445
472
2170
300
--
723
--
us/cm
04/23/08
--
--
20
90
--
330
48
120
82
1532
-
502
476 -
-
90
705
32
179
499
2163
264
--
403
--
us/cm
10/08/08
--
--
17
105
--
999
215
684
90
1330
-
457
529 -
-
80
554
30
316
521773
245
-
328
--
us/cm
04/13/09
--
--
13
178
--
258
76
148
123
1323
-
563
1160 -
-
92
791
38
373
369
2214
315
--
530
--
um
10/17/09
--
--
22
81
--
436
45
184
216
1981
-
584
1115 -
-
239
879
44
623
437
2270
403
--
854
--
us/cm
04/26/10
--
--
15
139
--
331
56
177
148
1645
-
624
425 -
-
76
717
40
379
653
2184
286
--
551
--
us/cm
10/19/10
--
--
20
97
--
387
74
207
129
1953
-
679
670 -
-
78
729
46
523
502
2199
384
--
682
--
us/cm
04/18/11
--
--
21
98
--
410
81
235
142
1802
-
710
1406 -
-
89
802
49
478
452
2395
392
--
869
--
us/cm
10/10/11
--
--
24
64
--
418
47
302
265
1452
-
671
898 -
-
281
855
53
699
-
2342
Dry
--
1041
--
um
04/17/12
--
--
21
69
--
357
49
123
118
791
-
620
869 -
-
202
807
39
619
383
2328
Dry
--
698
--
us/cm
10I09/12
--
--
20
58
--
341
56
212
25
926
-
572
627 -
-
152
821
37
642
406
2092
Dry
--
698
--
us/cm
04/15/13
--
--
18
52
--
313
60
206
75
963
--
532
930 -
-
71
694
34
645
405
2176
Dry
--
697
--
us/cm
09/30/13
--
--
21
144
--
391
106
359
102
1014
--
673
1227 -
-
77
491
43
725
761
2303
Dry
--
550
--
us/cm
04/16/14
--
--
58
227
--
422
158
684
99
1103
--
690
797 --
--
95
534
54
769
697
2292
Dry
--
671
--
uS/cm
10/15/14
--
--
Dry
105
--
420
91
810
148
1186
--
710
2260 --
-
120
580
88
920
640
2360
Dry
--
1150
--
us/cm
04/15/15
--
--
23
191
--
263
107
846
398
728
-
494
2030 -
-
87
576
40
523
300
1835
Dry
--
455
--
us/cm
10I07/15
--
--
23
180
--
361
82
633
118
1638
-
739
670 -
-
69
588
47
907
495
2381
Dry
--
1085
--
us/cm
04/11/16
--
--
19
243
--
261
133
759
351
1804
-
625
1326 -
-
53
467
53
818
521
1803
280
--
564
--
us/cm
11/30/16
--
--
19
263
--
321
102
811
314
2095
-
780
1274 -
-
53
454
46
917
516
2002
334
--
850
--
uS/cm
04/11/17
--
--
20
234
--
366
92
703
251
1925
-
806
1426 -
-
55
641
51
890
298
2217
312
--
1140
--
us/cm
12/12/17
--
--
20
208
--
429
49
526
324
1443
-
779
807 -
-
160
756
64
891
460
2200
401
-
984
--
us/cm
06I20/18
--
--
23
-
781
346
81
604
399
--
1233
820
449 -
-
61
784
54
840
590
220
-
268
989
--
us/cm
11/27/18
--
--
20
-
786
287
131
529
451
--
1604
863
299 -
-
52
467
44
922
560
2371
-
266
651
--
us/cm
04/02/19
--
--
18
-
800
257
164
581
445
--
1978
729
380 -
-
51
453
52
888
976
2016
-
359
597
--
uS/cm
11/19/19
--
--
23
-
684
439
60
--
477
--
1421
958
-- 690
363
155
548
69
626
366
1376
-
356
1064
--
Temperature (field)
Celsius
04/28/06
--
--
16.00
18.00
--
-
14.00
16.00
16.00
18.00
-
17.00
16.00 -
-
16.00
15.00
14.00
17.00
17.00
18.00
19.00
-
13.00
--
(lab prior to Oct. 07)
Celsius
10I09/06
--
--
20.00
20.00
--
21.00
19.00
21.00
20.00
21.00
-
19.00
21.00 -
-
20.00
19.00
19.00
19.00
20.00
20.00
18.00
-
20.00
--
Celsius
04124/07
--
--
17.00
17.00
--
16.00
16.00
17.00
19.00
19.00
-
16.00
19.00 -
-
18.00
17.00
17.00
17.00
18.00
20.00
18.00
--
16.00
--
Celsius
11I01/07
--
--
19.48
19.27
--
22.63
20.36
20.70
19.54
19.57
--
18.73
21.79 -
-
18.31
19.20
19.70
19.18
23.88
20.17
18.607
--
20.66
--
Celsius
04/23/08
--
--
14.83
17.56
--
16.92
17.97
19.26
16.55
16.83
--
16.55
18.28 -
-
14.84
15.59
14.80
16.52
16.28
17.82
17.33
--
16.61
--
Celsius
10/08/08
--
--
18.79
20.25
--
21.33
20.11
23.46
19.48
20.29
--
19.63
21.52 -
-
15.72
18.99
18.81
19.77
19.84
19.23
19.27
--
19.20
--
Celsius
04/13/09
--
--
14.55
16.64
--
14.52
15.95
17.69
15.24
16.47
--
16.11
17.99 -
-
14.94
14.91
14.86
15.82
16.55
18.62
17.43
--
14.09
--
Celsius
10/17/09
--
--
17.80
18.76
--
20.43
19.24
22.62
18.80
17.57
-
18.22
20.40 -
-
17.45
18.56
18.18
18.77
17.82
18.79
17.98
--
19.38
--
Celsius
04/26/10
--
--
16.23
18.63
--
16.30
17.85
20.91
15.66
16.52
-
16.85
18.44 -
-
14.40
15.51
14.85
17.05
18.24
18.45
17.25
--
16.05
--
Celsius
10/19/10
--
--
18.68
18.13
--
19.53
17.94
19.78
18.22
18.97
-
20.51
21.33 -
-
20.26
19.20
18.21
20.55
19.28
20.74
18.97
--
21.16
--
Celsius
04/18/11
--
--
15.48
18.09
--
15.69
17.59
22.01
16.10
17.19
-
17.16
19.67 -
-
17.39
15.45
15.45
16.95
19.00
21.49
19.89
--
15.23
--
Celsius
10/10/11
--
--
18.69
18.65
--
19.40
17.70
23.08
20.55
19.52
-
18.65
23.36 -
-
19.55
19.66
20.27
19.13
-
19.20
Dry
--
19.40
--
Celsius
04/17/12
--
--
16.60
18.06
--
17.34
19.68
21.08
16.25
18.15
-
17.29
20.47 -
-
17.55
16.39
16.11
18.01
16.55
19.29
Dry
--
16.42
--
Celsius
101 9/12
--
--
18.13
18.68
--
19.67
18.48
22.26
20.14
20.62
-
19.04
22.11 -
-
18.77
18.76
18.85
20.17
20.54
19.14
Dry
--
19.57
--
Celsius
04/15/13
--
--
14.23
18.63
--
15.72
16.97
19.35
14.23
18.08
-
16.64
19.06 -
-
15.28
14.26
14.04
16.92
17.86
19.24
Dry
--
16.11
--
Celsius
09/30/13
--
--
19.00
19.60
--
19.20
17.90
22.10
20.40
20.60
-
20.10
22.20 -
-
20.70
19.30
19.50
19.90
20.70
20.10
Dry
--
2080.
--
Celsius
04/16/14
--
--
12.90
17.30
--
14.60
16.40
17.10
14.00
15.80
-
14.80
14.80 -
-
13.20
13.70
13.60
15.20
16.80
17.10
Dry
--
13.80
--
Celsius
10/15/14
--
--
Dry
18.20
--
17.20
17.80
20.00
20.00
18.80
-
18.10
20.80 -
-
18.80
18.50
19.10
18.40
19.80
19.40
Dry
--
19.50
--
Celsius
04/15/15
--
--
13.69
16.40
--
13.65
15.35
16.12
13.52
14.29
-
13.47
15.42 -
-
13.71
13.38
13.45
14.21
14.37
16.53
Dry
--
12.66
--
Celsius
10/07/15
--
--
19.20
19.78
--
20.46
18.60
23.64
21.15
19.76
-
20.04
22.92 -
-
20.40
19.01
19.57
19.99
21.67
20.46
Dry
--
20.61
--
Celsius
04/11/16
--
--
15.60
16.88
--
14.93
16.25
20.15
13.71
14.90
-
14.61
15.73 -
-
14.06
14.90
15.70
16.20
16.30
16.65
17.80
--
13.72
--
Celsius
11/30/16
--
--
17.49
18.41
--
19.70
18.30
20.60
17.77
19.51
-
19.40
20.16 -
-
18.50
17.80
16.80
20.28
20.90
20.70
17.50
--
18.89
--
Celcius
04/11/17
--
--
16.13
18.21
--
16.60
18.43
20.27
15.93
17.61
-
17.20
18.41 -
-
16.34
15.51
15.34
17.60
18.77
19.59
18.70
-
16.62
--
Celcius
12112/17
--
--
15.00
17.90
--
18.50
17.80
16.90
14.20
15.70
-
18.00
18.90 -
-
16.20
16.00
15.10
18.20
13.90
18.00
17.80
-
17.50
--
Celsius
06I20/18
--
--
19.9
-
21.0
21.3
21.0
22.50
22.7
--
19.6
19.79
22.38 -
-
21.13
19.88
20.45
22.57
23.06
21.46
-
23.20
18.9
--
Celsius
11/27/18
--
--
16.2
-
17.1
18.7
16.9
19.1
15.5
--
19.0
18.9
20.4 -
-
15.9
16.3
15.5
18.8
18.6
19.5
-
17.6
15.7
--
Celsius
04/02/19
--
--
11.9
-
15.9
16.4
15.5
13.9
13.7
--
15
16.2
16.2 -
-
14.6
15.1
14.3
18.8
17.9
17.3
-
21.8
15.4
--
Celsius
11/19/19
--
--
17.2
-
18.9
18.6
18.2
--
17.4
--
19.7
19.0
-- 19.1
17.1
18.1
17.5
16.8
19.4
18.4
19.4
-
18.9
18.5
--
GOLDER

February 2020 Page 9 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural
Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling
Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Method
SwS
Aberdeen,
Active
Moore County, North Carolina
C&D Monitoring Wells & MNA Performance
Monitor! ng
Closed MSW
Parameter
Turbidity(field)
Rep rting
U.
nit.
NTU
Sample
04/28/O6
Detection
Lim!
--
ld"J�
--
74
NM
Active
--
C&D Monitoring
NM
Wells
NM
NM
5.1
290
-
20
1.2 -
-
to
7.8
Closed MSW
12
Monitoring Wells
55
& MNA Performance
86
Monitoring Wells
240
35
-
NM
--
(lab prior to Oct. 07)
NTU
10/09/06
--
--
13
NM
--
NM
NM
NM
120
850
-
500
-- -
-
65
55
34
210
500
330
75
-
NM
--
NTU
04/24/07
--
--
3.1
NM
--
NM
NM
NM
6
700
-
300
1.5 -
-
2.20
11
2.4
45
700
350
400
-
NM
--
NTU
11/01/07
--
--
116
204
--
243
415
116
330
>1000
--
95.1
137 -
--
39.4
96.3
99.1
116
105
155
111
-
151
--
NTU
04/23/08
--
--
21.7
2.34
-
20.2
45.1
3.33
12.2
369
-
3.91
12.4 -
-
2.71
8.15
4.35
9.36
29.2
67.9
15.8
-
7.07
--
NTU
10/08/08
--
--
2.46
5.68
-
46.6
6.21
2.11
5.77
286
-
8.06
20.1 --
-
3.94
1.03
1.11
7.37
47.9
90.4
30.4
--
4.75
--
NTU
04/13/09
--
--
2.26
9.91
-
9.42
13.7
2.33
6.49
38.2
-
12.6
28.8 -
-
3.98
17.6
15.8
-
69.4
16.7
81.5
--
15.6
--
NTU
10117/09
--
--
3.17
2.32
-
25.0
2.89
3.20
52.8
85.4
-
5.96
24.0 -
-
13.3
4.02
3.52
4.18
207
30.8
36.8
--
7.79
--
NTU
04/26/10
--
--
5.07
5.83
--
18.2
5.54
7.09
6.69
648
-
2.67
17.7 -
-
6.23
4.92
4.20
13.0
37.4
61.0
32.9
--
10.9
--
NTU
10,19/10
--
--
17.8
0.43
--
39.2
6.73
2.54
52.9
87.6
--
<100
8.94 --
--
10.3
36.1
2.44
12.8
71.3
23.0
8.36
--
'100
--
NTU
0.18/11
--
--
30.2
100
--
20.0
26.1
22.1
35.4
145
-
12.1
35.8 -
-
32.1
13.0
78.9
8.57
83.7
19.0
12.1
--
12.8
--
NTU
10/10/11
--
--
35.9
57.7
--
10.6
26.4
76.7
15.8
52.8
-
66
15.6 -
-
35.8
6.70
5.13
15.2
--
11.5
Dry
--
18.7
--
NTU
04/17/12
--
--
31.6
51.2
--
21.5
26.8
18.1
64.0
84.9
--
80.4
95.4 --
--
76.6
74.0
7.35
25.8
97.6
91.5
Dry
--
22.5
--
NTU
10/09/12
--
--
20.1
5.77
--
2.04
18.8
24.7
64.7
47.3
--
9.06
19.3 --
--
32.7
2.57
2.25
14.7
82.0
17.8
Dry
--
41.7
--
NTU
04/15/13
--
--
15.8
14.6
--
15.60
44.3
30.9
71.5
200
--
12.7
26.1 --
--
46.5
9.02
7.47
129
55.4
33.9
Dry
--
57.9
--
NTU
09/30/13
--
--
12.1
26.4
--
8.75
13.7
51.3
52.5
44.6
--
16.3
12.1 --
--
33.1
9.06
7.12
36.7
30.5
61.0
Dry
--
24.7
--
NTU
04/16/14
--
--
24.2
30.1
--
13.8
17.4
52.5
58.8
82.6
-
18.5
24.1 -
-
51.2
8.42
19.1
46.5
47.5
19.0
Dry
--
16.9
--
NTU
10/15/14
--
--
Dry
24.7
--
17.2
13.6
39.9
62.7
93.6
-
10
51 -
-
53
2.06
3.81
18.6
46.6
66.2
Dry
--
7.03
--
NTU
04/15/15
--
--
35.7
26.1
--
13.2
24.9
142
18.8
48.5
--
18.4
29.0 --
--
21.0
4.76
1.21
22.3
31.1
11.8
Dry
--
36.9
--
NTU
10/07/15
--
--
4.85
10.1
--
30.1
45.5
3.83
39.5
724
--
9.19
11.0 --
--
25.4
0.99
0.78
19.3
32.6
8.6
Dry
--
1.81
--
NTU
04/11/16
--
--
3.67
4.38
--
3.7
11.8
39.2
18.1
148
--
15.8
5.9 --
--
10.4
2.23
0.77
16.5
10.7
22.60
94.1
-
1.34
--
NTU
11/30/16
--
--
6.90
1.05
--
5.57
10.8
4.71
8.64
32.8
-
3.11
13.1 -
-
23.3
1.8
1.21
11.7
64.3
8.54
60
-
5.62
--
NTU
04111/17
--
--
7.89
5.43
--
4.85
9.97
25.4
33.3
220
-
4.48
8.26 -
-
11.7
2.03
0.72
8.47
19.0
8.31
34.2
-
6.31
--
NTU
12/12/17
--
--
5.14
4.33
--
4.79
4.68
8.62
40.8
28.3
-
15.5
10.8 -
-
28.8
4.74
0.13
7.36
6.0
6.76
19.7
-
8.12
--
NTU
06/20/18
--
--
6.11
-
6.36
9.22
9.91
8.13
9.38
--
4.97
820
7.93 -
-
9.98
7.76
7.08
9.89
5.98
7.63
-
6.34
5.01
--
NTU
11/27/18
--
--
2.4
--
9.87
6.83
7.05
6.25
8.0
--
4.44
2.11
9.69 -
-
9.8
7.64
1.41
9.99
6.79
9.95
-
9.75
9.24
--
NTU
04/02/19
--
--
9.14
--
2.09
9.69
5.26
132
8.52
--
3.62
5.28
2.51 -
-
8.50
5.74
3.92
8.26
16.4
9.58
-
9.60
18.8
--
NTU
11/19/19
--
--
1.36
--
1.40
2.83
6.10
--
17.0
--
0.54
3.89
-- 9.50
8.99
19.4
3.74
1.73
9.36
20.4
8.14
-
9.98
7.0
--
Oxidation Reduction Pot.
mV
04/28/06
--
--
286
NM
--
NM
NM
NM
239
-46.0
-
31.0
265 -
-
258
79.0
254
2.00
9.00
-43.0
128
-
NM
--
(field)
mV
10I09/06
--
--
232
NM
--
NM
NM
NM
194
-68.0
-
7.00
252 -
-
2.40
32.0
220
4.00
-2.00
-4.00
-7.00
-
NM
--
(lab prior to Oct. 07)
mV
04124/07
--
--
190
NM
--
NM
NM
NM
198
-77.0
-
9.00
224 -
-
168
32.0
220
-8.00
-38.0
-60.0
22.0
-
NM
--
mV
11I01/07
--
--
252
NM
--
NM
NM
NM
180
-171
-
-87.0
18.0 -
-
332
-48.0
331
-84.0
-119
-123
-72.0
-
NM
--
mV
04/23/08
--
--
60.9
65.2
--
-89.5
50.4
135
45.7
-102
-
-58.2
31.1 -
-
21.4
-4.70
67.1
-113
-114
-81.7
-134
-
-90.9
--
mV
10/08/08
--
--
223
164
--
-119
89.0
179
218
-72.1
-
-45.3
66.1 -
-
228
66.1
309
-107
-65.1
-94.4
-60.7
--
-32.1
--
mV
04/13/09
--
--
285
92.5
--
-22.8
119
332
214
-87.8
-
-25.1
-16.3 -
-
284
-8.30
292
-73.6
-28.5
-90.9
-27.0
--
-17.9
--
mV
10/17/09
--
--
297
193
--
-62.6
135
182
118
-92.5
-
-48.3
-48.4 --
-
36.9
-18.1
256
-54.6
-24.6
-94.3
-16.4
--
-59.9
--
mV
04/26/10
--
--
221
83.5
--
-52.3
118
146
200
-86.7
-
-48.5
54.4 -
-
173
28.0
173
-98.0
-42.7
-85.9
-77.9
--
-15.6
--
mV
10/19/10
--
--
282
105
--
-51.8
155
133
208
-83.7
-
-44.0
71.1 -
-
148
82.9
199
-81.7
-22.4
-94.8
-110
--
-48.9
--
mV
04/18/11
--
--
267
209
--
11.8
121
151
214
-62.8
-
-30.9
-2.20 -
-
223
45.2
220
-16.8
-44.7
-79.4
-5.10
--
12.8
--
mV
10/10/11
--
--
80.9
139
--
-70.1
87.4
61.8
97.3
-47.6
-
-85.1
-25.9 --
--
23.3
15.7
143
-86.3
--
-102
Dry
--
-75.4
--
mV
04/17/12
--
--
245
142
--
-5.4
126
188
163
-27.9
--
-53.9
16.3 -
-
67.2
138
181
-61.1
1.90
-112
Dry
--
-24.4
--
mV
to/ 09112
--
--
106.2
85.8
--
-32.2
111
60.8
89.8
-58.9
-
-76.4
13.1 -
-
70.0
19.4
101
-79.3
-32.1
-98.0
Dry
--
-53.2
--
mV
04/15/13
--
--
199
170
--
-33.9
107
117
133
-86.8
-
-74.4
-4.70 -
-
193
86.5
215
-38.7
-60.7
-113
Dry
--
-72.5
--
mV
09/30/13
--
--
286
139
--
-33.2
105
81.0
213
-41.6
--
-34.6
-3.30 --
--
309
128
333
-45.7
-43.9
-64.6
Dry
--
-16.4
--
mV
04/16/14
--
--
338
40.4
--
-62.2
88.3
31.3
232
-95.8
--
-60.0
4.90 --
--
282
143
338
-59.3
-55.0
-42.2
Dry
--
-39.8
--
mV
10/15/14
--
--
Dry
209
--
-56.2
178
25.00
187
-77.9
--
-38.6
-81.9 -
-
246
58.8
395
-56.1
-21.9
-103
Dry
--
-60.7
--
mV
04/15/15
--
--
340
61.4
--
-52.6
6.80
16.5
-22.1
-9.10
-
-63.3
-53.7 -
-
90.4
-20.8
65.1
-55.9
-19.8
-97.2
Dry
--
-36.6
--
mV
10I07/15
--
--
116
3.80
--
-20.9
27.1
-117
-40.5
-183
-
-61.1
-77.2 -
-
18.1
-61.9
20.2
-73.1
-96.2
-136
Dry
--
-100
--
mV
04/11/16
--
--
373
50.4
--
-29.2
40.7
8.00
64.0
-70.3
-
-55.3
-29.1 -
-
190
105
354
-41.8
24.7
-70.4
-
--
-14.6
--
mV
11/30/16
--
--
230
34.9
--
-46.0
74.0
-18
58.6
-86.6
-
-73.8
-65.1 -
-
379
66.8
345
-75.8
-58.4
-79.1
-27.6
--
-56.7
--
mV
04/11/17
--
--
175
68.2
--
-35.9
85.5
9.6
120
-85.6
-
-45.8
-29.1 -
-
262
49.1
200
-38.5
56.4
-61.4
11.8
-
-45.3
--
mV
12/12/17
--
--
385
80.8
--
1.7
211
17.2
62.0
-75.0
-
-87.9
-32.8 -
-
150
129
328
-66.3
--
-65.4
-1.8
--
-42.5
--
mV
O6120/18
--
--
417.3
--
-16.0
-20.3
109.2
15.3
156.4
--
-66.10
-52.4
67.1 -
-
196.4
177.8
166.4
-22.4
3.2
-69.9
-
42.2
-29.0
--
mV
11/27/18
--
--
298.4
-
-72.5
-29.9
42.6
12.1
131.6
--
-81.8
-70.8
56.8 -
-
256.9
59.4
287.2
-146.2
-90.6
-102.5
-
-59.2
-63.7
--
mV
04/02/19
--
--
270.8
-
-78
-65.7
14.4
6.9
90.0
--
-94.6
-80.9
190.2 -
-
194.4
98.8
418.6
-47.5
-77.20
-77.5
-
-17.6
-30.9
--
mV
11119/19
--
--
369.3
-
-79.9
-73.5
138.5
--
-42.0
--
-105.6
-12.1
-- -42.6
-43.5
38.4
43.3
56.8
-133.4
-97.6
-131.1
-
-123.1
-124.6
--
GOLDER

February 2020 Page 10 of 10 Project No. 19127453
TABLES
Summary of Historical Monitored Natural Attenuation Results
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling
Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
Dissolved Oxygen (field)
mg/L
04/28/O6
--
--
7.98
NM
--
NM
NM
NM
7.79
1.02 - 0.32
0.49 -
-
7.02
0.59
4.19
0.63
0.44
0.47
0.37
-
NM
--
(let)prior to Oct. 07)
mg/L
10/09/06
--
--
6.59
NM
--
NM
NM
NM
0.50
0.41 - 0.35
0.25 -
-
1.32
0.38
2.23
0.36
0.55
0.87
1.49
-
NM
--
mg/L
04124/07
--
--
10.02
NM
--
NM
NM
NM
4.26
0.99 - 0.91
0.84 -
-
6.37
5.25
4.26
0.90
1.19
0.75
1.41
-
NM
--
mg/L
11I01/07
--
--
8.02
NM
--
NM
NM
NM
2.17
0.40 -- 1.08
0.59 -
-
7.26
0.64
4.93
0.75
0.33
0.47
0.41
-
NM
--
mg/L
04/23/08
--
--
9.65
1.69
--
2.29
2.49
2.43
4.50
1.55 - 1.48
1.58 -
-
5.66
1.53
6.74
1.78
1.66
2.20
1.60
-
2.24
--
mg/L
10/08/08
--
--
7.12
2.28
--
0.67
0.54
0.79
1.67
0.72 - 0.98
2.15 -
--
5.41
0.81
3.84
0.49
0.86
6.29
1.46
--
0.85
--
mg/L
04/13/09
--
--
8.29
1.49
--
0.68
2.06
2.00
2.65
1.12 - 1.30
1.45 --
-
5.55
1.40
5.52
0.67
1.38
0.78
1.66
--
1.31
--
mg/L
10/17/09
--
--
9.10
0.88
--
0.89
1.37
0.95
1.80
0.85 - 1.04
1.15 --
-
1.84
1.23
4.89
0.74
0.55
1.05
3.97
--
2.05
--
mg/L
04/26/10
--
--
7.96
1.23
--
0.43
0.99
1.21
1.06
0.28 -- 1.05
1.28 --
--
4.23
0.91
5.52
0.54
1.98
0.70
0.96
--
1.08
--
mg/L
10/19/10
--
--
7.77
0.54
--
0.25
1.96
1.13
2.07
0.60 -- 0.60
0.47 --
--
4.77
0.27
4.52
0.31
1.50
0.31
0.36
--
0.50
--
mg/L
04/18/11
--
--
8.02
0.46
--
0.89
0.97
0.89
1.90
0.25 -- 0.55
0.62 --
--
4.94
0.59
5.15
0.65
2.38
0.59
0.72
--
0.77
--
mg/L
10/10/11
--
--
6.78
0.60
--
0.63
0.53
1.07
0.86
0.79 - 0.62
0.65 -
--
1.09
0.64
4.53
0.87
-
0.93
Dry
--
1.09
--
mg/L
04/17/12
--
--
9.09
1.00
--
0.24
1.78
2.73
1.44
1.31 -- 0.91
1.01 -
--
1.58
0.68
5.64
0.29
7.01
0.88
Dry
--
1.07
--
mg/L
10/09/12
--
--
6.36
0.23
--
0.48
0.39
0.32
4.86
0.23 -- 0.23
0.24 --
--
0.56
0.49
2.98
0.43
6.38
0.57
Dry
--
0.44
--
mg/L
04/15/13
--
--
8.50
0.86
--
0.83
0.89
1.21
2.97
1.04 -- 0.81
0.82 --
--
5.34
0.73
6.64
1.13
40.5
0.41
Dry
--
0.54
--
mg/L
09/30/13
--
--
7.46
0.32
--
0.42
0.47
0.61
0.70
0.68 -- 0.42
0.27 --
--
1.95
0.40
2.48
2.29
0.70
0.34
Dry
--
0.37
--
mg/L
04116/14
--
--
8.20
0.33
--
0.77
0.49
1.79
7.87
0.49 - 0.53
1.79 -
-
6.04
0.39
5.89
1.05
1.55
0.36
Dry
--
0.48
--
mg/L
10115/14
--
--
Dry
0.57
--
0.90
0.71
0.65
1.07
0.85 - 0.68
0.60 -
-
0.95
0.58
1.93
0.67
1.27
0.88
Dry
--
0.41
--
mg/L
04/15/15
--
--
7.24
0.89
--
0.84
0.86
0.68
0.53
0.61 - 0.86
0.50 --
--
3.195
0.59
4.00
0.96
1.72
0.69
Dry
--
0.75
--
mg/L
10/07/15
--
--
5.45
0.93
--
1.24
2.00
0.81
1.90
0.40 - 0.38
0.49 --
--
3.61
1.65
2.76
0.59
0.35
5.13
Dry
--
0.72
--
mg/L
04/11/i6
--
--
7.77
1.85
--
0.87
1.16
1.30
1.17
1.01 - 0.53
0.58 --
--
3.42
0.87
3.93
0.92
1.21
0.54
-
--
0.82
--
mg/L
11/30/16
--
--
7.26
0.20
--
0.33
0.18
0.22
0.10
0.05 - 0.71
0.13 -
-
2.78
0.28
4.11
0.22
1.34
1.12
0.42
-
0.18
--
mg/L
04;11/17
--
--
7.02
0.30
--
0.18
0.18
0.51
1.52
0.18 - 0.56
0.16 -
-
3.83
0.45
3.99
0.34
1.17
0.41
0.67
-
0.37
--
mg/L
12112/17
--
--
6.79
0.23
--
0.25
0.25
0.45
0.84
0.24 -- 0.24
0.25 --
--
1.71
0.39
2.38
0.26
-
0.38
0.41
--
0.35
--
mg/L
O6120/18
--
--
7.45
--
0.19
0.24
0.23
0.44
0.19
-- 0.47 0.21
0.69 --
--
3.71
0.23
7.08
1.39
0.15
0.26
--
0.26
0.24
--
mg/L
11/27/18
--
--
6.34
--
0.36
0.19
0.28
0.23
0.22
-- 0.17 0.21
1.45 --
--
2.80
0.42
3.17
0.20
0.26
0.1
-
0.25
0.38
--
mg/L
04/02/19
--
--
6.67
--
0.12
0.04
0.11
0.28
1.12
-- 6.27 0.11
2.76 -
-
2.34
0.12
3.21
0.20
0.27
0.24
-
0.18
0.20
--
m /L
11/19/19
--
--
6.26
--
0.21
0.14
0.10
--
0.8
-- 0.20 0.21
-- 0.14
1.98
1.00
0.30
2.20
0.44
0.68
0.24
-
0.28
0.36
--
Notes:
1.) Samples collected using low -flow purge and sample techniques.
2.) mg/L = milligrams per liter
3.) NO = not detected at or above the laboratory reporting limit
4.) NM = not measured
5.) uS/cm = microseimens per centimeter
6.) NTU = Nephelometric Turbidity Units
7.) S.U. = Standard Units
8.) Bold only = Concentration above current NC 2L Groundwater Standard or NC SWS Groundwater Protection Standard
9.) Shaded and Bold = Concentration above current NC 2L Groundwater Standard or NC SWS Groundwater Protection Standard and EPA MCL
10.) EPA MCL = US Environmental Protection Agency Maximum Contaminant Level
11.) SWS Reporting Limit = NCPQL or lab-sepcific reporting limit prior to October 2007 and NCSWSL starting in October 2007
12.) mV = millivolts
13.) -- = no data available or not established
14.) J = estimated concentration reported above the laboratory detection limit, but below the laboratory quantitation limit
15.) * = Wells MW-8, MW-11 DR, MW-135, MW-13D, MW-17D, and PW-1 are not sampled for monitored natural attenuation parameters since it is not required in the approved monitoring plan and therefore
these data are listed as "NM" in this table. Similarly, carbon dioxide, hydrogen and volatilve fatty acids were not analyzed beginning in April 2008, per NCDENR approval.
16.) The following dilutions were noted for the November 2019 event: Nitrate 5X for MW-7, Total Alkalinty 10X for MW-9, 5X for MW-11SR, 2X for MW-2, MW- 6, & MW-2 Methane 5X for MW-7, Chloride 2X for MW-9
GOLDER

February 2020 Page 1 of 1 Project No. 19127453
TABLE 9
Evaluation of Converging Lines of Evidence for Reductive Biological Attenuation
Water Quality Monitoring Report, 2019 Second Semi -Annual Sampling Event
Moore County Landfill, NC Solid Waste Permit No. 63-01
Aberdeen, Moore County, North Carolina
MW-15R
Relative Horizon!al
I
Near/Sidegradient
Presence of Product
wc
No
Presence of Biologi cal Attenuatio
�.
rTo,
Yes (1,1-DCA, cDCE, VC)
y'. ' )
Yes (benzene, toluene)
Yes (chlorobenzene, 1,4-
18.90
JHydrogen (nM)
NM
Disso ved
(mg/L)
0.25
units)
5.95
q,.P(
-123.1
NM
(mg/L)
ND
Organic IlTota
(mg/L)
18
mg/L)
97
(mg/L)
ND
(mg/L)
ND
Volati:e
(mg/L)
NM
Evaluation
Weaker
Indicator
0.065 mg/L
of Dominant
----------- Reducing
Iron 11
Indicator
4.8 mg/L
Electron
Conditions
Sulfate
Indicator
9.9 mg/L
Accepting Process
-------------- Stronger
Sulfide
Indicator Indicator-
0.37 mg/L 1.08 mg/L
of Source
<0.1 mg/L
dichlorobenzene)
Nitrate as N
Fe+2
Sulfate
Sulfide Methane
MW-6
Middle Portion
No
Yes (cDCE, VC)
Yes (benzene)
Yes (chlorobenzene, 1,4-
17.20
NM
0.44
6.16
-133.4
NM
13
13
260
ND
ND
NM
0.067 mg/L
3.3 mg/L
13 mg/L
0.097 J mg/L 1.12 mg/L
<0.1 mg/L
dichlorobenzene)
Nitrate as N
Fe+2
Sulfate
Sulfide Methane
MW-11SR
Middle Portion
No
Yes (cDCE, VC)
Yes (benzene)
Yes (chlorobenzene, 1,4-
19.70
NM
0.20
6.32
-105.6
NM
25
22
650
ND
ND
NM
0.086 mg/L
4.5 mg/L
3.3 J mg/L
0.061 J mg/L 0.244 mg/L Methane
<0.1 mg/L
dichlorobenzene)
Nitrate as N
Fe+2
Sulfate
Sulfide
MW-4
Downgradient
No
Yes (cDCE)
No
Yes (1,4-dichlorobenzene)
17.40
NM
0.80
6.29
-42
NM
18
27
190
ND
ND
NM
1.3 mg/L
7.0 mg/L
26 mg/L
0.0591 mg/L
ND
Portion
Nitrate as N
Fe*2
Sulfate
Methane
MW-5
Background Well
No
No
No
No
17.20
NM
6.26
4.33
369.3
NM
ND
ND
ND
ND
ND
NM
0.420 mg/L
ND
ND
ND ND
Nitrate as N
Suggested Value Conducive to
Yes (Acts as Carbon
Yes (Potential Carbon
Elevated >2X
Elevated >2X
Elevated >2X
Reductive Biological Attenuation:
Yes
Source)
Source)
>20°C
>1 nM
<0.5 mg/L
5-9
<50
Relative to
Relative to
>20
Relative to
>0.01 mg/L
>0.01 mg/L
>0.1 mg/L
<1 mg/L
>1 mg/L
<20 mg/L
>1 mg/L >0.5 mg/L
Background
Background
Background
Notes:
1.) Shaded cells indicate conditions conductive to reductive biological attenuation.
2.) Most recent analytical results are presented
3.) TCE = Tricholoroethene
4.) PCE = Tetrachlomethene
5.) cDCE = cis-1,2-dichloroethene
6.) tDCE = trans-1,2-dichloroethene
7.) VC = vinyl chloride
8.) 1,1-DCE = 1,1-dichloroethene
9.) 1,1-DCA= 1,1-dichloroethane
10.) CA = chloroethane
11.) NA = Not Available
12.) NM = Not Measured
13.) ND = Not Detected
14.) *Source: Weidemeier at al., 1998, Technical Protocol for Evaluating Natural Attenuation of Chlorinated Solvents in Ground Water
15.) **Dissolved methane concentrations may be related to landfill gas.
16.) BTEX = Benzene, Toluene, Ethylbenzene, and Xylenes
17.) TVFA = Total Volatile Fatty Acids
G-.PR EC %Mows CwnM19127453-Moore-Env Services FY19-20\P100-WGM&Repo,ling\6DDC CULN QNS1020-02-15WQMRTbM .4> G O L D E R

DRAWINGS

LEGEND
SW-2 [']�
l�\ DENSE GETATION
,I
DENSE VEGETATION
I
\ DENSE VEGETATION
I`
DENSE GETATION
GROUND OBSCURED
DENSE VEGETATION
SEE ACCURACY NOTE
\ DE VEGETATION
GROUND OBSCURED
SEE ACCURACY NOTE
SITE LOCATION MAP
NOT TO SCALE
V LILIV 1
MOORE COUNTY
wall vuvjon■ 444SIIO1G91W,
rr«rmmEu
GO L D E R DESIGN
REVIEW
DENSE
�
�`VEGETATI
DENSE
C—
STREAM, POND, AND WETLAND LIMITS
EXISTING 10 FT GROUND SURFACE CONTOUR
EXISTING 2 FT GROUND SURFACE CONTOUR
PROPERTY LINE
APPROXIMATE LIMITS OF WASTE
EXISTING ROAD
385 POTENTIOMETRIC GROUNDWATER CONTOURS (5 FT. INTERVAL)
GROUNDWATER FLOW SEGMENTS
MW-1 MONITORING WELL AND IDENTIFICATION
'380.94
GP-10 METHANE PROBE AND IDENTIFICATION
❑ SW-1 SURFACE WATER MONITORING POINT AND IDENTIFICATION
LANDFILL GAS TRENCH VENTS AND IDENTIFICATION
m PASSIVE LANDFILL GAS VENTS
0 PW-1 PRIVATE WELL LOCATION AND IDENTIFICATION
4 WETLAND AREA
SB-2 SOIL SAMPLE LOCATIONS
PZ-2 PIEZOMETERS
NOTES
1. TOPOGRAPHIC CONTOUR INTERVAL = 2 FEET
2. GROUNDWATER SURFACE CONTOUR INTERVAL = 5 FEET
3. GROUNDWATER ELEVATIONS MEASURED ON NOVEMBER 19, 2019.
4. GROUNDWATER CONTOURS BASED ON LINEAR INTERPOLATION BETWEEN AND
EXTRAPOLATION FROM KNOWN DATA, TOPOGRAPHIC CONTOURS, AND KNOWN FIELD
CONDITIONS. THEREFORE, GROUNDWATER CONTOURS MAY NOT REFLECT ACTUAL
CONDITIONS.
5. GROUNDWATER CONTOUR LINES SHOW THE WATER TABLE SHAPE AND ELEVATION. THESE
CONTOURS ARE INFERRED LINES FOLLOWING THE GROUNDWATER SURFACE AT A
CONSTANT ELEVATION ABOVE SEA LEVEL. THE GROUNDWATER FLOW DIRECTION IS
GENERALLY PERPENDICULAR TO THE GROUNDWATER SURFACE CONTOURS, SIMILAR TO THE
RELATIONSHIP BETWEEN SURFACE WATER FLOW AND TOPOGRAPHIC CONTOURS.
6. PROPERTY BOUNDARY SURVEY BY JAMES L. WRIGHT DATED NOVEMBER 1984. ITS LOCATION
IS RELATIVE TO TOPOGRAPHY APPROXIMATE BY HDR ENGINEERING, INC.
7. EXISTING TOPOGRAPHY WITHIN ACTIVE AND PROPOSED LANDFILL PROVIDED BY MATTHEWS
LAND SURVEYING & MAPPING, PLLC DATED APRIL 17, 2015 AND JUNE 2018.
8. MONITORING WELLS MW-1 THROUGH MW-5 SURVEYED JUNE 1987 BY S&ME, INC. MONITORING
WELLS MW-6 THROUGH MW-16 SURVEYED APRIL 1995, SEPTEMBER 1996, AND APRIL 2003 BY
HDR ENGINEERING INC./ ED BUCKNER RLS APRIL 17, 2015.
9. THE LOCATIONS OF LANDFILL GAS TRENCH VENTS ARE APPROXIMATE.
10. GROUNDWATER WELLS MW-11 DR, MW-13D, AND MW-17D ARE NOT SCREENED IN THE
SHALLOW AQUIFER AND ELEVATION DATA WERE NOT USED IN THE CONSTRUCTION OF
GROUNDWATER CONTOURS.
0 200 400
SCALE FEET
PROJECT
MOORE COUNTY LANDFILL
NC SOLID WASTE PERMIT NO. 63-01
ABERDEEN, MOORE COUNTY, NORTH CAROLINA
TITLE
GROUNDWATER SURFACE CONTOUR MAP
NOVEMBER 19, 2019
PROJECT No.
PHASE
Rev.
DRAWING
19127453
100
0
it
II'
11
APPROVED RPK

LL
-N- i ��,��� �� �1 vv LEGEND
6 PERENNIAL STREAM
�POND �.�..., POND
­6/% — — % ° ✓ A ;, WE aoas—
� INTERMITTENT STREAM
- — — — — — — — - EPHEMERAL STREAM
�_ \ ` - / ---- - -i — POND AND WETLAND LIMITS
�
,
-- EXISTING 10 FT GROUND SURFACE CONTOUR
tandard
- .- W-1 � 2L Si �...--d .:: i 1 - p� MW-1
-
°
' �� _ `� _„� ��� ' I n r 3 .8ro• - \ 17
EXISTING 2 FT GROUND SURFACE CONTOUR
GROUND OBSCU EO GROUND
SEE ACCURACY DTE i _ R SEE ACCURACY
� .'� ,��.. ,.'. '"" �,"" -' � ° ° ��'��//�� III 11 • 6 5 � i �� 0 � � .5 4
o m/ m m PROPERTY LINE3.7 u /� 4uMW^1.D � \ �J
/1� 8 J . •
\ ° �(((�(z.
s o \ APPROXIMATE LIMITS OF WASTE
z z�( z, \ �,�IT.,,°„ ��° � -4 ..`� -1,� �e ,s z �� z
4 �'" - - - - - - - - - -
= P-1 % �\ M - 15�' �\ EXISTING ROAD
2.3u /L �° ! �" 5.6u /
° e .
BENZENE ISO -CONCENTRATION CONTOURS UG/L V, �� ��
1 4-DICHLOROBENZENE ISO -CONCENTRATION CONTOURS UG/L
C 9 O I UMW- \2� D — MW- \2F o �� 6 ( )
W�1 - g 1.6 J ug/ ��' r MA1 DE g j 3.0 u / �,r
1 —Q 03 VINYL CHLORIDE ISO -CONCENTRATION CONTOURS (UG/L)
� I( I I I(
\ff M W-1 D` G P`1`4 G P4
I V L✓ °L 7.�.. e
�� 38rJ GROUNDWATER POTENTIOMETRIC SURFACE
. ( �" - �" ■ GROUNDWATER FLOW PATHWAY
r
0 MW-1 MONITORING WELL IDENTIFICATION AND VOC CONCENTRATION (PPB)
.s m
D - ,,i ° . •, � •-• NCOLOR IDENTIFIES VOC
� i \ i �•.ffi,)_� ^ i ~fin. i n _ GP-10 METHANE PROBE AND IDENTIFICATION
P-12�
- ---� �� �l �' •° �°••- ---� �� �❑ SW-1 SURFACE WATER MONITORING POINT AND IDENTIFICATION
rr/
ND OBSCURED \ �"T0N a„• rear.°0A "'/ �.� / l UND OBSCURED \ ���,••°m �• -�/`� /� g 1 PASSIVE LANDFILL GAS VENTS AND IDENTIFICATION
ACCURACY NOTE _ `� O /I - - _ ' ° ((( ACCURACY NOTE 15 vv
0 PW-1 PRIVATE WELL LOCATION AND IDENTIFICATION
NC 2L = 1 mg/L 1 ..° ' + .... NC 2L = 6 m /L
NOTES
BENZENE CONCENTRATION �`�` 1+DICHLOROBENZENE CONCENTRATION
" �� - s 1) TOPOGRAPHIC CONTOUR INTERVAL = 2 FEET
2) VOC - VOLATILE ORGANIC COMPOUND
I
"`� ��°+� „�� �� •-"°� "�'� �! i 3 VOC ISO -CONCENTRATIONS BASED ON LINEAR INTERPOLATION BETWEEN AND
/ )
0 ° EXTRAPOLATION FROM KNOWN DATA FOR THE UPPERMOST AQUIFER, TOPOGRAPHIC
PDND =" �` CONTOURS, AND KNOWN FIELD CONDITIONS. THEREFORE, ISO -CONCENTRATIONS MAY
�.�,� I ' POND ... �.. °m..., wE 403.6, NOT REFLECT ACTUAL CONDITIONS.
4) PROPERTY BOUNDARY SURVEY BY JAMES L. WRIGHT DATED NOVEMBER 1984. ITS
\� ,..°°„ � � °"•"'°" �n— '�, '/ � `,� ��--- __ ' - — - � � �\ � — �� � �,, i� I, __ _ _ ,r '� � LOCATION IS RELATIVE TO TOPOGRAPHY APPROXIMATE BY HDR ENGINEERING, INC.
_;, _ �, ------ --�- -- � � � � �� --� - � A IMA G OC ��// ��
D ��
�\ A G 5) TOPOGRAPHY BASED ON AERIAL SURVEYS BY LINDAIR SURVEYING ON MAY 10,
2000, AND CARTOGRAPHIC AERIAL MAPPING ON JANUARY 13, 2005.
0
R 6) MONITORING WELLS MW-1 THROUGH MW-5 SURVEYED JUNE 1987 BY S&ME, INC.
[U EO
nv.unn
Y°TE MONITORING WELLS MW-6 THROUGH MW-16 SURVEYED APRIL 1995, SEPTEMBER 1996,
GROUND OBSCU EO
SEE ACCURACY OTE �. �- I rc°�•,� - AND APRIL 2003 BY HDR ENGINEERING INC./ ED BUCKNER RLS.
1 S -- -�� �1�3 u6/L � 0 8 A4�';`�flZ(1� � \ i��� `'� � ss a•..• �'r i�� s�
N W- P-1
6 B
_ Np�1
O I I jell
ff MW- D` GP- \
N [�
IND OBSCURED
ACCURACY NOTE
���"° \ �\ t 4� ``'� ` \ l l°•., \O I 7) THE LOCATIONS OF LANDFILL GAS TRENCH VENTS ARE APPROXIMATE.
�Iw-14 D 8) VOC DATA FOR WELLS MW-1 1 D, MW-13D, AND MW-16D WERE NOT USED IN THE
�/1W-14 8 \ °•°°„ ' I a ' I° ° 1 o o CONSTRUCTION OF ISO -CONCENTRATION CONTOURS SINCE THEY ARE NOT SCREENED IN
I
THE SHALLOW AQUIFER.
/ / I�� A •�� ��� Mw\1 6 .� °Mw . ��� �� 9) A STREAM DETERMINATION WAS CONDUCTED ON APRIL 17, 2013 BY A GOLDER
oMW.3u- �y`" DI" a. \ I \ i ASSOCIATES NCB, INC. REPRESENTATIVE. THE STREAM DETERMINATION WAS CONDUCTED
1/L ` a . w- USING NC DWQ S METHODOLOGY FOR IDENTIFICATION OF INTERMITTENT AND PERENNIAL
G STREAMS AND THEIR ORIGINS, VERSION 4.1 1 .
10) ND = NON -DETECT
a
7)
w
"8
OM m•° °°„ � , - _ 11) J = ESTIMATED (I.E., NON -QUANTIFIABLE)
\, ND _ RESULT
12) VOC RESULTS ARE FROM THE RECENT WATER QUALITY MONITORING EVENT
(NOVEMBER 2019 AND JANUARY 2020 VERIFICATION SAMPLING EVENT)
13) GROUNDWATER CONTOURS SHOWN ARE AS MEASURED ON NOVEMBER 19, 2019.
P-12
13
W-2
W 0 400 800
..� 00
SCALE FEET
NC 2L = 0.03 mg/L
VINYL CHLORIDE CONCENTRATION GROUNDWATER SURFACE CONTOURS
CLIENT
MOORE COUNTY, NORTH CAROLINA
MOORE COUNTY LANDFILL, NCSWP NO. 63-01
ABERDEEN, NORTH CAROLINA
CONSULTANT YYYY-MM-DD
PG C-399 PREPARED
SOLDER DESIGN
REVIEW
GOLDER ASSOCIATES NC, INC. APPROVED
2020-01-07
BSD
NTT
DYR
RPK
PROJECT
MOORE COUNTY LANDFILL
CORRECTIVE ACTION EVALUATION UPDATE
TITLE
RECENT VOC NC 2L EXCEEDANCES (NOVEMBER 2019)
PROJECT No. PHASE No. DRAWING
19127463 100 0 2

FIGURES

atural Attenuation
Interpretation
Score
To INPUT
Screening
Inadequate evidence for anaerobic biodegradation' ofchlorinated organics
0105
Limited evidence for anaerobic biodegradation' ofchlorinated organics
6 to 14
Protocol
Score: 11
T1,V1 ­istekenh—M,usaPAptud[uisEM
199ej. TM1e.�ul4oftM1issw.ing
Adequate evidence for anaerohic hiodegradation'ofchlorinated organics
151020
po�M1eve no.eBula[wy
:�gnin�n�
Scroff to End of Tabfe
Strong evidence for anaerohic hiodegradation' of chlorinated organics
>20
�.ea�aiVeaecn�inffipn
Concentration in Points
Analysis Most Gontam. Zone Interpretation Yes do Awarded
Oxygen'
<0.5 mg/L
Tolerated, suppresses the reductive pathway a1 higher
0
concentrations
> 5mg/L
Not tolerated, however, VG may be oxidized aerobically
0
Nitrate`
<1 mg/L
At higher concentrations may compete with reductive
0
pathway
Iron II'
>1 mg/L
Reductive pathway possible, VC may be oxidized under
3
Fe(III)-reducing conditions
Sulfate'
020 mg/L
At higher concentrations may compete with reductive
f
0
pathway
Sufde'
>1 mg/L
Reductive pathway possible
r
0
Methane'
>0.5 mg/L
Ultimate reductive daughter product, VC Accumulates
0
Oxidation
<50 millivolts (mV)
Reductve pathway possible
1
Reduction
<-100mV
Reductive pathway likely
C
0
Potential' (ORR)
pH'
5 < pH < g
Optimal range for reductive pathway
O
0
TOG
>20 mg/L
Carbon and energy source, drives dechlorination; can he
r
Q
2
natural or anthropogenic
Temperature'
>20'G
At T >20'G biochemical process is accelerated
0
Carbon Dioxide
>2x background
Ultimate oxidative daughter product
C
0
Alkalinity
>2x background
Results from interaction of carbon dioxide with aquifer
e
1
minerals
Chloride`
>2x background
Daughter product of organic chlorine
e
2
Hydrogen
>1 nM
Reductive pathway possible, VG may accumulate
r
0
Volatile Fatty Acids
>0.1 mg/L
Intermediates resulting from biodegradation of aromatic
r
0
compounds, carbon and energy source
BI EX.
>0.1 mg/L
Carbon and energy source, drives dechlorination
r
0
PCE'
Material released
r
0
TGE'
Daughter product of PCE
0
DCE'
Daughter product of TGE.
If cis is greater than 80% of total DGE it is likely a daughter
G
Q
2
product of TCE� , I ,1-DCE can be a Chem. reaction product of TCA
VC'
Daughter product of DCE'
r
0
1,1,1-
Material released
r.
0
Trichloroethane'
DCA
Daughter product of TGA under reducing conditions
r
0
Carbon
Material released
r
0
Tetrachloride
Ghloroethane'
Daughter product of DCA or VC under reducing conditions
r
0
Ethene/Ethane
>0.01 mg/L
Daughter product of VG/ethene
r
0
>0_11 mg/L
Daughter product of VG/ethene
r
0
Chloroform
Daughter product of Carbon Tetrachloride
r,
d
0
Dichloromethane
Daughter product of Ghloroform
r
0
' requ¢ed analysis.
a! Points awarded wily if ft can be shown that the compound is a daughter product TO INPUT SCORE Reset
(i.e., not a constituent of the source NAPL).
DATE:01/07/2020
Title:
MW-4 EPA NATURAL ATTENUATION
Figure
Project #: 19127453
GOLDEF
SCREENING PROTOCOL WORKSHEET
"�
Prepared By: ESV
Moore County Landfill, NC Solid Waste
Permit No. 63-01
1
Reviewed By: BSD

Natural Attenuation
Interpretation
Score
TO INPUT
Screening
Inadequate evidence far anaerohic hiodegradation' ofchlorinated organics
0 to 5
Limited evidence for anaerohic hiAegradaticn" ofchlorinated organics
6 to 14
Protocol
.Score: 22.
Tnerouo.��q �a�e�nommeussar. potoml ,usaa�,
Adequate evidence for anaerohic hiodegradation' ofchlorinated organics
15 to 20
usasl. Tne.g�i4mm�:w���e p.nres nave ��Ea�isu�ry
Strong evidence for anaerobic biodegradation' ofchlorinated organics
>20
Scroll to End of Table
• ed�d'�deda'�m'o�
Concentration in Points
Analysis Most Contam. Zone Interpretation Yes No Awarded
Oxygen'
<0 5 mg/L
Tolerated, suppresses the reductive pathway at higher
;
d
3
concentrations
> 5mg/L
Not tolerated, however, VC may be oxidized aerobically
C
0
Nitrate'
<1 mg/L
At higher concentrations may compete with reductive
ce
Q
2
pathway
Iron II'
>1 mg/L
Reductive pathway possible, VG may be oxidized under
Q
3
Fe(III)-reducing conditions
Sulfate`
<20 mg/L
At higher concentrations may compete with reductive
p
0
2
pathway
Suede'
>1 mg/L
Reductive pathway possible
e
0
Methane'
>0.5 mg/L
Ultimate reductive daughter product, VG Accumulates
0
Oxidation
<50 millivolts (mV)
Reductive pathway possible
d
1
Reduction
<-100mV
Reductive pathway likely
e
2
Potential' (ORP)
pH'
5 < pH < g
Optimal range for reductive pathway
G
0
TOC
>20 mg/L
Carbon and energy source; drives dechlorination; can be
2
natural or anthropegenic
Temperature'
>20'G
At T >20'C biochemical process is accelerated
0
Carbon Dioxide
>2x background
Ultimate oxidative daughter product
e
Q
0
Alkalinity
>2x background
Results from interaction of carbon dioxide with aquifer
Q
1
minerals
Chloride'
>2x background
Daughter product of organic chlorine
2
Hydrogen
>1 nM
Reductive pathway possible, VG may accumulate
0
Volatile Fatty Acids
>0.1 mg/L
Intermediates resulting from biodegradation of aromatic
0
compounds, carbon and energy source
BTEX'
>0.1 ri
Carbon and energy source, drives dechlorination
0
PCE'
Material released
C
d
0
TCE'
Daughter product of PCE
e
0
DCE'
Daughter product of TCE_
If cis is greater than 80% of total DCE it is likely a daughter
G
(
2
product of TCE",1,1-DCE can be a chem. reaction product of TCA
VC'
Daughter product of DCE
2
1,1,1-
Material released
0
Trichloroethane'
DGA
Daughter product of TCA under reducing conditions
0
Carbon
Material released
Q
0
Tetrachloride
Chloroethane'
Daughter product of DGA or VC under reducing conditions
O
0
Ethane/Ethane
>0.01 ri
Daughter product of VC/ethene
0
>0.1 mg/L
Daughter product of VC/ethene
0
Chloroform
Daughter product of Carbon Tetrachloride
e
0
Dichloremethane
Daughter product of Chloroform
0
' requ ied analysis.
w Points awazded only if k can be shown that the compound is a daughter product TO INPUT SCORE Reset
(i.e., not a constituent of the source NAPL).
DATE:01/07/2020
Title:
MW-11SR EPA NATURAL ATTENUATION
Figure
G 0 L D E R
Project
SCREENING PROTOCOL WORKSHEET
No.
Prepared By: ESV
Moore County Landfill, NC Solid Waste
Permit No. 63-01
2
Reviewed By: BSD

Natural Attenuation
Interpretation
Score
Screening
Inadequate evidence for anaerobic biodegradation' ofchlorinated organics
0to5
Limited evidence for anaerobic biodegradation' of chlorinated organics
6 to 14
Protocol
Score: 23
the 11—,A is takes r,om me usePA p, t—l(usePA. aeaef.
The re�l�so�thissmring process h—no regul d.,
Adequate evidence for anaerobic biodegradation' of chlorinated organics
15 to 20
Strong evidence for anaerobic biodegradation' or chlorinated organics
>20
slpnaica°oe_
Scroll t0 End of Table
` redudive decHonna�ion
Concentration in Points
Analysis Most Contam. Zone Interpretation Yes No Awarded
Oxygen'
<0.5 mg/L
Tolerated, suppresses the reductive pathway at higher
41
0
3
concentrations
> 5mg/L
Not tolerated; however, VC may be oxidized aerobically
0
Nitrate'
<1 mg/L
At higher concentrations may compete with reductive
�.
2
pathway
Iron II"
>1 mg/L
Reductive pathway possible; VC may be oxidized under
3
Fe(Ill)-reducing conditions
Sulfate'
<20 mg/L
At higher concentrations may compete with reductive
0
2
pathway
Sulfide'
>1 mg/L
Reductive pathway possible
®
0
Methane'
>0.5 mg/L
Ultimate reductive daughter product, VC Accumulates
o
3
Oxidation
<50 millivolts (mV)
Reductive pathway possible
1
Reduction
®
Potential' (ORP)
<-100mV
Reductive pathway likely
O
2
pH'
5 < pH < 9
Optimal range for reductive pathway
0
TOC
>20 mg/L
Carbon and energy source; drives dechlorination; can be
0
natural or anthro o enic
®
Temperature'
>20°C
At T >20°C biochemical process is accelerated
0
Carbon Dioxide
>2x background
Ultimate oxidative daughter product
0
Alkalinity
>2x background
Results from interaction of carbon dioxide with aquifer
0
1
minerals
Chloride'
>2x background
Daughter product of organic chlorine
o
2
Hydrogen
>1 nM
Reductive pathway possible, VC may accumulate
o
®
0
Volatile Fatty Acids
>0.1 ni
Intermediates resulting from biodegradation of aromatic
0
compounds; carbon and energy source
BTEX'
>0.1 ni
Carbon and energy source; drives dechlorination
0
PCE'
Material released
,.
0
TCE"
Daughter product of PCE
o
0
DCE"
Daughter product of TCE.
If cis is greater than 80% of total DCE it is likely a daughter
+.
O
2
product of TCEs`;1,1-DCE can be a them. reaction product of TCA
VC`
Daughter product of DCE
C7
2
1,9,1-
Material released
0
Trichloroethane"
DCA
Daughter product of TCA under reducing conditions
0
Carbon
Material released
0
Tetrachloride
Chloroethane'
Daughter product of DCA or VC under reducing conditions
0
Ethene/Ethane
>0.01 ni
Daughter product of VC/ethene
0
0
>0.1 ni
Daughter product of VC/ethene
9
0
Chloroform
Daughter product of Carbon Tetrachloride
0
Dichloromethane
Daughter product of Chloroform
0
* required analysis.
al Points awarded only if it can be shown that the compound is a daughter product SCORE Reset
(i.e., not a constituent of the source NAPL).
End of Form
DATE:01/07/2020
Title:
MW-6 EPA NATURAL ATTENUATION
Figure
Project #:19127453
G0LDEI
SCREENING PROTOCOL WORKSHEET
"�
Prepared By: ESV
Moore County Landfill, NC Solid Waste
Permit No. 63-01
3
Reviewed By: BSD

---N—at—ural Attenuation
Interpretation
Score
TO INPUT
Screening
Inadequate evidence for anaerobic hiodegradaten` afchlorinated organics
0 to 5
Limited evidence for anaerobic biodegradation' ofchlorinated organics
6 to 14
Protocol
Score: 23
rherouom­
nasal. --IN rh,:no iardv
Adequate evidence for anaerobic biodegradation' of chlorinated organics
15 to 20
Strong evidence for anaerobic biodegradation' of chlorinated organics
>20
see �,fi
Scroll to End of Tabfe
Concentration in Points
Analysis Most CDntam Zone Interpretation IN Yes o Awarded
Oxygen'
<0.5 mI
Tolerated, suppresses the reductive pathway at higher
r;
Q
3
concentrations
> 5mg/L
Not tolerated, however, VC may be oxidized aerobically
0
Nitrate'
01 mg/L
At higher concentrations may compete with reductive
C
Q
2
pathway
Iron II'
>1 mg/L
Reductive pathway possible, VC may be oxidized under
O
Q
3
Fe(III)-reducing conditions
Sulfate'
<20 mg/L
At higher concentrations may compete with reductive
Q
Q
2
pathway
Sul fide'
>1 mg/L
Reductive pathway possible
G
0
Methane'
>0.5 mg/L
Ultimate reductive daughter product, VC Accumulates
G
3
Oxidation
<50 millivolts (mV)
Reductive pathway possible
Q
1
Reduction
<-100mV
Reductive pathway likely
r;
Q
2
Potential' (ORP)
pH'
5 < pH < g
Optimal range for reductive pathway
Q
0
TOG
>20 mg/L
Carbon and energy source, drives dechlonnation; can be
D
0
natural or anthropogenic
Temperature'
>20'C
At T >20'C biochemical process is accelerated
0
Carbon Dioxide
>2x background
Ultimate oxidative daughter product
r
0
Alkalinity
>2x background
Resulls from interaction of carbon dioxide with aquifer
Q
1
minerals
Chloride'
>2x background
Daughter product of organic chlorine
r,
0
Hydrogen
>1 nM
Reductive pathway possible, VC may accumulate
r
0
Volatile Fatty Acids
>0.1 mg/L
Intermediates resulting from biodegradation of aromatic
0
compounds, carbon and energy source
BIFX'
>0.1 mg/L
Carbon and energy source, drives dechlorination
0
PCE'
Material released
C
d
0
TCE'
Daughter product of PCE
r
0
DCE'
Daughter product of TCE.
If cis is greater than 80% of total DCE it is likely a daughter
G
Q
2
product of TGE"; I J-DGE can be a Chem. reaction product of TCA
VC'
Daughter product of DCE`
Q
2
Material released
r
0
Trichloroethane'
DCA
Daughter product of TCA under reducing conditions
Q
2
Carbon
Material released
0
Tetrachloride
Ghloroethane'
Daughter product of DGA or VC under reducing conditions
0
Ethene/Ethane
>0.01 mg/L
Daughter product of VC/ethene
r
Q
0
>0.1 mg/L
Daughter product of VC/ethene
r
r
0
Chloroform
Daughter product of Carbon Tetrachloride
r
e
0
Dichloromethane
Daughter product of Chloroform
r
G
0
'required analysis_
a/ Points awarded only if it can be shown that the compound is a daughter product TO INPUT SCORE Reset
(i c., not a constituent of the source NAPL).
DATE: 01/07/2020
Title:
MW-15R EPA NATURAL ATTENUATION
Figure
G 0 L D E R
Project#: 19127453
SCREENING PROTOCOL WORKSHEET
No.
Prepared By: ESV
Moore County Landfill, NC Solid Waste
Permit No. 63-01
4
Reviewed By: BSD

BIOCHLOR Natural Attenuation Decision Support System Moracounry Data Inputlostructiane:
Vwsmn T? LwndAtl Nor 2❑19 ,. -, Eller "*4 di'" a
Ezcef 2❑00 fB., N.v T'a 2. CBkdmehy Tinpnl7roy
HYPE OF C LVRPMTED SOLVENT EOlerl06 6- 6ENERAl 0j OR2 ,ut. P-Enuar. clen J
EpI6riY.S C 5r,a+YHm Tune' ill (Yh �L - CFO Tease Lorrrr4,, MThp FMIXAW tuan;
,. ACIVIE TUO a .. _ _.. r. MmAo odd oe W41n• ,raw (0) ", 1y Va,- Dabs vow ar adeI RTN
SuapepD VdoODy' Va - 3W 4 Wyo J Modobd A(04 L.00- 29IX1 IS) 1 TOM r�yrN +FganwMwn
Iw,9 1 LBnpSM' 2900 IN Zw 2 ,orme6 � � � Promm
i vd.N OvnducIrwy rc S.SE-0S (emus) lone 2 Lerq❑M' ❑ f0] L -Zone 1
HroreD OTad,e-D D.tl2v7 ln1
[11DcD.o Po.oxdy n 8.95 (-] F- Sol)RC6 DATA --Tyn Lynwuow, Verwar Prw Sow". D6rNRND6 Sw a Wet
2. DISPERIPON Sir* Planes .' Loce6On end Input SO}.Hn1 CMwenlra,bns
Alpha x. 18 I1) Gk _ Iran [lonnnc
r,'*na y]+(A,Pke x]' I.E {-] Swrce hack- n 8s. ibne' 55 [1t1
{apse r)r fW. •]' 9E-DT •] _ Y,
S. ALISPRP1toN WrrP• SAY IBDD = -
Rasudalmn F--- - .1
Care CI [,FYr1
5.46uk Nibs rho 1-6 ft.t1 PCE .017 0
FrKi-Org-ra"ru" Too 1.8E-8 [-) TCE 0, 0 Views DF FI1.0a L�9 Dam
PeM,en Cnp[6e,ml KDc y OCE 029 0
PCE 42B (L.'Lg]M
S•1 VC 05B D obwwd Ca,www COIor.■moo" w4b
TCE 100 [ M91[•1 EDI d 0
DCE 1P5 [LlIU](-1
VC 30
[I,.Drg]S-1 T. F r"VCW17AFOR _F.TI[ 302 [I.rogl[•1 POE Cone orkwL)
R TCE CenY;. (mpL]
4. MOTRANSFORWLTION .,NOT [DiMm Co�llo w j.E CMG. {ttq ,)
Z-1 1 her Her YW VC Ca,c- 1
PCE -y TCE O.BOv (- S.OD a i8 EfN 1AM.. 1*01
TCE -I DLE ^❑top t- 1,00 D74 :��a.,ro:r-•rnr
OCE i VC D eve t- ,.SD o6e nax� na,e rw�:s.l 2me
VC ETH
❑ hDD t- 8.00 00 8. CHOOSE TYPE OF OIt TPUT TO SEE:
INKY 2 1 IMF Ye
POE 9P TCE Davo f -s.00 RUN Help FN�Dna F7E6E'f
J7CE T OCE ❑3Dp s< HELP RUN ARRAY
OCE VC 7 �- [ gp CENTERLINE
VC ETH •0500 t- 8_00 SEE F'.64e Unprcgcl
-tDI-VED CHIORD-0 SOLVENT CORCEHTRAnroH$ ALOHO PWYS %HTSRLOHi(mgL] RA0
Groot. `-
PCs o tvv seo aTv +,ev +¢o Tres xwv sxa ss+e seDo
--------w
He v.R.e.ven
eenRwN.Far� n vmv �a om o i
Fud Ouu Vui am I am I 00.T0 C.O .
�H. o.rRe.,.rv�m,�-s.wrmr,.cw.DN.r . R.uva.,ran.sr.
r vvc a.. Pu
D,oD
fr TCE
� ndrD root
r500 2W0 2h00 mpm D.•00
Awl 2BW ��
oi.l.nce Fran Swrar Itt.}
61OCHLID R Natu rei Attenuation Decision Support System Frno Crony Data Input Ineuvchons:
VMsmn 5 2 Lant1AN INw 201% 115 •1 Ifni-s d,rKily or
Cxc.r! PDDO qrr rrenr 4 n _ 2 yylo by rffi ir, gray
TYPE OF CHLORINATED SOLVENT. EMara<a c 6- GENERAL L 0.02 cos Pr0S5 Enlor Fran J
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APPENDIX A
GROUNDWATER AND SURFACE WATER SAMPLING
LOGS

DATE: "
_.� G 0 L D E P GROUNDWATER SAMPLING LOG
Project Name:
Moore County Landfill
Project No./Phase No.:
19127453
Well ID:
eA W
Sampler(s): E. Vasko
v
Well Diameter:
2 inches
Initial Depth to Water:
f 7 , [3 feet
Depth to Bottom: 2 2 -o i feet
Water Column Thickness:
S,00 feet
Pumping Rate:
I ?-0—,lo c mUmin.
System Volume:
3 4 7_ mL
Equipment:
YSI Pro Plus, Hach 2100Q, Water Level Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 0.2 ± 20 (± 10 ideal)
• •
,is ' •
• '
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: Iecc -,,ei :Lt tom,
Signature:
QA/QC Sign Off:
Date: 4 / Z_ a f 11
Date: Z-IL-1- 207 0
r'6r E- lYc

DATE:
GOLDER
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill
Project No./Phase No.:
19127453
Well ID: NI \J� T
Sampler(s): E. Vasko/
NT^0 T^r-�
Well Diameter:
2 inches
Initial Depth to Water:
! 6
feet
Depth to Bottom: Z t
, °( '2 feet
Water Column Thickness:
S . ts
feet
Pumping Rate:mL/min.
System Volume:
"L 7E.
mL
Equipment: YSI Pro Plus,'
aQ, Water Level Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 0.2 ± 20 (± 10 ideal)
Time
pH
S.U.(US/cm)
Sp. Cond.
Turb
NTU)
Dis 02
(m /L
Temp.
°C
ORP
millivolts
DTW
feet
OC 3t,
r<..ZC,
tLcii
C� -'
l'
3�'
1-27
[" C
so
t r).
0
t 7,S
Q 4-
Z 2
S'
0 3
4-
Z 7, C,I
S L
►�c
�.30
r)C
4--
�.S
+z.
_37
7 4-6
tG
G-3t
<173
0
l
o �'
I
/G45
4- Z
?
-' U- c
t 7,
LlZ`
, 33
-7
i I io
Z
f )-3
7,Ci
fzs
l 4.Cn
7 3?
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: C 516('t S
Begin purging @ b `) 7 C
i
Signature: C�-�'V -V 1�� Date:
�—
QA/QC Sign Off: /t Date: I y U ��

DATE: Z -
GOLDE
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: h1 �- Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: z - > t feet
Depth to Bottom: 37 _ j 1� feet Water Column Thickness: , 0 feet
Pumping Rate: t 0, 0 mL/min. System Vq)lume�.. �J yam- 7 �' mL
Equipment: YSI Pro Plus, Hach 2900Q, Water Level Meter,Pump,-Pet#e-8a#tey� �1t'rs
±0.1 +5% <10 +ino/ nrn9
+ 9n f+ in „ion
Time
pH
S.U.
Sp. Cond.
US/cm
Turb
NTU
Dis Oz
m /L
Temp.
°C
ORP
millivolts
DTW
feet
C-ail:s
c,,4-'Q
iS" 4'
fr,'%
-7()
r�c,C'
fiS'•
Z4- -
U(l8
L 4-
L=
i S
�C
i
''
2
(Jot Z 3
c 9-t
j 4 5
( 3
C. '
ICA,Z
4-
Z 4 .22.
C% 2
,
Z
'$,7S
c I
.--Z 01,y
z I
('�33�
S
to
-7 �
0,3i
a,Z
-7�''-7
`Q Zz
l 3r
c
��
'-7
T
W(eZ' I
5'-3
C S�'
3-7
Si
c�.^�
iG
'�31.(
2.
oL V
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: Ci c ^ ,Y
Begin pur in @ 0-
Fe= _ S ---- -
Signature:
QA/QC Sign Off:
Date: H Z -(
Date: 7-H-Z02b

DATE: jk-&l Lj
. GOLDER
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: _ _ _11 - t( -0- Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: _Uc3 feet
Depth to Bottom: gl .6L _feet Water Column Thickness: 1 S. ro 2 feet
Pumping Rate: Zn6cD mL/min. System Volume: 3 q mL
Equipment: YSI Pro Plus, Hach 2100Q, Water Level Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 0.2 ± 20 (± 10 ideal)
Sp. Cond.
' •
• - •
Comments (,weather conditions, color, type of sample, purge -water management, etc.):
Weather: 1VII , W lh Guy _._...
Begin Rurging @ 32,a
Fe 41111.4 GG
Signature: ����/%/'� �� Date:
QA/QC Sign Off: - Date: ILI-2e�

DATE: k � - 7_.0 "
GOLDER
GROUNDWATER SAMPLING LOG
Project Name:
Moore County Landfill
Project No./Phase No.:
19127453
Well ID:
J,W - lk V(2-
Sampler(s): E. Vasko /
N. Tejeda - Torres
Well Diameter:
2 inches
Initial Depth to Water:
1G Z.( feet
Depth to Bottom: 4G F,Z feet
Water Column Thickness:
0.4-1 feet
Pumping Rate:
k mUmin.
System Volume:
¢ST mL
Equipment:
YS/ Pro Plus, Hach_ 2100Q, Water Level
Meter, Peristaltic Pump, Portable Battery
+ 0 1 +q <1n +1n0/ nrn9 +7n r+in iri—n
P. Cond.
, •
• -
---�---
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: ,"h mv)i, Vvn _a►n `� A
Begin purging @
Fe =
Signature: /, Date:
QA/QC Sign Off: ��- Date: 2 - / y -20 7 cj

DATE: Z.1 - (9
GOLDER
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: W'J - %vS Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: ,_ l feet
Depth to Bottom: ZI cx> feet Water Column Thickness: TS feet
Pumping Rate: ZZ d mUmin. System Volume: 3 ¢g- mL
Equipment: YS/ Pro Plus, Hach 2100Q, Water Level Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 0.2 + 20 1+ 10 idpnh
MOMIM""M
M,�M
Dis 02
---win
ft—b"M
M�
�—
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather:, w,
Begin purging @ IWO _..
Fe = G.$
Signature: / Z'b!/ Date:
/.�
-1Lj_ Z
QA/QC Sign Off: /`'" Date: oZ �'

DATE: iI -Z(-Iq
GOLDER
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: i{c. W feet
Depth to Bottom: q5 feet Water Column Thickness: ?- S .4 S feet
Pumping Rate: 200 mL/min. System Volume: *37 mL
Equipment: YS/ Pro Plus, Hach_ 2100Q, Water Level Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 0.2 + 2n f+ in moan
Time
pH
S.U.
Sp. Cond.
uS/cm
Turb
NTU
Dis 02
m /L
Temp.
°C
ORP
millivolts
DTW
feet
(
5T. q
6 26
O.
1 i
%52o
16 .to
522
1.
Z((
a
112Z
(so •
b t Z
.02.
5'4_1
0.n
l' I
t 51 3
6_ Z
hJ3
.(6
is, i
tom.
. t
t g
5 Z6
45,0
1.1-4
10.1
0G,
1 G
53
S.ZB
G
0-14
k4t.
i
t
5.Zq
Go.Z
lk.v
0.16
1 S
14%.3
6.
0-14
i 83
141.s
i
1 i
3Z
34.1
U.
tS
i39. 4
(e, I
lZc
zq
CMG 3
13.E
0 l
$. I
(3G .CA
ic. ,
►Z�a
5 3►
GO. 2
6.1 e
0 k0
IS z
1S
►� ti
i
9
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: SJu2A ,
Begin pur in 1120
Fe
Signature:, Date: ((- Z (- t `t
__ 2-1N 2vZ0
QA/QC Sign Off: � Date:

DATE: --
GOLDEN
GROUNDWATER SAMPLING LOG
Project Name:
Moore County Landfill
Project No./Phase No.: 19127453
Well ID:
ICJ- (
Sampler(s): E. Vasko
Well Diameter:
2 inches
Initial Depth to Water: (
feet
Depth to Bottom: Z feet
Water Column Thickness: 2
feet
Pumping Rate:
S mL/min.
System Volume: I
mL
Equipment:
YSI Pro Plus, Hach 2100Q, Water Level
Meter, Peristaltic Pump, Portable Battery
± 0.1 ± 5% <10 ± 10% or 02 ± 20 ± 10 ideal
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather:
Begin eurgin2 @ (G'Z"7
11
Signature:
QA/QC Sign Off: y/L"
Date: � '- M1 1 C
T
Date: , I Y 2 , , 0

„,)10 G0LDFR
DATE: ' , r-Z l
GROUNDWATER SAMPLING LOG
Project Name:
Moore County Landfill
Project No./Phase No.:
19127453
Well ID:
U �h_ `
Sampler(s): E. Vasko
E
Well Diameter:
2 inches
Initial Depth to Water:
, 5s — feet
Depth to Bottom:
G , _-7 feet
Water Column Thickness:
feet
Pumping Rate:
' 0t16)o mL/min.
System Volume:
_
mL
Equipment: YSI Pro Plus, Hach 2900Q, Water Level Meter, ,
± 0.1 ± 5% <10 ± 10% or 0.2 + 20 f+ in irleall
Time
pH
S.U.
Sp. Cond.
us/cm
Turb
NTU
Dis OZ
m /L
Temp.
°C
ORP
millivolts
DTW
feet
IC 2--(Zz
C'Y
S ' 4'
3
i
17 3
5-
s �
l 4
G
4-
, G
U ,
17. Z
S. "'
3s .
S
C
± c
S i
0,
17 5
- i 7
S Z
S• ic1
4 �-S
3
G,3"'
i7 4-
116,7
z b
�:
-3
3C
c,
, C
L t �'
Z_
Z
01 c''
3 �.,�'
2 7, l
e°� zr
<
-1l%
35' U!�b
5-
372.
,3c v
'ZS''
3 c
J-
_
3e 3
il: 3
(zc
-l2z.3
�3 /3
CSC
U ZQ
"z 3I
39-
�-
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: C L c 43
Begin purging @ I
Fe =
Signature: L/ Date:
l ��
QA/QC Sign Off:-� Date: Z �a

GOLDER
DATE: _ I l— I R -- l 9
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: 13 _ Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: I Z„ Zc feet
Depth to Bottom: ( 00 feet Water Column Thickness: feet
Pumping Rate: j , mL/min. System Volu i bkwWg# mL
Equipment: YS/ Pro Plus, Hach 2900Q, Water Level Meter,afr
± 0.1 ± 5% <10 ± 10% or 0.2 ± 20 (± 10 ideal)
Mom
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: C(c)"d- SOS
Begin purging @� 1 S
Signature:
QA/QC Sign Off:
Date: ( I- I q- l a
Date: ez — / t -Z c Z,0

GOLDER
DATE: k la — 20 _ tCi
GROUNDWATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Well ID: 11-o Sampler(s): E. Vasko / N. Tejeda - Torres
Well Diameter: 2 inches Initial Depth to Water: G feet
Depth to Bottom: '3Q . ejo feet Water Column Thickness: 't l . 0 feet
Pumping Rate: 12 0 mL/min. System Volume: 4-2-0 mL
Equipment: YS/ Pro Plus, Hach 2100Q, Water Level Meter, , P kct—
± 0.1 ± 5% <10 ± 10% or 0.2 ± 20 (± 10 ideal)
-------
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Weather: &vgVLq r kq4_, SZ).�
Begin purging @ l5yu
Fe = U. o
Signature: v"— Date: ZU
r
QA/QC Sign Off: Date:

DATE: I
G O L D E R SURFACE WATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Sample ID: .S W- ( Sampler(s): E. Vasko / N
Sampling Location:
Equipment: YSl Pro Plus, Hach 2100Q
Time
530
pH
s.u.
.$S
Sp. Cond.
US/cm
Turb.
ntu
�-
Dis.OZ
m /L
¢
0'4`
Temp.
'C
RvP m
�y Q
I TO p
Tejeda - Torres
Surface Water Sampling Location Sketch
5 w�'
13QCIr\
Comments (sample methodology, weather conditions, color, silt, etc.):
Weather: cIe4t- k�`cS = Z ;,iL
Flow: Good
Signature: �f/I/h G��GDate:
QA/QC Sign Off: � Date: 7 -fLf -ZUZt

G®LDER
DATE: I (-z l - IC(
SURFACE WATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Sample ID: j vi Sampler(s): E. Vasko / N. Tejeda - Torres
Sampling Location:
Equipment: YSI Pro Plus, Hach 2100Q
Time
pH
S.U.
Sp. Cond.
US/cm
+� (�
Turb.
ntu
7,3k
Dis. 02
m /L
35
Temp.
ORP
my
��0
Surface Water Sampling Location Sketch
Comments (sample methodology, weather conditions, color, silt, etc.):
Weather: d ea:___51 ,_-, s
Flow:
Signature:
QA/QC Sign Off:
Date: 11-Zl-lq
Date: 2"iy "z o? o

DATE:
SURFACE WATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Sample ID: 5 i" ; Sampler(s): E. Vasko / N. Tejeda - Torres
Sampling Location:
Equipment: YSI Pro Plus, Hach 2100Q
Surface Water Sampling Location Sketch
N� �v�Z
Time 177
pH
S.U.
�
Sp. Cond.
US/cm
,
Turb.
ntu
Z0 3
Dis. OZ
m /L
Temp.
p.
ORP
my
,
l�
N
N
/`\",-\3
1
Comments (sample methodology, weather conditions, color, silt, etc.):
Weather: CfcvdS rA M—) A,� -/- _-11 <.
(-Zt-cC(
2 "�q
QA/QC Sign Off: /�- ��� Date: �cGD
(u 4�_

G 0 L D E R
DATE: I (- 2 1 Icf
SURFACE WATER SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Sample ID: _S L,,)- 4L- Sampler(s): E. Vasko I N. Tejeda - Torres
Sampling Location:
Equipment: YSI Pro Plus, Hach 2100Q
Time
L�-
pH
s.u.
Sp. Cond.
us/cm
5�'s
Turb.
ntu
,
Dis. OZ
m /L
' 35
Temp.
cc
i 3,
ORP
my
_ f3
Surface Water Sampling Location Sketch
Comments (sample methodology, weather conditions, color, silt, etc.):
Weather: C
Flow:
Signature: L� - Date:
QA/QC Sign Off: Date:

G®LDEP
DATE:
f SAMPLING LOG
Project Name: Moore County Landfill Project No./Phase No.: 19127453
Sample ID: 61 Cam. L 7 zs, Sampler(s): E. Vasko /-A1.1'p�p�_ 4*ms
Sampling Location: (,F- or c F s^: ,� U!�✓��
Equipment: YS/ Pro Plus, Hach 2100Q
Time
p H
S.U.
Sp. Cond.
US/cm
2
Turb.
ntu
+ G
Dis. OZ
m /L
Temp.
cc
S. f
ORP
my
'P- C :
Surface Water Sampling Location Sketch
Comments (sample methodology, weather conditions, color, silt, etc.):
Weather: /�rsk; c y
*k"7---�
Signature: Date: - G ~ tq
QA/QC Sign Off: Date: ",?' l y- Z p z d

DATE:y�1l ; L i;�2o
GOLDER
Project Name: N 94. L":
Well ID:
Well Diameter: 2 inches
Depth to Bottom: `7(s,2i feet
Pumping Rate: E j mUmin.
GROUNDWATER SAMPLING LOG
Project No./Phase No.: 4\iZ- 4`-a_
Sampler(s): i I(A-Ccrfet
Initial Depth to Water: ' .`i2 S feet
Water Column Thickness: feet
System Volume:
Equipment: Turbidimeter, YSI Profts. WL Meter
MP-15 nr v iriblx bit l'bC'1
Comments (weather conditions, color, type of sample, purge -water management, etc.):
Date: C� 1
Signature:
Date:
QA/QC Sign Off: vY

APPENDIX B
NOVEMBER 2019 AND JANUARY 2020
GROUNDWATER AND SURFACE WATER
CERTIFICATE -OF -ANALYSIS, CHAIN -OF -CUSTODY
FORMS AND LABORATORY DATA REVIEW

2�SQ ENCO Laboratories
9g
Accurate. Timely. Respousive. luuavative.
102-A Woodwinds Industrial Court
Cary NC, 27511
Phone: [phone] FAX: [phone]
Friday, December 13, 2019
Golder Associates, Inc. (GO007)
Attn: Ben Draper
5B Oak Branch Drive
Greensboro, NC 27407
RE: Laboratory Results for
Project Number: 19127453.100, Project Name/Desc: Moore Co LF
ENCO Workorder(s): CC18640,CC19666
Dear Ben Draper,
Enclosed is a copy of your laboratory report for test samples received by our laboratory on
Friday, November 22, 2019.
Unless otherwise noted in an attached project narrative, all samples were received in
acceptable condition and processed in accordance with the referenced methods/procedures.
Results for these procedures apply only to the samples as submitted.
The analytical results contained in this report are in compliance with NELAC standards, except
as noted in the project narrative if applicable. This report shall not be reproduced except in
full, without the written approval of the Laboratory.
This report contains only those analyses performed by Environmental Conservation
Laboratories. Unless otherwise noted, all analyses were performed at ENCO Cary. Data from
outside organizations will be reported under separate cover.
If you have any questions or require further information, please do not hesitate to contact me.
Sincerely,
Stephanie Franz For Meghan K Shea
Project Manager
Enclosure(s)
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 1 of 56

PROJECT NARRATIVE
Date:
13 December 2019
Client:
Golder Associates, Inc. (G0007)
Project:
Moore Co LF
Lab ID:
CC18640, CC19666
Overview
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Environmental Conservation Laboratories, Inc. (ENCO) analyzed all submitted samples in accordance with the methods
referenced in the laboratory report. Any particular difficulties encountered during sample handling by ENCO are discussed in
the QC Remarks section below.
Quality Control Samples
The spike recovery of 1,4-Dioxane was outside of control limits for the 8260D SIM MS and MSD samples. The QC batch
was approved based on acceptable LCS recovery of this analyte.
The 8260D Continuing Calibration Verification sample (CCV) exhibited a high bias for 1,1,1-Trichloroethane,
1,1-Dichloroethane, Acetone, Acrylonitrile, Benzene, Bromochloromethane, Carbon Disulfide, Carbon Tetrachloride,
Chloroform, Chloromethane, cis- 1,2-Dichloroethene, lodomethane, trans- 1,2-Dichloroethene, Trichloroethene,
Trichlorofluoromethane, Vinyl Chloride, and Tetrahydrofuran. The LCS sample also exhibited a high bias for
Bromochloromethane. However, these analytes were not detected in the associated samples, reducing the impact of the
deviation.
The spike recovery of Iron was outside of control limits for the 601 OD MS, MSD, and Post Spike samples. The QC batch
was approved based on acceptable LCS recovery of this element.
The spike recoveries of Alkalinity, Chloride, Sulfate, and Sulfide were outside of control limits for the MS or MSD samples.
The QC batches were approved based on acceptable LCS recovery of these analytes.
Quality Control Remarks
No Comments
Other Comments
All samples received under this project arrived in acceptable conditions. The samples were not checked for residual chlorine,
as it is not required.
The analytical data presented in this report are consistent with the methods as referenced in the analytical report. Any
exceptions or deviations are noted in the QC remarks section of this narrative or in the Flags/Notes and Definitions section of
the report.
Released By:
Environmental Conservation Laboratories, Inc.
Stephanie Franz
Project Manager
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 2 of 56

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW13S
Lab ID: CC18640-01
Sampled: 11/21/19 10:35
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/03/19 21:55
12/03/19 21:55
EPA 310.2
NO PREP
12/05/19
12/02/19 13:13
12/02/19 13:13
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:27
EPA 6020B
EPA 3005A
05/19/20
11/26/19 10:07
12/02/19 19:36
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:39
EPA 8260D
EPA 5030B_MS
12/05/19
12/01/19 13:20
12/02/19 01:12
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 11:33
SM 254OC-2011
NO PREP
11/28/19
11/27/19 17:42
11/27/19 17:42
SM 4500S2 D-2011
NO PREP
11/28/19
11/23/19 14:42
11/23/19 14:59
Client ID: 6301-MW13S
Lab ID: CC18640-01RE1
Sampled: 11/21/19 10:35
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/05/19
12/05/19 14:08
12/05/19 19:06
Client ID: 6301-MW13D
Lab ID: CC18640-02
Sampled: 11/21/19 12:18
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/03/19 22:48
12/03/19 22:48
EPA 310.2
NO PREP
12/05/19
12/02/19 13:14
12/02/19 13:14
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:18
EPA 6020B
EPA 3005A
05/19/20
11/26/19 10:07
12/02/19 19:41
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:41
EPA 8260D
EPA 503013_MS
12/05/19
12/01/19 13:20
12/02/19 01:49
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 12:06
SM 254OC-2011
NO PREP
11/28/19
11/27/19 17:42
11/27/19 17:42
Client ID: 6301-MW13D
Lab ID: CC18640-02RE1
Sampled: 11/21/19 12:18
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 5030B_MIS
12/05/19
12/05/19 14:08
12/05/19 19:38
Client ID: 6301-SW1
Lab ID: CC18640-03
Sampled: 11/21/19 15:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:21
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:43
EPA 8260D
EPA 503013_MS
12/05/19
12/01/19 13:20
12/02/19 02:25
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 12:38
Client ID: 6301-SW2
Lab ID: CC18640-04
Sampled: 11/21/19 14:15
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:38
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:50
EPA 8260D
EPA 5030B_MS
12/05/19
12/01/19 13:20
12/02/19 03:01
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 13:10
Client ID: 6301-SW3
Lab ID: CC18640-05
Sampled: 11/21/19 15:10
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:33
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:52
EPA 8260D
EPA 5030B_MS
12/05/19
12/01/19 13:20
12/02/19 03:39
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 13:43
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in lull. I Page 3 Of 56

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-SW4
Lab ID: CC18640-06
Sampled: 11/21/19 14:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:35
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:55
EPA 8260D
EPA 503013_MS
12/05/19
12/01/19 13:20
12/02/19 04:15
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 14:15
Client ID: 6301-Field Blank
Lab ID: CC18640-07
Sampled: 11/21/19 13:25
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/03/19 23:06
12/03/19 23:06
EPA 310.2
NO PREP
12/05/19
12/02/19 13:14
12/02/19 13:14
EPA 6010D
EPA 3005A
05/19/20
12/02/19 09:35
12/05/19 14:41
EPA 6020B
EPA 3005A
05/19/20
11/26/19 10:07
12/02/19 19:45
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 15:57
EPA 8260D
EPA 503013_MS
12/05/19
12/01/19 13:20
12/02/19 04:51
EPA 8260D
EPA 5030B_MS
12/05/19
12/03/19 13:47
12/04/19 09:57
SM 254OC-2011
NO PREP
11/28/19
11/27/19 17:42
11/27/19 17:42
Client ID: 6301-Trip Blank
Lab ID: CC18640-08
Sampled: 11/21/19 10:35
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 5030B_MIS
12/05/19
12/01/19 13:20
12/02/19 05:28
EPA 8260D
EPA 503013_MS
12/05/19
12/03/19 13:47
12/04/19 10:29
Client ID: 6301-MW8
Lab ID: CC19666-01
Sampled: 11/20/19 10:25
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D
EPA 3005A
05/18/20
12/03/19 10:18
12/05/19 15:41
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:18
12/03/19 15:03
Client ID: 6301-MW8
Lab ID: CC19666-01RE1
Sampled: 11/20/19 10:25
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 5030B_MS
12/04/19
12/02/19 00:00
12/02/19 18:43
EPA 8260D
EPA 5030B_MS
12/04/19
12/03/19 13:49
12/04/19 14:52
Client ID: 6301-MW11DR
Lab ID: CC19666-02
Sampled: 11/20/19 11:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/04/19 04:42
12/04/19 04:42
EPA 310.2
NO PREP
12/04/19
12/02/19 13:22
12/02/19 13:22
EPA 6010D
EPA 3005A
05/18/20
12/03/19 10:18
12/05/19 15:43
EPA 6020E
EPA 3005A
05/18/20
12/02/19 10:57
12/03/19 15:03
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:18
12/03/19 15:06
EPA 8260D
EPA 5030B_MS
12/04/19
12/03/19 13:41
12/04/19 02:56
SM 2540C-2011
NO PREP
11/27/19
11/27/19 17:42
11/27/19 17:42
Client ID: 6301-MW11DR
Lab ID: CC19666-02RE1
Sampled: 11/20/19 11:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 5030B_MS
12/04/19
12/02/19 00:00
12/02/19 18:06
EPA 8260D
EPA 5030B_MS
12/04/19
12/03/19 13:49
12/04/19 15:23
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 4 Of 5G

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW17D
Lab ID: CC19666-03
Sampled: 11/20/19 15:25
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/04/19
04:59
12/04/19
04:59
EPA 310.2
NO PREP
12/04/19
12/02/19
13:22
12/02/19
13:22
EPA 6010D
EPA 3005A
05/18/20
12/03/19
10:18
12/05/19
15:52
EPA 6020B
EPA 3005A
05/18/20
12/02/19
10:57
12/03/19
15:08
EPA 7470A
EPA 7470A
12/18/19
12/02/19
12:18
12/03/19
15:08
EPA 8260D
EPA 5030B_MS
12/04/19
12/02/19
00:00
12/02/19
15:01
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19
13:41
12/04/19
03:28
SM 254OC-2011
NO PREP
11/27/19
11/27/19
17:42
11/27/19
17:42
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 5 Of 56

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW13S Lab ID: CC18640-01
Anala Results Flag MDL POLL Units Method Notes
1,4-Dioxane 6.0 0.80 2.0 ug/L EPA 8260D
Barium - Total 36.7 1.10 10.0 ug/L EPA 6010D
Chloride
11000
2200
5000
ug/L
EPA 300.0
Iron - Total
99700
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
189
1.50
10.0
ug/L
EPA 6010D
Sulfide
36
1
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
87000
14000
15000
ug/L
EPA 310.2
Total Dissolved Solids
110000
50000
50000
ug/L
SM 2540C-2011
Client ID: 6301-MW13S
Lab ID:
CC18640-01RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Benzene
1.1
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
2.1
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
1.1
0.15
1.0
ug/L
EPA 8260D
Vinyl chloride
0.70
1
0.32
1.0
ug/L
EPA 8260D
Client ID: 6301-MW13D
Lab ID:
CC18640-02
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dioxane
2.8
0.80
2.0
ug/L
EPA 8260D
Barium - Total
11.7
1.10
10.0
ug/L
EPA 6010D
Chloride
5400
2200
5000
ug/L
EPA 300.0
Copper - Total
2.75
1 1.60
10.0
ug/L
EPA 6010D
Iron - Total
6040
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
15.2
1.50
10.0
ug/L
EPA 6010D
Total Alkalinity as CaCO3
14000
1 14000
15000
ug/L
EPA 310.2
Client ID: 6301-MW13D
Lab ID:
CC18640-02RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
cis- 1,2-Dichloroethene
0.71
1
0.15
1.0
ug/L
EPA 8260D
Client ID: 6301-SW1
Lab ID:
CC18640-03
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
1.3
1
0.80
2.0
ug/L
EPA 8260D
Barium - Total
19.3
1.10
10.0
ug/L
EPA 6010D
Cadmium - Total
0.446
1
0.360
1.00
ug/L
EPA 6010D
Chlorobenzene
0.57
1
0.17
1.0
ug/L
EPA 8260D
Client ID: 6301-SW2
Lab ID:
CC18640-04
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
Arsenic - Total
9.27
1
7.60
10.0
ug/L
EPA 6010D
Barium - Total
13.9
1.10
10.0
ug/L
EPA 6010D
Client ID: 6301-SW3
Lab ID:
CC18640-05
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
2.5
0.80
2.0
ug/L
EPA 8260D
Barium - Total
22.1
1.10
10.0
ug/L
EPA 6010D
Client ID: 6301-SW4
Lab ID:
CC18640-06
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
1.0
1
0.80
2.0
ug/L
EPA 8260D
Barium - Total
20.0
1.10
10.0
ug/L
EPA 6010D
Client ID: 6301-MW8
Lab ID:
CC19666-01
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
Barium - Total
102
1.10
10.0
ug/L
EPA 6010D
Client ID: 6301-MW8
Lab ID:
CC19666-01RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,2-Dichlorobenzene
0.84
1
0.19
1.0
ug/L
EPA 8260D
1,4-Dichlorobenzene
6.2
0.19
1.0
ug/L
EPA 8260D
1,4-Dioxane
39
0.80
2.0
ug/L
EPA 8260D
Benzene
2.9
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
6.1
0.17
1.0
ug/L
EPA 8260D
Toluene
0.48 1
0.14
1.0
ug/L
EPA 8260D
Xylenes (Total)
2.2 1
0.45
3.0
ug/L
EPA 8260D
FINAL
This report relates only to the sample as received by the
laboratory, and may
only be reproduced
in full.
I Page 6 Of 56

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW11DR
Lab ID:
CC19666-02
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Barium - Total
59.3
1.10
10.0
ug/L
EPA 6010D
Chloride
21000
2200
5000
ug/L
EPA 300.0
Iron - Total
75900
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
191
1.50
10.0
ug/L
EPA 6010D
Sulfate as SO4
15000
2900
5000
ug/L
EPA 300.0
Total Alkalinity as CaCC3
240000
D
28000
30000
ug/L
EPA 310.2
Total Dissolved Solids
220000
50000
50000
ug/L
SM 2540C-2011
Client ID: 6301-MW11DR
Lab ID:
CC19666-02RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dichlorobenzene
2.0
0.19
1.0
ug/L
EPA 8260D
1,4-Dioxane
3.9
0.80
2.0
ug/L
EPA 8260D
Benzene
1.6
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
0.90
1
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
2.4
0.15
1.0
ug/L
EPA 8260D
Vinyl chloride
1.3
0.32
1.0
ug/L
EPA 8260D
Client ID: 6301-MW17D
Lab ID:
CC19666-03
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dioxane
5.2
0.80
2.0
ug/L
EPA 8260D
Barium - Total
16.5
1.10
10.0
ug/L
EPA 6010D
Chloride
2300
1
2200
5000
ug/L
EPA 300.0
Copper - Total
2.96
1
1.60
10.0
ug/L
EPA 6010D
Iron - Total
181
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
2.71
1
1.50
10.0
ug/L
EPA 6010D
Sulfate as SO4
48000
2900
5000
ug/L
EPA 300.0
Total Alkalinity as CaCC3
130000
14000
15000
ug/L
EPA 310.2
Total Dissolved Solids
220000
50000
50000
ug/L
SM 2540C-2011
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 7 Of 56

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ANALYTICAL RESULTS
Description: 6301-MW13S Lab Sample ID:CC18640-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 10:35 Work Order: CC18640
Project: Moore Cc LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
u
ug/L
1
0.12
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
u
ug/L
1
0.28
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
u
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,1-Dichloroethane [75-34-3]^
0.13
u
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,1-Dichloroethene [75-35-4]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
u
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2-Dibromoethane [106-93-4]^
0.66
u
ug/L
1
0.66
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
u
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2-Dichloroethane [107-06-2]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,2-Dichloropropane [78-87-5]^
0.10
u
ug/L
1
0.10
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
u
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
2-Butanone [78-93-3]^
1.3
u
ug/L
1
1.3
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
2-Hexanone [591-78-6]^
0.88
u
ug/L
1
0.88
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
u
ug/L
1
1.1
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Acetone [67-64-1]^
10
u
ug/L
1
10
20
9LO5039
EPA 8260D
12/05/19
19:06
REF
Acrylonitrile [107-13-1]^
3.5
u
ug/L
1
3.5
10
9LO5039
EPA 8260D
12/05/19
19:06
REF
Benzene [71-43-2]^
1.1
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Bromochloromethane [74-97-5]^
0.48
u
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Bromodichloromethane [75-27-4]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Bromoform [75-25-2]^
0.22
u
ug/L
1
0.22
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Bromomethane [74-83-9]^
0.14
u
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Carbon disulfide [75-15-0]^
1.5
u
ug/L
1
1.5
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Carbon tetrachloride [56-23-5]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Chlorobenzene [108-90-7]^
2.1
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Chloroethane [75-00-3]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Chloroform [67-66-3]^
0.18
u
ug/L
1
0.18
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Chloromethane [74-87-3]^
0.13
u
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
cis-1,2-Dichloroethene [156-59-2]^
1.1
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
u
ug/L
1
0.20
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Dibromochloromethane [124-48-1]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Dibromomethane [74-95-3]^
0.27
u
ug/L
1
0.27
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Ethylbenzene [100-41-4]^
0.13
u
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Iodomethane [74-88-4]^
1.7
u
ug/L
1
1.7
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Methylene chloride [75-09-2]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Styrene [100-42-5]^
0.11
u
ug/L
1
0.11
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Tetrachloroethene [127-18-4]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Tetrahydrofuran [109-99-9]^
0.53
u
ug/L
1
0.53
1.0
9LO3038
EPA 8260D
12/04/19
11:33
REF QV-01
Toluene [108-88-3]^
0.14
u
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
u
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
u
ug/L
1
0.70
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Trichloroethene [79-01-6]^
0.15
u
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Trichlorofluoromethane [75-69-4]^
0.24
u
ug/L
1
0.24
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Vinyl acetate [108-05-4]^
0.95
u
ug/L
1
0.95
5.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
Vinyl chloride [75-01-4]^
0.70
J
ug/L
1
0.32
1.0
9LO5039
EPA 8260D
12/05/19
19:06
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 8 Of 56

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ANALYTICAL RESULTS
Description: 6301-MW13S Lab Sample ID:CC18640-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 10:35 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO5039 EPA 8260D 12/05/19 19:06 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
51
1
50.0
103 %
53-136
9LO5039
EPA 8260D
12105119 19:06
REF
Dlbromofluoromethane
50
1
50.0
100 %
67-129
9LO5039
EPA 6260D
1210511919:06
REF
Toluene-d8
45
1
50.0
90 %
59-134
9LO5039
EPA 8260D
1210511919:06
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:39
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9K26013
EPA 6020B
12/02/19 19:36
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Barium [7440-39-3]^
36.7
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Copper[7440-50-8]^
1.60
U
ug/L
1
1.60
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Iron [7439-89-6]^
99700
ug/L
1
22.0
50.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Manganese [7439-96-5]^
189
ug/L
1
1.50
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9K26013
EPA 6020B
12/02/19 19:36
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9LO2012
EPA 6010D
12/05/19 14:27
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Chloride [16887-00-6]^
11000
ug/L
1
2200
5000
9L03017
EPA 300.0
12/03/19 21:55
PDK
Sulfate as SO4 [14808-79-8]^
2900
U
ug/L
1
2900
5000
9LO3017
EPA 300.0
12/03/19 21:55
PDK
Sulfide [18496-25-8]^
36
J
ug/L
1
10
100
9K23005
iM 4500S2 D-2011
11/23/19 14:59
JOC
Total Alkalinity as CaCO3 [471-34-1]^
87000
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:13
AKF
Total Dissolved Solids^
110000
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 9 Of 56

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ANALYTICAL RESULTS
Description: 6301-MW13S Lab Sample ID:CC18640-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 10:35 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
Results
Flag Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]A
6.0
ug/L
1
0.80 2.0
9LO1004
EPA 8260D
12/02/19 01:12
M]H
Surrogates
Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-&
5.7
1 5.00
114 %
75-125
9LO1004
EPA 8260D
12102119 01:12
MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 10 of 56

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ANALYTICAL RESULTS
Description: 6301-MW13D Lab Sample ID:CC18640-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 12:18 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO5039
EPA 8260D
12/05/19
19:38
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO5039
EPA 8260D
12/05/19
19:38
REF
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
cis-1,2-Dichloroethene [156-59-2]^
0.71
J
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
9LO3038
EPA 8260D
12/04/19
12:06
REF QV-01
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO5039
EPA 8260D
12/05/19
19:38
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 11 Of 56

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW13D Lab Sample ID:CC18640-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 12:18 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO5039 EPA 8260D 12/05/19 19:38 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
50
1
50.0
101 %
53-136
9LO5039
EPA 8260D
12105119 19:38
REF
Dlbromofluoromethane
50
1
50.0
99 %
67-129
9LO5039
EPA 6260D
1210511919:38
REF
Toluene-d8
44
1
50.0
88 %
59-134
9LO5039
EPA 8260D
121051191938
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:41
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9K26013
EPA 6020B
12/02/19 19:41
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Barium [7440-39-3]^
11.7
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Copper[7440-50-8]^
2.75
J
ug/L
1
1.60
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Iron [7439-89-6]^
6040
ug/L
1
22.0
50.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Manganese [7439-96-5]^
15.2
ug/L
1
1.50
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9K26013
EPA 6020B
12/02/19 19:41
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9LO2012
EPA 6010D
12/05/19 14:18
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Chloride [16887-00-6]^
5400
ug/L
1
2200
5000
9LO3017
EPA 300.0
12/03/19 22:48
PDK
Sulfate as SO4 [14808-79-8]^
2900
U
ug/L
1
2900
5000
9LO3017
EPA 300.0
12/03/19 22:48
PDK
Total Alkalinity as CaCO3 [471-34-1]^
14000
J
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:14
AKF
Total Dissolved Solids^
50000
U
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 12 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW13D Lab Sample ID:CC18640-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 12:18 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
Results
Flag Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]A
2.8
ug/L
1
0.80 2.0
9LO1004
EPA 8260D
12/02/19 01:49
M]H
Surrogates
Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-&
4.6
1 5.00
93 %
75-125
9LO1004
EPA 8260D
12102119 01:49
MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 13 of 56

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW1 Lab Sample ID:CC18640-03 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 15:30 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Chlorobenzene [108-90-7]^
0.57
J
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Iodomethane[74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
QV-01
Xylenes (Total) [1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3038
EPA 8260D
12/04/19
12:38
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 14 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW1 Lab Sample ID:CC18640-03 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 15:30 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene 46
1
50.0
93 %
53-136
9LO3038
EPA 8260D
12104119 12:38
REF
Dibromofluoromethane 60
1
50.0
120 %
67-129
9LO3038
EPA 8260D
12104119 12:38
REF
Toluene-& 52
1
50.0
103 %
59-134
9LO3038
EPA 8260D
12104119 12:38
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Mercury [7439-97-6]^ 0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:43
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Arsenic[7440-38-2]^ 7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Barium [7440-39-3]^ 19.3
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Cadmium [7440-43-9]^ 0.446
J
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Chromium [7440-47-3]^ 1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Lead [7439-92-1]^ 3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Selenium [7782-49-2]^ 6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Silver[7440-22-4]^ 1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:21
]DH
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
1,4-Dioxane [123-91-1]^
Surrogates
Toluene-&
Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1.3 J ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 02:25 M]H
Results DF Snike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
4.8 1 5.00 95 % 75-125 9LO1004 EPA 8260D 12102119 02:25 MJH
FINAL
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 15 Of rJ6

00�
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ANALYTICAL RESULTS
Description: 6301-SW2 Lab Sample ID:CC18640-04 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 14:15 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Chlorobenzene [108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
QV-01
Xylenes(Total)[1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3038
EPA 8260D
12/04/19
13:10
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 16 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW2 Lab Sample ID:CC18640-04 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 14:15 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene 45
1
50.0
89 %
53-136
9LO3038
EPA 8260D
12104119 13:10
REF
Dibromofluoromethane 58
1
50.0
116 %
67-129
9LO3038
EPA 8260D
1210411913:10
REF
Toluene-& 53
1
50.0
106 %
59-134
9LO3038
EPA 8260D
1210411913:10
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Mercury [7439-97-6]^ 0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:50
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Arsenic [7440-38-2]^ 9.27
J
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Barium [7440-39-3]^ 13.9
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Cadmium [7440-43-9]^ 0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Chromium [7440-47-3]^ 1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Lead [7439-92-1]^ 3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Selenium [7782-49-2]^ 6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Silver[7440-22-4]^ 1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:38
]DH
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
1,4-Dioxane [123-91-1]^
Surrogates
Toluene-&
Results Flag Units DF MDL P L Batch Method Analyzed By Notes
0.80 U ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 03:01 M]H
Results DF Soike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
5.0 1 5.00 100 % 75-125 9LO1004 EPA 8260D 12102119 03:01 MJH
FINAL
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 17 Of rJ6

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW3 Lab Sample ID:CC18640-05 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 15:10 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Iodomethane[74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
QV-01
Xylenes (Total) [1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3038
EPA 8260D
12/04/19
13:43
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 18 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW3 Lab Sample ID:CC18640-05 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 15:10 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene 45
1
50.0
90 %
53-136
9LO3038
EPA 8260D
12104119 13:43
REF
Dibromofluoromethane 61
1
50.0
122 %
67-129
9LO3038
EPA 8260D
1210411913:43
REF
Toluene-& 53
1
50.0
107 %
59-134
9LO3038
EPA 8260D
1210411913:43
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Mercury [7439-97-6]^ 0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:52
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Arsenic[7440-38-2]^ 7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Barium [7440-39-3]^ 22.1
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Cadmium [7440-43-9]^ 0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Chromium [7440-47-3]^ 1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Lead [7439-92-1]^ 3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Selenium [7782-49-2]^ 6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Silver[7440-22-4]^ 1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:33
]DH
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
1,4-Dioxane [123-91-1]^
Surrogates
Toluene-&
Results Flag Units DF MDL P L Batch Method Analyzed By Notes
2.5 ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 03:39 M]H
Results DF Soike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
5.1 1 5.00 102 % 75-125 9LO1004 EPA 8260D 12102119 0329 MJH
FINAL
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 19 Of rJ6

00�
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ANALYTICAL RESULTS
Description: 6301-SW4 Lab Sample ID:CC18640-06 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 14:30 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Chlorobenzene [108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
QV-01
Xylenes(Total)[1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3038
EPA 8260D
12/04/19
14:15
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 20 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-SW4 Lab Sample ID:CC18640-06 Received: 11/22/19 07:00
Matrix: Surface Water Sampled:11/21/19 14:30 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene 45
1
50.0
90 %
53-136
9L03038
EPA 8260D
12104119 14:15
REF
Dibromofluoromethane 55
1
50.0
110 %
67-129
9L03038
EPA 8260D
12104119 14:15
REF
Toluene-& 52
1
50.0
105 %
59-134
9L03038
EPA 8260D
12104119 14:15
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Mercury [7439-97-6]^ 0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:55
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Arsenic[7440-38-2]^ 7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Barium [7440-39-3]^ 20.0
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Cadmium [7440-43-9]^ 0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Chromium [7440-47-3]^ 1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Lead [7439-92-1]^ 3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Selenium [7782-49-2]^ 6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Silver[7440-22-4]^ 1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:35
]DH
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
1,4-Dioxane [123-91-1]^
Surrogates
Toluene-&
Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1.0 1 ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 04:15 M]H
Results DF Soike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
5.5 1 5.00 110 % 75-125 9L01004 EPA 8260D 12102119 04:15 MJH
FINAL
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 21 of 56

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-Field Blank Lab Sample ID:CC18640-07 Received: 11/22/19 07:00
Matrix: Water Sampled:11/21/19 13:25 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Ethylbenzene[100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Iodomethane[74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Naphthalene [91-20-3]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Styrene[100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3038
EPA 8260D
12/04/19
09:57
REF
QV-01
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 22 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-Field Blank Lab Sample ID:CC18640-07 Received: 11/22/19 07:00
Matrix: Water Sampled:11/21/19 13:25 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO3038 EPA 8260D 12/04/19 09:57 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
46
1
50.0
92 %
53-136
9LO3038
EPA 8260D
12104119 09:57
REF
Dlbromofluoromethane
56
1
50.0
112 %
67-129
9LO3036
EPA 6260D
12104119 09:57
REF
Toluene-d8
59
1
50.0
119 %
59-134
9LO3036
EPA 8260D
12104119 09:57
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
PQL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 15:57
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9K26013
EPA 6020B
12/02/19 19:45
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Barium [7440-39-3]^
1.10
U
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Copper[7440-50-8]^
1.60
U
ug/L
1
1.60
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Iron [7439-89-6]^
22.0
U
ug/L
1
22.0
50.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Manganese [7439-96-5]^
1.50
U
ug/L
1
1.50
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9K26013
EPA 6020B
12/02/19 19:45
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9LO2012
EPA 6010D
12/05/19 14:41
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Chloride[16887-00-6]^
2200
U
ug/L
1
2200
5000
9LO3017
EPA 300.0
12/03/19 23:06
PDK
Sulfate as SO4 [14808-79-8]^
2900
U
ug/L
1
2900
5000
9LO3017
EPA 300.0
12/03/19 23:06
PDK
Total Alkalinity as CaCO3 [471-34-1]^
14000
U
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:14
AKF
Total Dissolved Solids^
50000
U
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 23 of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-Field Blank Lab Sample ID:CC18640-07 Received: 11/22/19 07:00
Matrix: Water Sampled:11/21/19 13:25 Work Order: CC18640
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte I'CAS Numberl
Results
Flao
Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]^
0.80
U
ug/L
1
0.80 2.0
9LO1004
EPA 8260D
12/02/19 04:51
M]H
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-&
5.2
1
5.00
103 %
75-125
9LO1004
EPA 8260D
12102119 04:51
MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 24 of 56

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-Trip Blank Lab Sample ID:CC18640-08 Received: 11/22/19 07:00
Matrix: Water Sampled:11/21/19 10:35 Work Order: CC18640
Project: Moore Co LF Sampled By: ENCO
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Iodomethane[74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Naphthalene [91-20-3]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3038
EPA 8260D
12/04/19
10:29
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 25 Of 56

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ANALYTICAL RESULTS
Description: 6301-Trip Blank Lab Sample ID:CC18640-08 Received: 11/22/19 07:00
Matrix: Water Sampled:11/21/19 10:35 Work Order: CC18640
Project: Moore Co LF Sampled By: ENCO
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Vinyl chloride [75-01-4]1 0.32 U ug/L 1 0.32 1.0 9LO3038 EPA 8260D 12/04/19 10:29 REF QV-01
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO3038 EPA 8260D 12/04/19 10:29 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
4-Bromofluorobenzene
47
1
50.0
94 %
53-136
9LO3038
EPA 8260D
12104119 10:29
REF
Dlbromofluoromethane
51
1
50.0
101 %
67-129
9LO3038
EPA 6260D
12104119 10:29
REF
Toluene-d8
54
1
50.0
108 %
59-134
9LO3036
EPA 8260D
12104119 10:29
REF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL POLL
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]^
0.80
U
ug/L
1
0.80 2.0
9LO1004
EPA 8260D
12/02/19 05:28
MJH
Surrogates
Results
DF
So/ke Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
By Notes
Toluene-&
5.2
1
5.00
105 %
75-125
9LO1004
EPA 8260D
12102119 05:28
MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 26 Of 56

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ANALYTICAL RESULTS
Description: 6301-MW8 Lab Sample ID:CC19666-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 10:25 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
u
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
u
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
u
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,1-Dichloroethane [75-34-3]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,1-Dichloroethene [75-35-4]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
u
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2-Dibromoethane [106-93-4]^
0.66
u
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2-Dichlorobenzene [95-50-1]^
0.84
J
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2-Dichloroethane [107-06-2]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,2-Dichloropropane [78-87-5]^
0.10
u
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
1,4-Dichlorobenzene [106-46-7]^
6.2
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
2-Butanone [78-93-3]^
1.3
u
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
2-Hexanone [591-78-6]^
0.88
u
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
u
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Acetone [67-64-1]^
10
u
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
14:52
REF
Acrylonitrile [107-13-1]^
3.5
u
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
14:52
REF
Benzene [71-43-2]^
2.9
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Bromochloromethane [74-97-5]^
0.48
u
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Bromodichloromethane [75-27-4]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Bromoform [75-25-2]^
0.22
u
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Bromomethane [74-83-9]^
0.14
u
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Carbon disulfide [75-15-0]^
1.5
u
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Carbon tetrachloride [56-23-5]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Chlorobenzene [108-90-7]^
6.1
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Chloroethane [75-00-3]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Chloroform [67-66-3]^
0.18
u
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Chloromethane [74-87-3]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
cis-1,2-Dichloroethene [156-59-2]^
0.15
u
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
u
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Dibromochloromethane [124-48-1]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Dibromomethane [74-95-3]^
0.27
u
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Ethylbenzene [100-41-4]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Iodomethane [74-88-4]^
1.7
u
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Methylene chloride [75-09-2]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Styrene [100-42-5]^
0.11
u
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Tetrachloroethene [127-18-4]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Toluene [108-88-3]^
0.48
J
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
trans- l,2-Dichloroethene [156-60-5]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
u
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
u
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Trichloroethene [79-01-6]^
0.15
u
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Trichlorofluoromethane [75-69-4]^
0.24
u
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Vinyl acetate [108-05-4]^
0.95
u
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Vinyl chloride [75-01-4]^
0.32
u
ug/L
1
0.32
1.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
Xylenes(Total) [1330-20-7]^
2.2
J
ug/L
1
0.45
3.0
9LO3039
EPA 8260D
12/04/19
14:52
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 27 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW8 Lab Sample ID:CC19666-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 10:25 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene 51
1
50.0
102 %
53-136
9LO3039
EPA 8260D
12104119 14:52
REF
Dibromofluoromethane 52
1
50.0
103 %
67-129
9LO3039
EPA 8260D
12104119 14:52
REF
Toluene-& 44
1
50.0
88 %
59-134
9LO3039
EPA 8260D
12104119 14:52
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Mercury [7439-97-6]^ 0.150
U
ug/L
1
0.150
0.200
9LO2029
EPA 7470A
12/03/19 15:03
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Arsenic[7440-38-2]^ 7.60
U
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Barium [7440-39-3]^ 102
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Cadmium [7440-43-9]^ 0.360
U
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Chromium [7440-47-3]^ 1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Lead [7439-92-1]^ 3.10
U
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Selenium [7782-49-2]^ 6.20
U
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Silver[7440-22-4]^ 1.90
U
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:41
]DH
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
1,4-Dioxane [123-91-1]^
Surrogates
Toluene-&
Results Flag Units DF MDL P L Batch Method Analyzed By Notes
39 ug/L 1 0.80 2.0 9LO2040 EPA 8260D 12/02/19 18:43 KKW
Results DF Soike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
5.4 1 5.00 108 % 75-125 9LO2040 EPA 8260D 12102119 16:43 KKW
FINAL
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 28 Of rJ6

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ANALYTICAL RESULTS
Description: 6301-MW11DR Lab Sample ID:CC19666-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19666
Project: Moore Cc LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
u
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
u
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
u
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,1-Dichloroethane [75-34-3]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,1-Dichloroethene [75-35-4]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
u
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2-Dibromoethane [106-93-4]^
0.66
u
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
u
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2-Dichloroethane [107-06-2]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,2-Dichloropropane [78-87-5]^
0.10
u
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
1,4-Dichlorobenzene [106-46-7]^
2.0
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
2-Butanone [78-93-3]^
1.3
u
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
2-Hexanone [591-78-6]^
0.88
u
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
u
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Acetone [67-64-1]^
10
u
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
15:23
REF
Acrylonitrile [107-13-1]^
3.5
u
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
15:23
REF
Benzene [71-43-2]^
1.6
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Bromochloromethane [74-97-5]^
0.48
u
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Bromodichloromethane [75-27-4]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Bromoform [75-25-2]^
0.22
u
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Bromomethane [74-83-9]^
0.14
u
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Carbon disulfide [75-15-0]^
1.5
u
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Carbon tetrachloride [56-23-5]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Chlorobenzene [108-90-7]^
0.90
J
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Chloroethane [75-00-3]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Chloroform [67-66-3]^
0.18
u
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Chloromethane [74-87-3]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
cis-1,2-Dichloroethene [156-59-2]^
2.4
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
u
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Dibromochloromethane [124-48-1]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Dibromomethane [74-95-3]^
0.27
u
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Ethylbenzene [100-41-4]^
0.13
u
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Iodomethane [74-88-4]^
1.7
u
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Methylene chloride [75-09-2]^
0.23
u
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Styrene [100-42-5]^
0.11
u
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Tetrachloroethene [127-18-4]^
0.17
u
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Tetrahydrofuran [109-99-9]^
0.53
u
ug/L
1
0.53
1.0
9LO3036
EPA 8260D
12/04/19
02:56
REF
Toluene [108-88-3]^
0.14
u
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
u
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
u
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
u
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Trichloroethene [79-01-6]^
0.15
u
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Trichlorofluoromethane [75-69-4]^
0.24
u
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Vinyl acetate [108-05-4]^
0.95
u
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
Vinyl chloride [75-01-4]^
1.3
ug/L
1
0.32
1.0
9LO3039
EPA 8260D
12/04/19
15:23
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 29 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW11DR Lab Sample ID:CC19666-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO3039 EPA 8260D 12/04/19 15:23 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
49
1
50.0
97 %
53-136
9LO3039
EPA 8260D
12104119 15:23
REF
Dlbromofluoromethane
51
1
50.0
102 %
67-129
9LO3039
EPA 6260D
1210411915:23
REF
Toluene-d8
44
1
50.0
87 %
59-134
9LO3039
EPA 8260D
1210411915:23
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2029
EPA 7470A
12/03/19 15:06
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9LO2023
EPA 6020B
12/03/19 15:03
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Barium [7440-39-3]^
59.3
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Copper[7440-50-8]^
1.60
U
ug/L
1
1.60
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Iron [7439-89-6]^
75900
ug/L
1
22.0
50.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Manganese [7439-96-5]^
191
ug/L
1
1.50
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9LO2023
EPA 6020B
12/03/19 15:03
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9LO3016
EPA 6010D
12/05/19 15:43
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
21000
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 04:42
PDK
Sulfate as SO4 [14808-79-8]^
15000
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 04:42
PDK
Total Alkalinity as CaCO3 [471-34-1]^
240000
D
ug/L
2
28000
30000
9LO2007
EPA 310.2
12/02/19 13:22
AKF
Total Dissolved Solids^
220000
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 30 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW11DR Lab Sample ID:CC19666-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
Results
Flag Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]A
3.9
ug/L
1
0.80 2.0
9LO2040
EPA 8260D
12/02/19 18:06
KKW
Surrogates
Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-&
5.2
1 5.00
104 %
75-125
9LO2040
EPA 8260D
12102119 16:06
KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 31 of 56

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW17D Lab Sample ID:CC19666-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 15:25 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By
Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3036
EPA 8260D
12/04/19
03:28
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QL-02,
QV-01
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1 0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1 0.22
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1 0.14
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1 1.5
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1 0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1 0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Chloroethane [75-00-31^
0.23
U
ug/L
1 0.23
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1 0.18
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
Chloromethane [74-87-3]^
0.13
U
ug/L
1 0.13
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1 0.15
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1 0.20
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1 0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1 0.27
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Ethylbenzene[100-41-4]^
0.13
U
ug/L
1 0.13
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1 1.7
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1 0.23
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Styrene[100-42-5]^
0.11
U
ug/L
1 0.11
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1 0.17
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1 0.53
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Toluene [108-88-3]^
0.14
U
ug/L
1 0.14
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1 0.21
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1 0.15
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1 0.70
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1 0.15
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1 0.24
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1 0.95
5.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1 0.32
1.0
9LO3036
EPA 8260D
12/04/19
03:28
REF
QV-01
FINAL
This report relates only to the sample as received
by the laboratory,
and may only be reproduced in full.
I Page 32 Of 56

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW17D Lab Sample ID:CC19666-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 15:25 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO3036 EPA 8260D 12/04/19 03:28 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
45
1
50.0
91 %
53-136
9LO3036
EPA 8260D
12104119 03:28
REF
Dlbromofluoromethane
56
1
50.0
ill %
67-129
9LO3036
EPA 6260D
12104119 03:28
REF
Toluene-d8
52
1
50.0
105 %
59-134
9L03036
EPA 8260D
12104119 03:28
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2029
EPA 7470A
12/03/19 15:08
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9LO2023
EPA 6020B
12/03/19 15:08
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Barium [7440-39-3]^
16.5
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Copper[7440-50-8]^
2.96
J
ug/L
1
1.60
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Iron [7439-89-6]^
181
ug/L
1
22.0
50.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Manganese [7439-96-5]^
2.71
J
ug/L
1
1.50
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9LO2023
EPA 6020B
12/03/19 15:08
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9LO3016
EPA 6010D
12/05/19 15:52
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
2300
J
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 04:59
PDK
Sulfate as SO4 [14808-79-8]^
48000
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 04:59
PDK
Total Alkalinity as CaCO3 [471-34-1]^
130000
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:22
AKF
Total Dissolved Solids^
220000
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 33 Of 56

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ANALYTICAL RESULTS
Description: 6301-MW17D Lab Sample ID:CC19666-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 15:25 Work Order: CC19666
Project: Moore Co LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte MAS Numberl
Results
Flag Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
1,4-Dioxane [123-91-1]A
5.2
ug/L
1
0.80 2.0
9LO2040
EPA 8260D
12/02/19 15:01
KKW
Surrogates
Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-&
4.9
1 5.00
98 %
75-125
9LO2040
EPA 6260D
1210211915:01
KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 34 of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03036 -EPA 50306 MS
Blank (9L03036-BLK3) Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
Analvte
Result
Flaa
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Tetrahydrofuran
0.53
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene
FINAL
47 u9/L 50.0 93 53-136
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 35 Of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03036 - EPA 50306 MS - Continued
Blank (9L03036-BLK3) Continued Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
D/bromot7uoromethane 54 u91L 50.0 107 67-129
Toluene-& 53 u91L 50.0 106 59-134
LCS (9L03036-BSI) Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 16:43
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
23
1.0
ug/L
20.0
116
75-133
Benzene
23
1.0
ug/L
20.0
116
80-134
Chlorobenzene
19
1.0
ug/L
20.0
94
80-120
Toluene
19
1.0
ug/L
20.0
94
71-120
Trichloroethene
23
1.0
ug/L
20.0
117
74-120
Matrix Spike (9L03036-MS1)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:15
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
24
1.0
ug/L
20.0
0.21 U
122
75-133
Benzene
25
1.0
ug/L
20.0
0.15 U
125
80-134
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
93
80-120
Toluene
19
1.0
ug/L
20.0
0.14 U
97
71-120
Trichloroethene
21
1.0
ug/L
20.0
0.15 U
106
74-120
Matrix Spike Dup (9L03036-MSD1)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:47
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
25
1.0
ug/L
20.0
0.21 U
127
75-133 4
20
Benzene
24
1.0
ug/L
20.0
0.15 U
120
80-134 4
17
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
93
80-120 0.2
16
Toluene
20
1.0
ug/L
20.0
0.14 U
98
71-120 1
17
Trichloroethene
22
1.0
ug/L
20.0
0.15 U
112
74-120 5
22
Batch A03039 -EPA 5030E MS
Blank (9L03038-BLK1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 08:20
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units Level Result %REC Limits RPD Limit Notes
1,1,1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 36 Of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03038 - EPA 50308 MS - Continued
Blank (9111-03038-BLK3) Continued Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 08:20
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Naphthalene
0.11
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Tetrahydrofuran
0.53
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
4-Bromof/uorobenzene
43
u91L
50.0
86
53-136
Dibromof/uoromethane
55
u91L
50.0
111
67-129
Toluene-d8
54
u91L
50.0
107
59-134
LCS (9L03038-BS1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 06:11
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
23
1.0
ug/L
20.0
114
75-133
Benzene
22
1.0
ug/L
20.0
112
80-134
Chlorobenzene
18
1.0
ug/L
20.0
88
80-120
Toluene
19
1.0
ug/L
20.0
93
71-120
Trichloroethene
24
1.0
ug/L
20.0
119
74-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 37 Of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9LO3038 - EPA 50308 MS - Continued
Matrix Spike (9L03038-MS3)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 06:43
Source: CC18500-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
27
1.0
ug/L
20.0
0.21 U
133
75-133
Benzene
23
1.0
ug/L
20.0
0.15 U
117
80-134
Chlorobenzene
18
1.0
ug/L
20.0
0.17 U
90
80-120
Toluene
19
1.0
ug/L
20.0
0.14 U
96
71-120
Trichloroethene
22
1.0
ug/L
20.0
0.15 U
110
74-120
Matrix Spike Dup (9L03038-MSD1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 07:15
Source: CC18500-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
26
1.0
ug/L
20.0
0.21 U
129
75-133 2
20
Benzene
24
1.0
ug/L
20.0
0.15 U
121
80-134 4
17
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
95
80-120 5
16
Toluene
20
1.0
ug/L
20.0
0.14 U
102
71-120 6
17
Trichloroethene
24
1.0
ug/L
20.0
0.15 U
119
74-120 8
22
Batch 9L03039 - EPA 5030E MS
Blank (91-03039-BLK3)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 08:37
Analvte
Result
Flaq
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 38 Of 56

QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03039 - EPA 50308 MS - Continued
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Blank (9L03039-BLK3) Continued Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 08:37
Analvte
Result
Flaq
POL
Units
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene 50
u9/L
50.0 100 53-136
Dibromofluoromethane 50
u9/L
50.0 100 67-129
Toluene-d8 44
u9/L
50.0 87 59-134
LCS (9L03039-BS3)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 06:32
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
88
75-133
Benzene
21
1.0
ug/L
20.0
106
80-134
Chlorobenzene
21
1.0
ug/L
20.0
104
80-120
Toluene
21
1.0
ug/L
20.0
107
71-120
Trichloroethene
22
1.0
ug/L
20.0
112
74-120
Matrix Spike (91-03039-MS1)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 07:04
Source: CC19707-02
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
0.21 U
90
75-133
Benzene
21
1.0
ug/L
20.0
0.15 U
107
80-134
Chlorobenzene
21
1.0
ug/L
20.0
0.17 U
105
80-120
Toluene
21
1.0
ug/L
20.0
0.14 U
106
71-120
Trichloroethene
20
1.0
ug/L
20.0
0.46
99
74-120
Matrix Spike Dup (91-03039-MSD1)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 07:35
Source: CC19707-02
Spike
Analvte
Result Flag
POL
Units
Level
1,1-Dichloroethene
19
1.0
ug/L
20.0
Benzene
22
1.0
ug/L
20.0
Chlorobenzene
21
1.0
ug/L
20.0
Toluene
21
1.0
ug/L
20.0
Trichloroethene
20
1.0
ug/L
20.0
Source
%REC
Result
%REC
Limits
0.21 U
93
75-133
0.15 U
109
80-134
0.17 U
104
80-120
0.14 U
107
71-120
0.46
98
74-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full.
RPD
RPD
Limit Notes
4
20
2
17
1
16
1
17
0.9
22
Page 39 of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9LO5039 - EPA 5030E MS
Blank (9L05039-BLK3) Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 17:33
Analvte
Result
Flaq
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene
Dibromofluoromethane
FINAL
48 u9/L 50.0 96 53-136
51 u9/L 50.0 101 67-129
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 40 Of 56

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L05039 - EPA 50308 MS - Continued
Blank (9L05039-BLK3) Continued Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 17:33
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Toluene-d8 45 u9/L 50.0 90 59-134
LCS (91-05039-BSI) Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 15:28
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
91
75-133
Benzene
22
1.0
ug/L
20.0
112
80-134
Chlorobenzene
21
1.0
ug/L
20.0
106
80-120
Toluene
22
1.0
ug/L
20.0
110
71-120
Trichloroethene
21
1.0
ug/L
20.0
103
74-120
Matrix Spike (91-05039-MS1)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 15:59
Source: CC20745-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
16
1.0
ug/L
20.0
0.21 U
81
75-133
Benzene
20
1.0
ug/L
20.0
0.15 U
101
80-134
Chlorobenzene
20
1.0
ug/L
20.0
0.17 U
100
80-120
Toluene
21
1.0
ug/L
20.0
0.14 U
105
71-120
Trichloroethene
19
1.0
ug/L
20.0
0.15 U
93
74-120
Matrix Spike Dup (91-05039-MSD1)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 16:31
Source: CC20745-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
0.21 U
88
75-133
8
20
Benzene
22
1.0
ug/L
20.0
0.15 U
109
80-134
7
17
Chlorobenzene
21
1.0
ug/L
20.0
0.17 U
106
80-120
6
16
Toluene
22
1.0
ug/L
20.0
0.14 U
108
71-120
4
17
Trichloroethene
20
1.0
ug/L
20.0
0.15 U
99
74-120
6
22
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02029 - EPA 7470A
Blank (9L02029-BLK3) Prepared: 12/02/2019 12:18 Analyzed: 12/03/2019 14:34
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Mercury 0.150 U 0.200 ug/L
LCS (91-02029-BSI) Prepared: 12/02/2019 12:18 Analyzed: 12/03/2019 14:38
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Mercury
4.96
0.200
ug/L
5.00
99
80-120
Matrix Spike (91-02029-MS1)
Prepared: 12/02/2019 12:18 Analyzed: 12/03/2019 14:43
Source: CC18500-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Mercury
5.09
0.200
ug/L
5.00
0.150 U
102
75-125
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 41 of 56

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QUALITY CONTROL DATA
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02029 - EPA 7470A - Continued
Matrix Spike Dup (9L02029-MSDI)
Prepared: 12/02/2019 12:18 Analyzed: 12/03/2019 14:50
Source: CC18500-01
Spike Source %REC
RPD
Analvte
Result Flaq
Q
Units
Level Result %REC Limits RPD
Limit Notes
Mercury
5.20
0.200
ug/L
5.00 0.150 U 104 75-125 2
25
Post Spike (9L02029-PS1)
Prepared: 12/02/2019 12:18 Analyzed: 12/03/2019 14:53
Source: CC18500-01
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Mercury
5.69
0.200
ug/L
5.00 0.0190 113 75-125
Batch 9L02030 - EPA 7470A
Blank (9L02030-BLK1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:20
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Mercury 0.150 U 0.200 ug/L
LCS (9L02030-BS3) Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:23
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
5.04
0.200
ug/L
5.00
101
80-120
Matrix Spike (9L02030-MS1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:28
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.62
0.200
ug/L
5.00
0.150 U
92
75-125
Matrix Spike Dup (9L02030-MSD1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:30
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.21
0.200
ug/L
5.00
0.150 U
84
75-125 9
25
Post Spike (91-02030-PS1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:32
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.46
0.200
ug/L
5.00
0.0430
88
75-125
Metals (total recoverable) by EPA 6000/7000
Series Methods -
Quality Control
Batch 9K26013 - EPA 3005A
Blank (9K26013-BLK1) Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:20
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Antimony
0.370
U
1.00
ug/L
Thallium
0.110
U
1.00
ug/L
LCS (9K26013-BS3)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:24
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Antimony
22.3
1.00
ug/L
20.0 112 80-120
FINAL
This report relates only to the sample as received by the
laboratory, and may only be reproduced in full.
Page 42 Of 56

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K26013 - EPA 3005A - Continued
LCS (9K26013-BS3) Continued Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:24
Spike Source %REC
RPD
Analvte
Result
Flaq
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Thallium
21.8
1.00
ug/L
20.0 109 80-120
Matrix Spike (9K26013-MSi)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:28
Source: CCI8513-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
44.6
2.00
ug/L
40.0 0.740 U 112 75-125
Thallium
42.9
2.00
ug/L
40.0 0.220 U 107 75-125
Matrix Spike Dup (9K26013-MSD3)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:32
Source: CC18513-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
45.1
2.00
ug/L
40.0 0.740 U 113 75-125 1
20
Thallium
42.6
2.00
ug/L
40.0 0.220 U 107 75-125 0.6
20
Post Spike (9K26013-PS1)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:37
Source: CC18513-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
23.0
1.00
ug/L
20.0-0.00221 115 75-125
Thallium
21.8
1.00
ug/L
20.0 0.0188 109 75-125
Batch 9L02012 - EPA 3005A
Blank (9L02012-BLK3) Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 10:29
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Beryllium
0.160
U
1.00
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Cobalt
1.40
U
10.0
ug/L
Copper
1.60
U
10.0
ug/L
Iron
22.0
U
50.0
ug/L
Lead
3.10
U
10.0
ug/L
Manganese
1.50
U
10.0
ug/L
Nickel
2.20
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
Vanadium
1.40
U
10.0
ug/L
Zinc
4.40
U
10.0
ug/L
LCS (911-02012-BSI)
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:16
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result %REC
Limits
RPD Limit Notes
Arsenic
187
10.0
ug/L
200
94
80-120
Barium
183
10.0
ug/L
200
91
80-120
Beryllium
18.6
1.00
ug/L
20.0
93
80-120
Cadmium
18.4
1.00
ug/L
20.0
92
80-120
FINAL
This report relates only to
the sample as received by the
laboratory, and
may only be reproduced in
full.
Page 43 of 56

(� �Eo
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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02012 - EPA 3005A - Continued
LCS (9L02012-BS3) Continued Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:16
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Chromium
184
10.0
ug/L
200
92
80-120
Cobalt
189
10.0
ug/L
200
94
80-120
Copper
184
10.0
ug/L
200
92
80-120
Iron
913
50.0
ug/L
1000
91
80-120
Lead
185
10.0
ug/L
200
92
80-120
Manganese
185
10.0
ug/L
200
92
80-120
Nickel
184
10.0
ug/L
200
92
80-120
Selenium
185
10.0
ug/L
200
92
80-120
Silver
192
10.0
ug/L
200
96
80-120
Vanadium
186
10.0
ug/L
200
93
80-120
Zinc
191
10.0
ug/L
200
95
80-120
Matrix Spike (911-02012-MS1)
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:19
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Arsenic
182
10.0
ug/L
200
7.60 U
91
75-125
Barium
215
10.0
ug/L
200
32.4
92
75-125
Beryllium
18.9
1.00
ug/L
20.0
0.160 U
95
75-125
Cadmium
18.2
1.00
ug/L
20.0
0.360 U
91
75-125
Chromium
186
10.0
ug/L
200
1.40 U
93
75-125
Cobalt
188
10.0
ug/L
200
1.40 U
94
75-125
Copper
189
10.0
ug/L
200
1.60 U
94
75-125
Iron
942
50.0
ug/L
1000
124
82
75-125
Lead
186
10.0
ug/L
200
3.10 U
93
75-125
Manganese
229
10.0
ug/L
200
44.8
92
75-125
Nickel
184
10.0
ug/L
200
2.20 U
92
75-125
Selenium
186
10.0
ug/L
200
6.20 U
93
75-125
Silver
194
10.0
ug/L
200
1.90 U
97
75-125
Vanadium
190
10.0
ug/L
200
2.12
94
75-125
Zinc
190
10.0
ug/L
200
4.40 U
95
75-125
Matrix Spike Dup (9L02012-MSD1)
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:22
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
Arsenic
185
10.0
ug/L
200
7.60 U
92
75-125
1
20
Barium
221
10.0
ug/L
200
32.4
95
75-125
3
20
Beryllium
19.4
1.00
ug/L
20.0
0.160 U
97
75-125
2
20
Cadmium
18.5
1.00
ug/L
20.0
0.360 U
93
75-125
2
20
Chromium
191
10.0
ug/L
200
1.40 U
96
75-125
3
20
Cobalt
193
10.0
ug/L
200
1.40 U
96
75-125
2
20
Copper
194
10.0
ug/L
200
1.60 U
97
75-125
3
20
Iron
1010
50.0
ug/L
1000
124
89
75-125
7
20
Lead
188
10.0
ug/L
200
3.10 U
94
75-125
0.8
20
Manganese
236
10.0
ug/L
200
44.8
95
75-125
3
20
Nickel
190
10.0
ug/L
200
2.20 U
95
75-125
4
20
Selenium
182
10.0
ug/L
200
6.20 U
91
75-125
2
20
Silver
199
10.0
ug/L
200
1.90 U
100
75-125
3
20
Vanadium
196
10.0
ug/L
200
2.12
97
75-125
3
20
Zinc
196
10.0
ug/L
200
4.40 U
98
75-125
3
20
FINAL
This report relates only to
the sample as received by the
laboratory, and
may only be
reproduced in
full.
Page 44 Of 56

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02012 - EPA 3005A - Continued
Post Spike (9L02012-PS1)
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:24
Source: CC18513-03
Spike
Source
%REC RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD Limit Notes
Arsenic
0.185
0.0100
mg/L
0.200
-0.00934
93
80-120
Barium
0.221
0.0100
mg/L
0.200
0.0324
94
80-120
Beryllium
0.0197
0.00100
mg/L
0.0200
8.06E-5
98
80-120
Cadmium
0.0190
0.00100
mg/L
0.0200
-0.000194
95
80-120
Chromium
0.193
0.0100
mg/L
0.200
0.000391
96
80-120
Cobalt
0.196
0.0100
mg/L
0.200
-0.000223
98
80-120
Copper
0.195
0.0100
mg/L
0.200
-0.000112
98
80-120
Iron
1.02
0.0500
mg/L
1.00
0.124
89
80-120
Lead
0.196
0.0100
mg/L
0.200
0.000195
98
80-120
Manganese
0.236
0.0100
mg/L
0.200
0.0448
96
80-120
Nickel
0.191
0.0100
mg/L
0.200
0.00162
95
80-120
Selenium
0.187
0.0100
mg/L
0.200
-0.00931
93
80-120
Silver
0.210
0.0100
mg/L
0.200
0.000488
105
80-120
Vanadium
0.197
0.0100
mg/L
0.200
0.00212
97
80-120
Zinc
0.199
0.0100
mg/L
0.200
0.00338
98
80-120
Batch 9102023 - EPA 3005A
Blank (9L02023-BLK3)
Prepared: 12/02/2019 10:57 Analyzed: 12/03/2019 13:38
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Antimony 0.370 U 1.00 ug/L
Thallium 0.110 U 1.00 ug/L
LCS (911-02023-BSI) Prepared: 12/02/2019 10:57 Analyzed: 12/03/2019 13:42
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
20.7
1.00
ug/L
20.0 104 80-120
Thallium
20.2
1.00
ug/L
20.0 101 80-120
Matrix Spike (9L02023-MS3)
Prepared: 12/02/2019 10:57 Analyzed: 12/03/2019 13:47
Source: CC18505-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
40.6
2.00
ug/L
40.0 0.740 U 102 75-125
Thallium
38.8
2.00
ug/L
40.0 0.220 U 97 75-125
Matrix Spike Dup (9L02023-MSD1)
Prepared: 12/02/2019 10:57 Analyzed: 12/03/2019 13:51
Source: CC18505-01
Spike Source %REC
RPD
Analvte
Result
Flaq
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
41.4
2.00
ug/L
40.0 0.740 U 103 75-125 2
20
Thallium
40.3
2.00
ug/L
40.0 0.220 U 101 75-125 4
20
Post Spike (911-02023-PSI)
Prepared: 12/02/2019 10:57 Analyzed: 12/03/2019 13:55
Source: CC18505-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
21.4
1.00
ug/L
20.0 0.0110 107 75-125
Thallium
20.9
1.00
ug/L
20.0 0.00860 105 75-125
Batch 9L03016 - EPA 3005A
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 45 Of 56

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Blank (9L03016-BLK3) Prepared: 12/03/2019 10:18 Analyzed: 12/05/2019 10:39
Spike Source %REC RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Beryllium
0.160
U
1.00
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Cobalt
1.40
U
10.0
ug/L
Copper
1.60
U
10.0
ug/L
Iron
22.0
U
50.0
ug/L
Lead
3.10
U
10.0
ug/L
Manganese
1.50
U
10.0
ug/L
Nickel
2.20
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
Vanadium
1.40
U
10.0
ug/L
Zinc
4.40
U
10.0
ug/L
LCS (911-03016-BSI)
Prepared: 12/03/2019 10:18 Analyzed: 12/05/2019 15:02
Spike
Source
%REC RPD
Analvte
Result Flaa
iQ
Units
Level
Result %REC
Limits RPD Limit Notes
Arsenic
211
10.0
ug/L
200
106
80-120
Barium
216
10.0
ug/L
200
108
80-120
Beryllium
20.8
1.00
ug/L
20.0
104
80-120
Cadmium
20.4
1.00
ug/L
20.0
102
80-120
Chromium
207
10.0
ug/L
200
104
80-120
Cobalt
213
10.0
ug/L
200
106
80-120
Copper
211
10.0
ug/L
200
105
80-120
Iron
1040
50.0
ug/L
1000
104
80-120
Lead
208
10.0
ug/L
200
104
80-120
Manganese
208
10.0
ug/L
200
104
80-120
Nickel
206
10.0
ug/L
200
103
80-120
Selenium
206
10.0
ug/L
200
103
80-120
Silver
216
10.0
ug/L
200
108
80-120
Vanadium
209
10.0
ug/L
200
104
80-120
Zinc
216
10.0
ug/L
200
108
80-120
Matrix Spike (9L03016-MS3)
Prepared:
12/03/2019 10:18 Analyzed: 12/05/2019 15:05
Source: CC19724-01
Spike
Source
%REC RPD
Analvte
Result Flaa
POL
Units
Level
Result
%REC
Limits RPD Limit Notes
Arsenic
199
10.0
ug/L
200
7.60 U
100
75-125
Barium
408
10.0
ug/L
200
200
104
75-125
Beryllium
21.5
1.00
ug/L
20.0
1.11
102
75-125
Cadmium
19.7
1.00
ug/L
20.0
0.360 U
99
75-125
Chromium
202
10.0
ug/L
200
1.40 U
101
75-125
Cobalt
211
10.0
ug/L
200
3.81
103
75-125
Copper
218
10.0
ug/L
200
10.7
104
75-125
Iron
5700
50.0
ug/L
1000
5220
48
75-125 QM-07
Lead
212
10.0
ug/L
200
7.59
102
75-125
Manganese
253
10.0
ug/L
200
55.1
99
75-125
Nickel
204
10.0
ug/L
200
4.12
100
75-125
Selenium
205
10.0
ug/L
200
6.20 U
102
75-125
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 46 Of 56

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L03016 - EPA 3005A - Continued
Matrix Spike (9L03016-MS3) Continued
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:05
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Silver
211
10.0
ug/L
200
1.90 U
105
75-125
Vanadium
207
10.0
ug/L
200
4.04
102
75-125
Zinc
214
10.0
ug/L
200
8.00
103
75-125
Matrix Spike Dup (9L03016-MSD1)
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:07
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
Q
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
198
10.0
ug/L
200
7.60 U
99
75-125
0.6
20
Barium
407
10.0
ug/L
200
200
103
75-125
0.2
20
Beryllium
21.0
1.00
ug/L
20.0
1.11
99
75-125
2
20
Cadmium
19.0
1.00
ug/L
20.0
0.360 U
95
75-125
4
20
Chromium
197
10.0
ug/L
200
1.40 U
99
75-125
2
20
Cobalt
203
10.0
ug/L
200
3.81
100
75-125
3
20
Copper
210
10.0
ug/L
200
10.7
100
75-125
4
20
Iron
5790
50.0
ug/L
1000
5220
57
75-125
2
20
QM-07
Lead
196
10.0
ug/L
200
7.59
94
75-125
8
20
Manganese
250
10.0
ug/L
200
55.1
97
75-125
1
20
Nickel
199
10.0
ug/L
200
4.12
98
75-125
2
20
Selenium
201
10.0
ug/L
200
6.20 U
100
75-125
2
20
Silver
205
10.0
ug/L
200
1.90 U
102
75-125
3
20
Vanadium
202
10.0
ug/L
200
4.04
99
75-125
3
20
Zinc
207
10.0
ug/L
200
8.00
100
75-125
3
20
Post Spike (9L03016-PS1)
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:10
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
0.195
0.0100
mg/L
0.200
0.00559
94
80-120
Barium
0.375
0.0100
mg/L
0.200
0.200
88
80-120
Beryllium
0.0201
0.00100
mg/L
0.0200
0.00111
95
80-120
Cadmium
0.0183
0.00100
mg/L
0.0200
-0.000125
92
80-120
Chromium
0.190
0.0100
mg/L
0.200
0.00103
94
80-120
Cobalt
0.194
0.0100
mg/L
0.200
0.00381
95
80-120
Copper
0.198
0.0100
mg/L
0.200
0.0107
94
80-120
Iron
5.79
0.0500
mg/L
1.00
5.22
57
80-120
QM-07
Lead
0.188
0.0100
mg/L
0.200
0.00759
90
80-120
Manganese
0.243
0.0100
mg/L
0.200
0.0551
94
80-120
Nickel
0.192
0.0100
mg/L
0.200
0.00412
94
80-120
Selenium
0.192
0.0100
mg/L
0.200
-0.00212
96
80-120
Silver
0.205
0.0100
mg/L
0.200
0.000380
102
80-120
Vanadium
0.195
0.0100
mg/L
0.200
0.00404
96
80-120
Zinc
0.193
0.0100
mg/L
0.200
0.00800
93
80-120
Classical Chemistry Parameters
- Quality Control
Batch 9K23005 - NO PREP
Blank (9K23005-BLKS) Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 47 Of 56

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K23005 - NO PREP - Continued
Blank (9K23005-BLKI) Continued Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Spike Source %REC RPD
Analvte Result Flag Q Units Level Result %REC Limits RPD Limit Notes
Sulfide 10 U 100 ug/L
LCS (9K23005-BSI) Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
0.35
0.10
mg/L
0.401 87 80-120
Duplicate (9K23005-DUPI)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
10
U
100
ug/L
10 U
25
Matrix Spike (9K23005-MS3)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC
RPD
Analvte
Result
Flag
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
260
100
ug/L
401 10 U 64 80-120
QM-07
Matrix Spike Dup (9K23005-MSD3)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
320
100
ug/L
401 10 U 80 80-120 22
25
Batch 9K27004 - NO PREP
Blank (9K27004-BLKS) Prepared & Analyzed: 11/27/2019 17:42
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Total Dissolved Solids 50000 U 50000 ug/L
LCS (9K27004-BS3) Prepared & Analyzed: 11/27/2019 17:42
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
980
50
mg/L
1000 98 80-120
Duplicate (9K27004-DUPi)
Prepared & Analyzed: 11/27/2019 17:42
Source: CC16655-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
270000
50000
ug/L
270000
1
20
Duplicate (9K27004-DUP2)
Prepared & Analyzed: 11/27/2019 17:42
Source: CC16869-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
2300000
50000
ug/L
2400000
2
20
Batch 9L02007 - NO PREP
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 48 Of 56

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO2007 - NO PREP - Continued
Blank (9L02007-BLK3) Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:05
Spike Source %REC RPD
Analvte Result Flaq fQ Units Level Result %REC Limits RPD Limit Notes
Total Alkalinity as CaCO3 14000 U 15000 ug/L
LCS (911-02007-BSI) Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:06
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
100
15
mg/L
100
101
80-120
Matrix Spike (911-02007-MS3)
Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:07
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
410000
DE
30000
ug/L
37800
380000
61
80-120
QM-07
Matrix Spike Dup (9L02007-MSD3)
Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:08
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
420000
DE
30000
ug/L
37800
380000
84
80-120 2
25
Batch 9LO3017 - NO PREP
Blank (9L03017-BLK3) Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 15:44
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
Sulfate as SO4 2900 U 5000 ug/L
LCS (9L03017-BS3) Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:02
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
49000
5000
ug/L
50000 99 90-110
Sulfate as SO4
51000
5000
ug/L
50000 101 90-110
Matrix Spike (911-03017-MS3)
Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:37
Source: CC18494-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
67000
5000
ug/L
20000 47000 104 90-110
Sulfate as SO4
37000
5000
ug/L
20000 16000 104 90-110
Matrix Spike (911-03017-MS2)
Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 17:30
Source: CC18500-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
20000
5000
ug/L
20000 2200 U 102 90-110
Sulfate as SO4
21000
5000
ug/L
20000 2900 U 106 90-110
Matrix Spike Dup (9L03017-MSD1)
Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:55
Source: CC18494-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
68000
5000
ug/L
20000 47000 108 90-110 1
10
FINAL
This report relates only to the sample as received by the
laboratory, and may only be reproduced in full.
Page 49 Of 56

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO3017 - NO PREP - Continued
Matrix Spike Dup (911-03017-MSD3) Continued Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:55
Source: CC18494-01
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Sulfate as SO4 37000 5000 ug/L 20000 16000 106 90-110 0.9 10
Batch 9L03027 - NO PREP
Blank (9L03027-BLK3) Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 01:10
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
Sulfate as SO4 2900 U 5000 ug/L
LCS (9L03027-BS3) Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 01:27
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
50000
5000
ug/L
50000
100
90-110
Sulfate as SO4
51000
5000
ug/L
50000
102
90-110
Matrix Spike (9L03027-MS1)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 02:20
Source: CC19657-02
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
32000
5000
ug/L
20000
13000
100
90-110
Sulfate as SO4
34000
5000
ug/L
20000
13000
104
90-110
Matrix Spike (91-03027-MS2)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 03:13
Source: CC19657-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
43000
5000
ug/L
26700
22000
77
90-110
QM-07
Sulfate as SO4
19000
5000
ug/L
26700
2900 U
73
90-110
QM-07
Matrix Spike Dup (911-03027-MSDI)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 02:38
Source: CC19657-02
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
33000
5000
ug/L
20000
13000
100
90-110 0.3
10
Sulfate as SO4
34000
5000
ug/L
20000
13000
105
90-110 0.3
10
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9L01004 - EPA 5030E MS
Blank (9L01004-BLK3)
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 23:22
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 0.80 U 2.0 ug/L
Toluene-d8 5.5 ug/L 5.00 109 75-125
LCS (9L01004-BS1) Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 20:57
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 23 2.0 ug/L 25.0 92 80-133
Page 50 of 56
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full.

(� �Eo
www.encolabs.com
QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9101004 - EPA 50308 MS - Continued
LCS (9L01004-BS3) Continued
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 20:57
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Toluene-&
4.6
u9/L
5.00 96 75-125
Matrix Spike (9L03004-MS1)
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 21:33
Source: AC08266-11
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
23
2.0
ug/L
25.0 0.80 U 92 80-133
Toluene-d8
5.5
u91L
5.00 110 75-125
Matrix Spike Dup (9L03004-MSD1)
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 22:09
Source: AC08266-11
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
23
2.0
ug/L
25.0 0.80 U 92 80-133 0.5
19
Toluene-d8
5.0
u9/L
5.00 100 75-125
Batch 9L02040 - EPA 50308 MS
Blank (9L02040-BLK3)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 11:40
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
0.80
U
2.0
ug/L
Toluene-d8
4.8
u91L
5.00 95 75-125
LCS (911-02040-BSI)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 10:30
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
24
2.0
ug/L
25.0 94 80-133
Toluene-d8
4.9
u9/L
5.00 97 75-125
Matrix Spike (9L02040-MS1)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 15:37
Source: AC08289-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
42
2.0
ug/L
25.0 22 78 80-133
QM-07
Toluene-d8
4.7
u91L
5.00 95 75-125
Matrix Spike Dup (9L02040-MSD1)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 16:15
Source: AC08289-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
41
2.0
ug/L
25.0 22 75 80-133 2
19
QM-07
Toluene-d8 4.9 u91L 5.00 97 75-125
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 51 of 56

(� �Eo
www.encolabs.com
FLAGS/NOTES AND DEFINITIONS
B The analyte was detected in the associated method blank.
D The sample was analyzed at dilution.
J The reported value is between the laboratory method detection limit (MDL) and the laboratory method
reporting limit (MRL), adjusted for actual sample preparation data and moisture content, where applicable.
U The analyte was analyzed for but not detected to the level shown, adjusted for actual sample preparation
data and moisture content, where applicable.
E The concentration indicated for this analyte is an estimated value above the calibration range of the
instrument. This value is considered an estimate.
MRL Method Reporting Limit. The MRL is roughly equivalent to the practical quantitation limit (PQL) and is
based on the low point of the calibration curve, when applicable, sample preparation factor, dilution
factor, and, in the case of soil samples, moisture content.
PQL PQL: Practical Quantitation Limit. The PQL presented is the laboratory MRL.
N The analysis indicates the presence of an analyte for which there is presumptive evidence (85% or greater
confidence) to make a "tentative identification".
P Greater than 25% concentration difference was observed between the primary and secondary GC column.
The lower concentration is reported.
[CALC] Calculated analyte - MDL/MRL reported to the highest reporting limit of the component analyses.
QL-02 The associated laboratory control sample exhibited high bias; since the result is ND, there is no impact.
QM-07 The spike recovery was outside acceptance limits for the MS and/or MSD. The batch was accepted based
on acceptable LCS recovery.
QV-01 The associated continuing calibration verification standard exhibited high bias; since the result is ND, there
is no impact.
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 52 of 56

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Sample Preservation Verification
ENCO Cary
Work Order: CC18640 Project: Moore Co LF
Client: Golder Associates, Inc. (GO007) Project #: 0739615018.100
Logged In: 22-Nov-19 08:53 Logged By: John C King
Preservation Check Performed By: DatelTime:
CC18640-01
moo
Cont
Type
Pres (pH)
Requirement
pH Checked /
In Control
pH Adjusted Date[Trme
Adjusted
Reagent Used/Comments
B
250mLP+HNO3
<2
Y) / N / NA
Y Ic I NA
C
250mLP+ZnAc+NaOH
>9
Y; I N / NA
Y 1 / NA
CC18640-02
Cont
Type
Pres (pH)
Requirement
pH Checked /
In Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
B
250mLP+HNO3
<2
'Y / N 1 NA
Y I I NA
CC18640-03
Cant
Type
Pres (pH)
Requirement
pH Checked 1
In Control
Date/Time
pH Adjusted Adjusted
Reagent Used/Comments
A
250mLP+HNO3
<2
(� N / NA
Y 1 N / NA
CC18640-04
Cont
Type
Pres (pH)
pH Checked 1
pH Adjusted Date/Time
Reagent Used/Comments
Requirement
In Control
Adjusted
A
250mLP+HNO3
<2
Y/ N I NA
Y/ N/ NA
C C 18640-05
Cont
Type
Pres (pH)
pH Checked /
pH Adjusted Date/Time
Reagent Used/Comments
Requirement
In Control
Adjusted
A
250mLP+HNO3
<2
Y 1 N / NA
Y N 1 NA
CC18640-06
Gant
Type
Prt;s (pH)
pH Checked 1
pH Adjusted DatelTime
Reagent Used/Comments
Requirement
In Control
Adjusted
A
250mLP+HNO3
<2
Y / N / NA
Y .I N / NA
L ✓
CC18640-07
Cont
Type
Pres (pH)
pH Checked /
pH Adjusted Date/Time
Reagent Used/Comments
Requirement
In Control
Adjusted
B
250mLP+HNO3
<2
'Y N / NA
Y / N I NA
Reagent Name ID
1
2
pH Strip ID:
Reagent Name ID
3
4
Rea ent Name ID
5
6
C:IELMNTIPrintlwko—PreservationCheck, rpt
Page 54 of 56
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Page 55 of 56

Sample Preservation Verification
ENCO Cary
Work Order: CC19666 Project: Moore Co LF
Client: Golder Associates, Inc. (GO007) Project #: 0739615018.100
Logged in: 22-Nov-19 09:00 Logged By: John C King
Preservation Check Performed By: Date/Time:
C C 19666-01
Cont
Type
Pres (PH)
Requirement
pH Checked /
Control
pH Adjusted Date/Time
Adiusted
Reagent Used/Comments
A
250mLP+HNO3
<2
1 N / NA
Y I�Wl NA
CC19666-02
Cont
Type
Pres (PH)
Requirement
pH Checked I
Control
pH Adjusted Date/Ti
Adiusted
Reagent Used/Comments
B
250mLP+HNO3
<2
/ N / NA
Y 1J N/ / NA
CC19666-03
Cont
Type
Pres (PH)
PH Checked/
pH Adjusted Date/Time
Reagent Used/Comments
Requirement
In Control
Adjusted
B
254mLP+HNO3
<2 t
Y l N/ NA
Y !'N,1 NA
Rea ent Name ID
1
2
pH Strip 0:
Rea ent Name ID
3
4
Reagent Name ID
5
6
C:IELMNT1Printlwko_PreservationCheck. rpt
Page 56 of 56
age

GOLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY CONTROL
LABORATORY DATA REVIEW
Page 1 of 4
Project Name: Moore County Landfill
Project Reference Number: 19127453.100
Sampling Event Date: November 19-21, 2019
Review Date: December 17, 2019
Report #: CC18640,CC19666
Signature:
QA/QC Sign Off:
Date:
Date:
GOLDER
Initials: NTT
Person(s) performing the review are to initial each item on this form as acknowledgement
of data acceptance, or as acknowledgement of a review issue. In the case of the latter, a
brief explanation should follow the applicable item.
Golder Associates Inc. has reviewed the laboratory certificates of analysis, chain -of -custody form,
and laboratory provided sample group quality assurance and quality control data for the above
referenced sample group to identify potential bias or inaccuracy, in general accordance with the
following United States Environmental Protection Agency documents:
• Region III Modifications to Functional Guidelines for Organic Data Review Multi -Media,
Multi -Concentration, September 1994;
• Region III Modifications to the Laboratory Data Validation Functional Guidelines for
Evaluating Inorganic Analyses, April 1993; and
• Laboratory Data Validation Functional Guidelines for Evaluating Inorganic Analyses, July
1998.
COMPLIANCE ANALYTE LIST(S) (check all that apply)
NC Closed Facility/C & D List
X NC Appendix I VOAs and NC RCRA Metals
NC Appendix I + Detects
X MNA Parameters
X NC Appendix II + C&D + MNA
NC Subtitle D Leachate List
Other: Hg, Cyanide, Sulfate, Sulfide, Alkalinity, Chloride, TDS
1.0 CHAIN OF CUSTODY (COC) REVIEW
NTT COC was properly signed by all parties.
NTT Correct project name and number are on the form.
NTT Sample receipt condition at laboratory was acceptable.
NTT Each sample and blank submitted for analysis appears in the report.

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 2 of 4
2.0 SAMPLE HOLDING TIMES
NTT Holding times for extraction and/or analysis were met for each analytical
Method (see below for reference).
GOLDER
Review Criteria
Method
Anal tes
HoldingTime
SW-846 Method 8260 and 8011
VOCs
14 days
SW-846 Methods 8270, 8080,
8081, 8082, and 8151
SVOCs, PCBs,
pesticides and
herbicides
7 days for extraction, 40 days
from extraction for analysis
SW-846 Methods 6000 and 7000
Series
Metals except mercury
6 months (no temperature
requirements)
SW-846 Method 7470
Mercury
28 days
SM18 4500-S2 D
Sulfide
7 days
SW-846 Method 9010
Cyanide
14 days
EPA Method 300
Nitrate/Sulfate
48 hours/28 days
EPA Method 405.1
BOD
48 hours
EPA Method 410.4
COD
28 days
EPA Method 365.4
Phosphorous
28 days
3.0 LABORATORY QUALITY CONTROL REVIEW
NTT Laboratory analyzed at least one internal blank for each method, where applicable.
NTT Laboratory blank is interference -free.
NTT Surrogate recoveries are provided for each analytical method, where applicable.
NTT Surrogate recoveries for each method are within the acceptable limits (i.e., at least
50% of the surrogates were within range).
NTT MS/MSD/LCS data results are provided for each analytical method.
NTT MS/MSD/LCS recoveries for each method are within the acceptable limits (i.e., at least
1 of the 3 were within range).
The spike recovery of 1,4-Dioxane was outside of control limits for the 8260D SIM MS and
MSD samples. The QC batch was approved based on acceptable LCS recovery of this
analyte.
➢ The spike recovery of Iron was outside of control limits for the 6010D MS, MSD, and Post
Spike samples. The QC batch was approved based on acceptable LCS recovery of this
element.
➢ The spike recoveries of Alkalinity, Chloride, Sulfate, and Sulfide were outside of control
limits for the MS or MSD samples. The QC batches were approved based on acceptable
LCS recovery of these analytes.
4.0 ANALYTE LISTS/METHODS
NTT The proper number of constituents are present for each analyte list as identified above
(including detects where applicable).
NTT Proper EPA SW-846 analytical methods were used for analysis.

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 3 of 4
Notes:
5.0 DATA REPORTING
GOLDER
NTT All analytical reporting associated with the event was performed by the contracted lab
NTT Trip, field and/or equipment, and laboratory blank results have all been reported. All
detects for blanks are listed below by constituent. All laboratory method blanks, if any,
have been `flagged' with a `B' where detected in other samples as appropriate and a
laboratory narrative was provided. If the sample was flagged by the laboratory and is
not within 5X of the concentration in the blank (or 10X for commonly detected laboratory
contaminants -acetone, methylene chloride and phthalates), list below with explanation
if flags should be removed. If flags need to be added for samples, also list below.
NTT It is clear from the laboratory report that samples have or have not been diluted during
analysis, and if the samples have been diluted, the result is reported as a multiple of
the dilution (e.g., a sample diluted 10x resulting in an analytical detection of 1.0 should
be reported as 10). Those that have been diluted are listed below with the dilution
factor.
y Antimony: 2x in MW-13D, MW-13S, MW-11 DR, MW-17D and Field Blank
Thallium: 2x in MW-13D, MW-13S, MW-11 DR, MW-17D and Field Blank
➢ Alkalinity 2x in MW-11 DR
NTT
The report provides the reporting limit for each constituent.
NTT
The results were reported at or below their proper reporting limits. Those that are not
reported correctly are listed below (by constituent) with the proper reporting limit listed
beside them. State if the reporting limit error is due to dilutions.
NTT
No inorganic or organic constituents were reported above their respective NC 2L
Drinking Water Standards or IMAC
standards in wells, surface points, or
field/equipment/trip blanks.
➢
Benzene (NC2L = 1 ug/L)
• MW-11 DR @ 1.6 ug/L
➢ Iron (NC2L = 300 ug/L)
• MW-8 @ 2.9 ug/L
0 MW-13S @99700 ug/L
• MWA3S @ 1.1 ug/L
• MW-11DR @ 75900 ug/L
• MW-13D @ 6040 ug/L
➢
VinVI Chloride (NC2L = 0.03 ug/L)
• MWA 1 DR @ 1.3 ug/L
➢ Manganese (NC2L = 50 uq/L)
• MW-13S @ 0.70 ug/L (J)
MW-13S @ 189 ug/L
• MWA 1 DR @ 191 ug/L
➢
1,4 Dioxane (NC2L = 3.0 uq/L)
• MW-8 @ 39 ug/L
➢ Cis-1-2-Dicholorethene
• MWA 1 DR @ 3.9 ug/L
(NC2L=0.4 ug/L)
• MW-13D @ 2.8 ug/L
MWA3D @ 0.71 ug/L (J)
• MW-13S @ 6.0 ug/L
• MW-17D @ 5.2 ug/L
➢ 1,4-Dichlorobenzene
• SWA @ 1.3 ug/L (J)
(NC2L=6.0 uq/L)
• SW-3 @ 2.5 ug/L
• MW-8 @ 6.2 ug/L
• SW-4 @ 1.0 ug/L (J)

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 4 of 4
GOLDER
NTT No quantifiable inorganic or organic constituents were detected in a well or surface
water point at concentrations outside of their historical range (more than 5X previous
concentrations or first-time detections).
1ST time detection of 1,4-dioxane on MW-17D (5.2 ug/L)
1,4-Dichlorobenzene in MW-8 at 6.2 ug/L, outside historical range.
NTT Other report issues/Communications with laboratory/etc.:
y The 8260D Continuing Calibration Verification sample (CCV) exhibited a high bias for 1,1,1-
Trichloroethane, 1,1-Dichloroethane, Acetone, Acrylonitrile, Benzene,
Bromochloromethane, Carbon Disulfide, Carbon Tetrachloride, Chloroform,
Chloromethane, cis-1,2-Dichloroethene, lodomethane, trans-1,2-Dichloroethene,
Trichloroethene, Trichlorofluoromethane, Vinyl Chloride, and Tetrahydrofuran. The LCS
sample also exhibited a high bias for Bromochloromethane. However, these analytes were
not detected in the associated samples, reducing the impact of the deviation.

WORK ORDER Printed: 12/13/2019 11:41:13AM
CC18640
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore Co LIT Project Number: 19127453.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: John C King Date Received: 22-Nov-19 07:00
Logged In By: John C King Date Logged In: 22-Nov-19 08:53
Work Order Comments:
C-1854 received at 1.1°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temoeratme Corrected Y
Page 1 of 1

WORK ORDER Printed: 12/13/2019 11:40:53AM
CC19666
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore Co LIT Project Number: 19127453.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: John C King Date Received: 22-Nov-19 07:00
Logged In By: John C King Date Logged In: 22-Nov-19 09:00
Work Order Comments:
C-1854 received at 1.1°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temoeratme Corrected Y
Page 1 of 1

Environmental Conservation Laboratories, Inc.
102-A Woodwinds Industrial Court
Cary NC, 27511
Phone: [phone] FAX: [phone]
Monday, December 16, 2019
Golder Associates, Inc. (G0007)
Attn: Ben Draper
5B Oak Branch Drive
Greensboro, NC 27407
RE: Laboratory Results for
Project Number: 19127453.100, Project Name/Desc: Moore Co LF- Blake Residence
ENCO Workorder(s): CC18641
Dear Ben Draper,
Enclosed is a copy of your laboratory report for test samples received by our laboratory on
Friday, November 22, 2019.
Unless otherwise noted in an attached project narrative, all samples were received in
acceptable condition and processed in accordance with the referenced methods/procedures.
Results for these procedures apply only to the samples as submitted.
The analytical results contained in this report are in compliance with NELAC standards, except
as noted in the project narrative if applicable. This report shall not be reproduced except in
full, without the written approval of the Laboratory.
This report contains only those analyses performed by Environmental Conservation
Laboratories. Unless otherwise noted, all analyses were performed at ENCO Cary. Data from
outside organizations will be reported under separate cover.
If you have any questions or require further information, please do not hesitate to contact me.
Sincerely,
Stephanie Franz For Meghan K Shea
Project Manager
Enclosure(s)
(� �C—o
www.encolabs.com
The total number of pages in this report, including this page is 16.
Page 1 of 17

PROJECT NARRATIVE
Date: 16 December 2019
Client: Golder Associates, Inc. (G0007)
Project: Moore Co LF- Blake Residence
Lab ID: CC18641
Overview
(� 0a
www.encolabs.com
Environmental Conservation Laboratories, Inc. (ENCO) analyzed all submitted samples in accordance with the methods
referenced in the laboratory report. Any particular difficulties encountered during sample handling by ENCO are discussed in
the QC Remarks section below.
Quality Control Samples
The 8260D Continuing Calibration Verification sample (CCV) exhibited a high bias for 1,1-Dichloroethane,
1,1-Dichloroethene, Acrylonitrile, Bromochloromethane, Carbon Disulfide, Chloroform, Chloromethane,
cis- 1,2-Dichloroethene, Trichlorofluoromethane, and Vinyl chloride; however, these analytes were not detected in the
associated sample, reducing the impact of the deviation.
Quality Control Remarks
No Comments
Other Comments
All samples received under this work order arrived in acceptable conditions. The samples were not checked for residual
chlorine, as it is not required.
The analytical data presented in this report are consistent with the methods as referenced in the analytical report. Any
exceptions or deviations are noted in the QC remarks section of this narrative or in the Flags/Notes and Definitions section of
the report.
Released By:
Environmental Conservation Laboratories, Inc.
Stephanie Franz
Project Manager
Page 2 of 16
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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-Blake Residence
Lab ID: CC18641-01
Sampled: 11/20/19 12:15
Received: 11/22/19 07:00
Parameter Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 6010D EPA 3005A
O5/18/20
12/02/19 09:35
12/05/19 14:49
EPA 7470A EPA 7470A
12/18/19
12/02/19 12:21
12/03/19 16:00
EPA 8260D EPA 5030B_MS
12/04/19
12/03/19 13:41
12/03/19 23:42
Client ID: 6301-Blake Residence
Lab ID: CC18641-01RE1
Sampled: 11/20/19 12:15
Received: 11/22/19 07:00
Parameter Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D EPA 5030B_MS
12/04/19
11/27/19 00:00
11/27/19 12:18
Page 3 of 16
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NORTH CAROLINA SWS SAMPLE DETECTION SUMMARY
lient ID: 6301-Blake Residence
Lab ID:
CC18641-01
Analyte
Results Flag DF MDL
MRL NC SWSL
Units Method Notes
Barium - Total
20.7 1 1.10
10.0 NE
ug/L EPA 6010D
Lead - Total
26.3 1 3.10
10.0 NE
ug/L EPA 6010D
Page 4 of 16
Page 4 of 17

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ANALYTICAL RESULTS
Description: 6301-Blake Residence Lab Sample ID: CC18641-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled: 11/20/19 12:15 Work Order: CC18641
Project: Moore Co LF- Blake Residence Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
^ - ENCO Cary certified analyte [NC 591]
Analyte [CAS Numberl
Results
Flan
Units
DF
MDL
MRL NC SWSL
Method
Analyzed
ft
Notes
1,1,1,2-Tetrachloroethane [630-20-6] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
1,1,1-Trichloroethane [71-55-6] ^
0.12
U
ug/L
1
0.12
1.0
EPA 8260D
12/03/19 23:42
REF
1,1,2,2-Tetrachloroethane [79-34-5] ^
0.28
U
ug/L
1
0.28
1.0
EPA 8260D
12/03/19 23:42
REF
1,1,2-Trichloroethane [79-00-5] ^
0.14
U
ug/L
1
0.14
1.0
EPA 8260D
12/03/19 23:42
REF
1,1-Dichloroethane [75-34-3] ^
0.13
U
ug/L
1
0.13
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
1,1-Dichloroethene [75-35-4] ^
0.21
U
ug/L
1
0.21
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
1,2,3-Trichloropropane [96-18-4] ^
0.23
U
ug/L
1
0.23
1.0
EPA 8260D
12/03/19 23:42
REF
1,2-Dibromo-3-chloropropane [96-12-8] ^
0.48
U
ug/L
1
0.48
1.0
EPA 8260D
12/03/19 23:42
REF
1,2-Dibromoethane [106-93-4] ^
0.66
U
ug/L
1
0.66
1.0
EPA 8260D
12/03/19 23:42
REF
1,2-Dichlorobenzene [95-50-1] ^
0.19
U
ug/L
1
0.19
1.0
EPA 8260D
12/03/19 23:42
REF
1,2-Dichloroethane [107-06-2] ^
0.21
U
ug/L
1
0.21
1.0
EPA 8260D
12/03/19 23:42
REF
1,2-Dichloropropane [78-87-5] ^
0.10
U
ug/L
1
0.10
1.0
EPA 8260D
12/03/19 23:42
REF
1,4-Dichlorobenzene [106-46-7] ^
0.19
U
ug/L
1
0.19
1.0
EPA 8260D
12/03/19 23:42
REF
2-Butanone [78-93-3] ^
1.3
U
ug/L
1
1.3
5.0
EPA 8260D
12/03/19 23:42
REF
2-Hexanone [591-78-6] ^
0.88
U
ug/L
1
0.88
5.0
EPA 8260D
12/03/19 23:42
REF
4-Methyl-2-pentanone [108-10-1] ^
1.1
U
ug/L
1
1.1
5.0
EPA 8260D
12/03/19 23:42
REF
Acetone [67-64-1] ^
10
U
ug/L
1
10
20
EPA 8260D
12/03/19 23:42
REF
Acrylonitrile [107-13-1] ^
3.5
U
ug/L
1
3.5
10
EPA 8260D
12/03/19 23:42
REF
QV-01
Benzene [71-43-2] ^
0.15
U
ug/L
1
0.15
1.0
EPA 8260D
12/03/19 23:42
REF
Bromochloromethane [74-97-5] ^
0.48
U
ug/L
1
0.48
1.0
EPA 8260D
12/03/19 23:42
REF
QL-02,
QV-01
Bromodichloromethane [75-27-4] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
Bromoform [75-25-2] ^
0.22
U
ug/L
1
0.22
1.0
EPA 8260D
12/03/19 23:42
REF
Bromomethane [74-83-9] ^
0.14
U
ug/L
1
0.14
1.0
EPA 8260D
12/03/19 23:42
REF
Carbon disulfide [75-15-0] ^
1.5
U
ug/L
1
1.5
5.0
EPA 8260D
12/03/19 23:42
REF
QV-01
Carbon tetrachloride [56-23-5] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
Chlorobenzene [108-90-7] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
Chloroethane [75-00-3] ^
0.23
U
ug/L
1
0.23
1.0
EPA 8260D
12/03/19 23:42
REF
Chloroform [67-66-3] ^
0.18
U
ug/L
1
0.18
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
Chloromethane [74-87-3] ^
0.13
U
ug/L
1
0.13
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
cis-1,2-Dichloroethene [156-59-2] ^
0.15
U
ug/L
1
0.15
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
cis-1,3-Dichloropropene [10061-01-5] ^
0.20
U
ug/L
1
0.20
1.0
EPA 8260D
12/03/19 23:42
REF
Dibromochloromethane [124-48-1] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
Dibromomethane [74-95-3] ^
0.27
U
ug/L
1
0.27
1.0
EPA 8260D
12/03/19 23:42
REF
Ethylbenzene [100-41-4] ^
0.13
U
ug/L
1
0.13
1.0
EPA 8260D
12/03/19 23:42
REF
Iodomethane [74-88-4] ^
1.7
U
ug/L
1
1.7
5.0
EPA 8260D
12/03/19 23:42
REF
Methylene chloride [75-09-2] ^
0.23
U
ug/L
1
0.23
1.0
EPA 8260D
12/03/19 23:42
REF
Styrene [100-42-5] ^
0.11
U
ug/L
1
0.11
1.0
EPA 8260D
12/03/19 23:42
REF
Tetrachloroethene [127-18-4] ^
0.17
U
ug/L
1
0.17
1.0
EPA 8260D
12/03/19 23:42
REF
Toluene [108-88-3] ^
0.14
U
ug/L
1
0.14
1.0
EPA 8260D
12/03/19 23:42
REF
trans-1,2-Dichloroethene [156-60-5] ^
0.21
U
ug/L
1
0.21
1.0
EPA 8260D
12/03/19 23:42
REF
trans-1,3-Dichloropropene [10061-02-6] ^
0.15
U
ug/L
1
0.15
1.0
EPA 8260D
12/03/19 23:42
REF
trans-1,4-Dichloro-2-butene [110-57-6] ^
0.70
U
ug/L
1
0.70
1.0
EPA 8260D
12/03/19 23:42
REF
Trichloroethene [79-01-6] ^
0.15
U
ug/L
1
0.15
1.0
EPA 8260D
12/03/19 23:42
REF
Trichlorofluoromethane [75-69-4] ^
0.24
U
ug/L
1
0.24
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
Vinyl acetate [108-05-4] ^
0.95
U
ug/L
1
0.95
5.0
EPA 8260D
12/03/19 23:42
REF
Vinyl chloride [75-01-4] ^
0.32
U
ug/L
1
0.32
1.0
EPA 8260D
12/03/19 23:42
REF
QV-01
Xylenes(Total) [1330-20-7] ^
0.45
U
ug/L
1
0.45
3.0
EPA 8260D
12/03/19 23:42
REF
Page 5 of 16
Page 5 of 17

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Description: 6301-Blake Residence
Lab Sample ID: CC18641-01
Received: 11/22/19 07:00
Matrix: Ground Water
Sampled: 11/20/19 12:15
Work Order: CC18641
Project: Moore Co LF- Blake Residence
Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
- - - - - - - - - - - - - - - - - - -
- - -
- - - -
- - - - - - - - - - - - - -
- - - - -
- - - - - - - - - - - - -
^ - ENCO Cary certified anaiyte [NC 591]
Analyte MAS Numberl Results
Flag
Units
DF MDL MRL NC SWSL
Method
Analyzed By Notes
Surrogates Results
DF
Spike Lvi
% Rec % Rec Limits Batch
Method
Analyzed By Notes
4-8romofluorobenzene 47
1
50.0
94 % 53-136 9LO3036
EPA 8260D
12103119 23:42 REF
Dibromofluoromethane 54
1
50.0
108% 67-129 9LO3036
EPA8260D
1210311923:42 REF
Toluene-d8 54
1
50.0
109 % 59-134 9LO3036
EPA8260D
1210311923:42 REF
Page 6 of 16
Page 6 of 17

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Description: 6301-Blake Residence Lab Sample ID: CC18641-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled: 11/20/19 12:15 Work Order: CC18641
Project: Moore Co LF- Blake Residence Sampled By: Nicolas Tejada
Metals by EPA 6000/7000 Series Methods
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flaa Units DF MDL MRL INC SWSL Method Analyzed IX Notes
Mercury [7439-97-61 A 0.150 u ug/L 1 0.150 0.200 EPA 7470A 12/03/19 16:00 KAH
Page 7 of 16
Page 7 of 17

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Description: 6301-Blake Residence Lab Sample ID: CC18641-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled: 11/20/19 12:15 Work Order: CC18641
Project: Moore Co LF- Blake Residence Sampled By: Nicolas Tejada
Metals (total recoverable) by EPA 6000/7000 Series Methods
- - - - - - - - - - - - - - - - - - - - - - - - - - -
- -
- - - -
- - - - - - -
- - - - -
- - - - - - -
- - - - - -
^ - ENCO Cary certified anaiyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
MRL NC SWSL
Method
Analyzed
Ay Notes
Arsenic [7440-38-2] ^
7.60
U
ug/L
1
7.60
10.0
EPA 6010D
12/05/19 14:49
JDH
Barium [7440-39-3] ^
20.7
ug/L
1
1.10
10.0
EPA 6010D
12/05/19 14:49
JDH
Cadmium [7440-43-9] ^
0.360
U
ug/L
1
0.360
1.00
EPA 6010D
12/05/19 14:49
JDH
Chromium [7440-47-3] ^
1.40
U
ug/L
1
1.40
10.0
EPA 6010D
12/05/19 14:49
JDH
Lead [7439-92-1] ^
26.3
ug/L
1
3.10
10.0
EPA 6010D
12/05/19 14:49
JDH
Selenium [7782-49-2] ^
6.20
U
ug/L
1
6.20
10.0
EPA 6010D
12/05/19 14:49
JDH
Silver [7440-22-4] ^
1.90
U
ug/L
1
1.90
10.0
EPA 6010D
12/05/19 14:49
JDH
Page 8 of 16
Page 8 of 17

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Description: 6301-Blake Residence Lab Sample ID: CC18641-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled: 11/20/19 12:15 Work Order: CC18641
Project: Moore Co LF- Blake Residence Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
^ - ENCO Orlando Certified analyte [NC 424]
Analyte fCAS Numberl Results Flaa Units DF MDL MRL NC SWSL Method Analyzed AX Notes
1,4-Dioxane [123-91-1] A 0.80 u ug/L 1 0.80 2.0 EPA 8260D 11/27/19 12:18 KKW
Surrogates Results DF Spike Lvl %Rec % Rec Limits Batch Method Analyzed By Notes
Toluene-d8 4.8 1 5.00 96 % 75-125 9K27030 EPA 6260D 1112711912:18 KKW
This report relates only to the sample as received by the laboratory, and may only be reproduced in full.
Page 9 of 16
Page 9 of 17

QUALITY CONTROL
Volatile Organic Compounds by GCMS - Quality Control
Batch 9LO3036 - EPA 5030E MS
(� 0a
www.encolabs.com
Blank (91.03036-BLK1)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
�Analyte
Spike Source %REC RPD
Result
Flag
MRL
Units Level Result %REC Limits RPD Limit Notes
1,1,1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
5urrogate:4-Bromofluorobenzene 47 ug/L 50.0 93 53-136
Page 10 of 16
Page 10 of 17

QUALITY CONTROL
Volatile Organic Compounds by GCMS - Quality Control
Batch 9LO3036 - EPA 5030E MS
(� 0a
www.encolabs.com
Blank (9L03036-BLK1) Continued
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
Surrogate: Dibromofluoromethane
54
ug/L
50.0 107 67-129
Surrogate: Toluene-c48
53
ug/L
50.0 106 59-134
- - - - - - - - - - - - - -
LCS (9L03036-BS1)
- - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 16:43
- - - -
- - - -
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
1,1-Dichloroethene
23
1.0
ug/L
20.0 116 75-133
Benzene
23
1.0
ug/L
20.0 116 80-134
Chlorobenzene
19
1.0
ug/L
20.0 94 80-120
Toluene
19
1.0
ug/L
20.0 94 71-120
Trichloroethene
23
1.0
ug/L
20.0 117 74-120
- - - - - - - - - - - - - -
Matrix Spike (9L03036-MS1)
- - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:15
- - - -
- - - -
Source: CC18494-01
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
1,1-Dichloroethene
24
1.0
ug/L
20.0 0.21 U 122 75-133
Benzene
25
1.0
ug/L
20.0 0.15 U 125 80-134
Chlorobenzene
19
1.0
ug/L
20.0 0.17 U 93 80-120
Toluene
19
1.0
ug/L
20.0 0.14 U 97 71-120
Trichloroethene
21
1.0
ug/L
20.0 0.15 U 106 74-120
- - - - - - - - - - - - - -
Matrix Spike Dup (9L03036-MSD1)
- - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:47
- - - -
- - - -
Source: CC18494-01
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
1,1-Dichloroethene
25
1.0
ug/L
20.0 0.21 U 127 75-133 4
20
Benzene
24
1.0
ug/L
20.0 0.15 U 120 80-134 4
17
Chlorobenzene
19
1.0
ug/L
20.0 0.17 U 93 80-120 0.2
16
Toluene
20
1.0
ug/L
20.0 0.14 U 98 71-120 1
17
Trichloroethene
- - - - - - - - - - - - - -
22
- - - -
- - -
1.0
- - - -
ug/L
- - - -
20.0 0.15 U 112 74-120 5
- - - - - - - - - - - - - - - - - - - -
22
- - - -
- - -
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9LO2030 - EPA 7470A
Blank (9L02030-BLKI)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:20
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
- - - - - - - - - - - - - -
0.150
- - - -
U
- - -
0.200
- - - -
ug/L
- - - -
- - - - - - - - - - - - - - - - - - - -
- - - -
- - - -
LCS (9L02030-BSI)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:23
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
5.04
0.200
ug/L
5.00 101 80-120
- - - - - - - - - - - - - -
Matrix Spike (9L02030-MS1)
- - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:28
- - - -
- - - -
Page 11 of 16
Page 11 of 17

QUALITY CONTROL
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02030 - EPA 7470A
(� 0a
www.encolabs.com
Matrix Spike (9L02030-MS3) Continued Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:28
Source: CC18494-01
Spike Source %REC RPD
�Analyte Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
Mercury 4.62 0.200 ug/L 5.00 0.150 U 92 75-125
Matrix Spike Dup (9L02030-MSD1) Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:30
Source: CC18494-01
Spike Source %REC RPD
�Analyte Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
Mercury 4.21 0.200 ug/L 5.00 0.150 U 84 75-125 9 25
Post Spike (9L02030-PS3) Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:32
Source: CC18494-01
Spike Source %REC RPD
�Analyte Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
Mercury 4.46 0.200 ug/L 5.00 0.0430 88 75-125
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02012 - EPA 3005A
Blank (9L02012-BLK1)
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 10:29
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Lead
3.10
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
- - - - - - - - - - - - -
LCS (9L02012-BS1)
- - - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:16
- - - - - - - -
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit Notes
Arsenic
187
10.0
ug/L
200 94 80-120
Barium
183
10.0
ug/L
200 91 80-120
Cadmium
18.4
1.00
ug/L
20.0 92 80-120
Chromium
184
10.0
ug/L
200 92 80-120
Lead
185
10.0
ug/L
200 92 80-120
Selenium
185
10.0
ug/L
200 92 80-120
Silver
192
10.0
ug/L
200 96 80-120
- - - - - - - - - - - - -
Matrix Spike (9L02012-MS1)
- - - - -
- - -
- - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:19
- - - - - - - -
Source: CC18513-03
�Analyte
Spike Source %REC
RPD
Result
Flag
MRL
Units
Level Result %REC Limits RPD
Limit Notes
Arsenic
182
10.0
ug/L
200 7.60 U 91 75-125
Barium
215
10.0
ug/L
200 32.4 92 75-125
Page 12 of 16
Page 12 of 17

(� �C-O
www.encolabs.com
QUALITY CONTROL
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9LO2012 - EPA 3005A
Matrix Spike (9L02012-MS3) Continued
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:19
Source: CC18513-03
inalyte
OF
Spike
Source
%REC
RPD
Result
F
m
Level
Result
%REC Limits RPD
Limit Notes
Cadmium
18.2
1.00
ug/L
20.0
0.360 U
91 75-125
Chromium
186
10.0
ug/L
200
1.40 U
93 75-125
Lead
186
10.0
ug/L
200
3.10 U
93 75-125
Selenium
186
10.0
ug/L
200
6.20 U
93 75-125
Silver
194
10.0
ug/L
200
1.90 U
97 75-125
- - - - - - - - - - - - - - -
Matrix Spike Dup (9L02012-MSD1)
- - -
- - - - - - -
- - - -
- - - - -
Prepared:
- - - -
12/02/2019
- - - - - - - - - - -
09:35 Analyzed: 12/05/2019 13:22
- - - - - - - -
Source: CC18513-03
�Analyte
Spike
Source
%REC
RPD
m
Level
Result
%REC Limits RN
Limit Notes
Arsenic
185
10.0
ug/L
200
7.60 U
92 75-125 1
20
Barium
221
10.0
ug/L
200
32.4
95 75-125 3
20
Cadmium
18.5
1.00
ug/L
20.0
0.360 U
93 75-125 2
20
Chromium
191
10.0
ug/L
200
1.40 U
96 75-125 3
20
Lead
188
10.0
ug/L
200
3.10 U
94 75-125 0.8
20
Selenium
182
10.0
ug/L
200
6.20 U
91 75-125 2
20
Silver
199
10.0
ug/L
200
1.90 U
100 75-125 3
20
- - - - - - - - - - - - - - -
Post Spike (9L02012-PSI)
- - -
- - - - - - -
- - - -
- - - - -
Prepared:
- - - -
12/02/2019
- - - - - - - - - - -
09:35 Analyzed: 12/05/2019 13:24
- - - - - - - -
Source:CC18513-03
Lalyte
Spike
Source
%REC
Result
Flag MRL
Units
Level
Result
%REC Limits RPD
Arsenic
0.185
0.0100
mg/L
0.200
-0.00934
93 80-120
Barium
0.221
0.0100
mg/L
0.200
0.0324
94 80-120
Cadmium
0.0190
0.00100
mg/L
0.0200
-0.000194
95 80-120
Chromium
0.193
0.0100
mg/L
0.200
0.000391
96 80-120
Lead
0.196
0.0100
mg/L
0.200
0.000195
98 80-120
Selenium
0.187
0.0100
mg/L
0.200
-0.00931
93 80-120
Silver
- - - - - - - - - - - - - - -
0.210
- - -
0.0100
- - - - - - -
mg/L
- - - -
0.200
- - - - -
0.000488
- - - -
105 80-120
- - - - - - - - - - -
- - - - - - - -
QUALITY CONTROL
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9K26034 - EPA 5030B M5
Blank (9K26034-BLK1) Prepared: 11/26/2019 12:49 Analyzed: 11/27/2019 00:32
Spike Source %REC RPD
�Analyte Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 0.80 U 2.0 ug/L
Surrogate: Toluene-& 5.9 ug/L 5.00 119 75-125
LCS (9K26034-BSI) Prepared: 11/26/2019 12:49 Analyzed: 11/26/2019 22:10
Spike Source %REC RPD
�A.alyte Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 24 2.0 ug/L 25.0 98 80-133
Surrogate: Toluene-& 5.5 ug/L 5.00 111 75-125
Page 13 of 16
Page 13 of 17

(� �C—O
www.encolabs.com
QUALITY CONTROL
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9K26034 - EPA 5030E MS
Matrix Spike (9K26034-MSI) Prepared: 11/26/2019 12:49 Analyzed: 11/26/2019 22:46
Source:AC08257-01
Spike Source %REC RPD
�Analyte IL Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 23 2.0 ug/L 25.0 1.0 89 80-133
Surrogate: Toluene-d8 5.0 ug/L 5.00 99 75-125
Matrix Spike Dup (9K26034-MSD1) Prepared: 11/26/2019 12:49 Analyzed: 11/26/2019 23:22
Source:AC08257-01
Spike Source %REC RPD
IF Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 25 2.0 ug/L 25.0 1.0 98 80-133 9 19
Surrogate: Toluene-&
- - - - - - - - - - - - -
4.8
- - - - - - - - - - - -
ug/L
- - - -
5.00 96 75-125
- - - - - - - - - - - - - - - - - - - -
- - - - - - - -
Batch 9K27030 - EPA 5030E MS
Blank (9K27030-BLK3)
Prepared: 11/27/2019 00:00 Analyzed: 11/27/2019 11:13
�Analyte
Spike Source %REC
RPD
Flag MRL
Units
Level Result %REC Limits RPD
Limit Notes
1,4-Dioxane
0.80 U 2.0
ug/L
Surrogate: Toluene-&
5.0
ug/L
5.00 100 75-125
- - - - - - - - - - - -
LCS (9K27030-BSI)
- - - - - - - - - - - -
- - - -
- - - - - - - - - - - - - - - - - - - -
Prepared: 11/27/2019 00:00 Analyzed: 11/27/2019 10:08
- - - - - - - -
IW—Level
Spike Source %REC
RPD
nalyte it
Result
Result %REC Limits RPD
Limit
1,4-Dioxane
25 2.0
ug/L
25.0 99 80-133
Surrogate: Toluene d8
5.2
ug/L
5.00 103 75-125
Matrix Spike (9K27030-MS1) Prepared: 11/27/2019 00:00 Analyzed: 11/27/2019 20:04
Source:AC08263-01
Spike Source %REC RPD
Analyte Result Flag MRL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 26 2.0 ug/L 25.0 1.8 97 80-133
Surrogate: Toluene-d8 5.8 U91L 5.00 116 75-125
Matrix Spike Dup (9K27030-MSD1) Prepared: 11/27/2019 00:00 Analyzed: 11/27/2019 20:41
Source: AC08263-01
Spike Source %REC RPD
7.1yte L.I. Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 25 2.0 ug/L 25.0 1.8 92 80-133 5 19
Surrogate: Toluene-& 4.7 ug/L 5.00 95 75-125
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
Page 14 of 16
Page 14 of 17

(� 0a
www.encolabs.com
FLAGS/NOTES AND DEFINITIONS
B The analyte was detected in the associated method blank.
D The sample was analyzed at dilution.
J The reported value is between the laboratory method detection limit (MDL) and the laboratory method
reporting limit (MRL), adjusted for actual sample preparation data and moisture content, where applicable.
U The analyte was analyzed for but not detected to the level shown, adjusted for actual sample preparation
data and moisture content, where applicable.
E The concentration indicated for this analyte is an estimated value above the calibration range of the
instrument. This value is considered an estimate.
MRL Method Reporting Limit. The MRL is roughly equivalent to the practical quantitation limit (PQL) and is
based on the low point of the calibration curve, when applicable, sample preparation factor, dilution
factor, and, in the case of soil samples, moisture content.
PQL PQL: Practical Quantitation Limit. The PQL presented is the laboratory MRL.
N The analysis indicates the presence of an analyte for which there is presumptive evidence (85% or greater
confidence) to make a "tentative identification".
P Greater than 25% concentration difference was observed between the primary and secondary GC column.
The lower concentration is reported.
[CALC] Calculated analyte - MDL/MRL reported to the highest reporting limit of the component analyses.
QL-02 The associated laboratory control sample exhibited high bias; since the result is ND, there is no impact.
QV-01 The associated continuing calibration verification standard exhibited high bias; since the result is ND, there
is no impact.
Page 15 of 16
Page 15 of 17

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Sample Preservation Verification.
ENCO Cary
Work Order: CC18641
Client: Golder Associates, Inc. (GO007)
Project: Moore Co LF- Blake Residence
Project #: 0739615018.100
Logged In: 07-Nov-19 08:50 Logged By: John C King
Preservation Check Performed By: i �� Date/Time: _ 1 I AOD
CC18641-01
Coat
Type
Pres (pH) pH Checked/
Requirement _tg Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
A
250mLP+HNO3
<2 Y N / NA
Y /% N, ! NA
Reagent Name ID
1
2 1 i
pH Strip ID: �� psa'g--
Rea ent Name ID
3
4
Rea ent Name ID
5
6
C:IELMN-RP rintlwko_PreservationCheck. rpt
Page 17 of 17
age 1

GOLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY CONTROL
LABORATORY DATA REVIEW
Page 1 of 3
Project Name: Moore County Landfill- Blake Residence
Project Reference Number: 19127453.100
Sampling Event Date: November 22, 2019
Review Date: December 17, 2019
Report #: CC18641
Signature:
QA/QC Sign Off:
Date:
Date:
GOLDER
Initials: NTT
Person(s) performing the review are to initial each item on this form as acknowledgement
of data acceptance, or as acknowledgement of a review issue. In the case of the latter, a
brief explanation should follow the applicable item.
Golder Associates Inc. has reviewed the laboratory certificates of analysis, chain -of -custody form,
and laboratory provided sample group quality assurance and quality control data for the above
referenced sample group to identify potential bias or inaccuracy, in general accordance with the
following United States Environmental Protection Agency documents:
• Region III Modifications to Functional Guidelines for Organic Data Review Multi -Media,
Multi -Concentration, September 1994;
• Region III Modifications to the Laboratory Data Validation Functional Guidelines for
Evaluating Inorganic Analyses, April 1993; and
• Laboratory Data Validation Functional Guidelines for Evaluating Inorganic Analyses, July
1998.
COMPLIANCE ANALYTE LIST(S) (check all that apply)
NC Closed Facility/C & D List
X NC Appendix I VOAs and NC RCRA Metals
NC Appendix I + Detects
MNA Parameters
NC Appendix II + C&D + MNA (MW-4 and MW-16S)
NC Subtitle D Leachate List
Other:
1.0 CHAIN OF CUSTODY (COC) REVIEW
NTT COC was properly signed by all parties.
NTT Correct project name and number are on the form.
NTT Sample receipt condition at laboratory was acceptable.
NTT Each sample and blank submitted for analysis appears in the report.

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 2 of 3
2.0 SAMPLE HOLDING TIMES
NTT Holding times for extraction and/or analysis were met for each analytical
Method (see below for reference).
GOLDER
Review Criteria
Method
Anal tes
HoldingTime
SW-846 Method 8260 and 8011
VOCs
14 days
SW-846 Methods 8270, 8080,
8081, 8082, and 8151
SVOCs, PCBs,
pesticides and
herbicides
7 days for extraction, 40 days
from extraction for analysis
SW-846 Methods 6000 and 7000
Series
Metals except mercury
6 months (no temperature
requirements)
SW-846 Method 7470
Mercury
28 days
SM18 4500-S2 D
Sulfide
7 days
SW-846 Method 9010
Cyanide
14 days
EPA Method 300
Nitrate/Sulfate
48 hours/28 days
EPA Method 405.1
BOD
48 hours
EPA Method 410.4
COD
28 days
EPA Method 365.4
Phosphorous
28 days
3.0 LABORATORY QUALITY CONTROL REVIEW
NTT Laboratory analyzed at least one internal blank for each method, where applicable.
NTT Laboratory blank is interference -free.
NTT Surrogate recoveries are provided for each analytical method, where applicable.
NTT Surrogate recoveries for each method are within the acceptable limits (i.e., at least
50% of the surrogates were within range).
NTT MS/MSD/LCS data results are provided for each analytical method.
NTT MS/MSD/LCS recoveries for each method are within the acceptable limits (i.e., at least
1 of the 3 were within range).
4.0 ANALYTE LISTS/METHODS
NTT The proper number of constituents are present for each analyte list as identified above
(including detects where applicable).
NTT Proper EPA SW-846 analytical methods were used for analysis.
Notes:
5.0 DATA REPORTING
NTT All analytical reporting associated with the event was performed by the contracted lab.
NTT Trip, field and/or equipment, and laboratory blank results have all been reported. All
detects for blanks are listed below by constituent. All laboratory method blanks, if any,
have been `flagged' with a `B' where detected in other samples as appropriate and a

OLDER ASSOCIATES NC, INC.
GOLDER
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 3 of 3
laboratory narrative was provided. If the sample was flagged by the laboratory and is
not within 5X of the concentration in the blank (or 1 OX for commonly detected laboratory
contaminants -acetone, methylene chloride and phthalates), list below with explanation
if flags should be removed. If flags need to be added for samples, also list below.
NTT It is clear from the laboratory report that samples have or have not been diluted during
analysis, and if the samples have been diluted, the result is reported as a multiple of
the dilution (e.g., a sample diluted 10x resulting in an analytical detection of 1.0 should
be reported as 10). Those that have been diluted are listed below with the dilution
factor.
NTT The report provides the reporting limit for each constituent.
NTT The results were reported at or below their proper reporting limits. Those that are not
reported correctly are listed below (by constituent) with the proper reporting limit listed
beside them. State if the reporting limit error is due to dilutions.
NTT No inorganic or organic constituents were reported above their respective NC 2L
Drinking Water Standards or IMAC standards in wells, surface points, or
field/equipment/trip blanks.
➢ Lead (NC 2L = 15 uq/L)
• Blake Res @ 26.3 ug/L
NTT No quantifiable inorganic or organic constituents were detected in a well or surface
water point at concentrations outside of their historical range (more than 5X previous
concentrations or first-time detections).
NTT Other report issues/Communications with laboratory/etc.:
➢ The 8260D Continuing Calibration Verification sample (CCV) exhibited a high bias for 1,1-
Dichloroethane, 1,1-Dichloroethene, Acrylonitrile, Bromochloromethane, Carbon Disulfide,
Chloroform, Chloromethane, cis-1,2-Dichloroethene, Trichlorofluoromethane, and Vinyl
chloride; however, these analytes were not detected in the associated sample, reducing the
impact of the deviation.

WORK ORDER Printed: 12/16/2019 9:52:24AM
CC18641
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore Co LF- Blake Residence Project Number: 19127453.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: John C King Date Received: 22-Nov-19 07:00
Logged In By: John C King Date Logged In: 07-Nov-19 08:50
Work Order Comments:
C-2034 received at 0.5°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Page 1 of 1

2�SQ ENCO Laboratories
9g
Accurate. Timely. Respousive. luuavative.
102-A Woodwinds Industrial Court
Cary NC, 27511
Phone: [phone] FAX: [phone]
Wednesday, December 18, 2019
Golder Associates, Inc. (GO007)
Attn: Ben Draper
5B Oak Branch Drive
Greensboro, NC 27407
RE: Laboratory Results for
Project Number: 0739615018.100, Project Name/Desc: Moore County LF
ENCO Workorder(s): CC18642,CC19657,CC19664
Dear Ben Draper,
Enclosed is a copy of your laboratory report for test samples received by our laboratory
between Wednesday, November 20, 2019 and Friday, November 22, 2019.
Unless otherwise noted in an attached project narrative, all samples were received in
acceptable condition and processed in accordance with the referenced methods/procedures.
Results for these procedures apply only to the samples as submitted.
The analytical results contained in this report are in compliance with NELAC standards, except
as noted in the project narrative if applicable. This report shall not be reproduced except in
full, without the written approval of the Laboratory.
This report contains only those analyses performed by Environmental Conservation
Laboratories. Unless otherwise noted, all analyses were performed at ENCO Cary. Data from
outside organizations will be reported under separate cover.
If you have any questions or require further information, please do not hesitate to contact me.
Sincerely,
Stephanie Franz For Meghan K Shea
Project Manager
Enclosure(s)
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 1 of 92

PROJECT NARRATIVE
Date:
18 December 2019
Client:
Golder Associates, Inc. (G0007)
Project:
Moore County LF
Lab ID:
CC18642, CC19657, CC19664
Overview
(� �Eo
www.encolabs.com
Environmental Conservation Laboratories, Inc. (ENCO) analyzed all submitted samples in accordance with the methods
referenced in the laboratory report. Any particular difficulties encountered during sample handling by ENCO are discussed in
the QC Remarks section below.
Quality Control Samples
The spike recovery of 1,4-Dioxane was outside of control limits for the 8260D SIM ID MS and MSD samples. The QC batch
was approved based on acceptable LCS recovery of this analyte. The spike recovery of Trichloroethene was outside of
control limits for the 8260D LCS sample, indicating a possible high bias; however, this analyte was not detected in the
associated sample, reducing the impact of the deviation. The Continuing Calibration Verification sample (CCV) exhibited a
high bias for 1,1-Dichloroethene, Carbon disulfide, and Trichlorofluoromethane; however, these analytes were not detected in
the associated samples.
Precision between duplicate analyses of Methane exceeded acceptance criteria for the RSK-175 analysis. The QC batch
was approved based on acceptable LCS recovery of this analyte.
The spike recoveries of Iron and Mercury were outside of control limits for the MS, MSD, and/or Post spike samples. The
QC batches were approved based on acceptable LCS recovery of these elements.
The spike recoveries of Alkalinity, Chloride, Nitrate/Nitrite (NOx), Nitrite, Sulfate, Sulfide, and TOC were outside of control
limits for the MS and/or MSD samples, and precision between duplicate TDS analyses exceeded acceptance criteria. The
QC batches were approved based on acceptable LCS recovery of these analytes.
Quality Control Remarks
No Comments
Other Comments
All samples received under this work order arrived in acceptable conditions. The samples were not checked for residual
chlorine, as it is not required.
The analytical data presented in this report are consistent with the methods as referenced in the analytical report. Any
exceptions or deviations are noted in the QC remarks section of this narrative or in the Flags/Notes and Definitions section of
the report.
Released By:
Environmental Conservation Laboratories, Inc.
Stephanie Franz
Project Manager
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 2 of 92

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW3
Lab ID: CC18642-01
Sampled: 11/19/19 16:01
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/02/19
22:40
12/02/19
22:40
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:21
EPA 353.2
NO PREP
11/21/19 16:01
11/21/19
08:50
11/21/19
09:57
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
13:11
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
05/17/20
11/25/19
12:44
12/03/19
11:39
EPA 7470A
EPA 7470A
12/17/19
11/21/19
10:14
11/25/19
14:41
EPA 8260D
EPA 503013_MS
12/03/19
11/27/19
16:06
11/28/19
02:35
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
14:12
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
11:55
11/23/19
12:18
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
Client ID: 6301-MW1
Lab ID: CC18642-OIRE1
Sampled: 11/19/19 16:01
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 8260D
EPA 5030B_MS
12/03/19
11/26/19
00:00
11/26/19
11:57
Client ID: 6301-MW2
Lab ID: CC18642-02
Sampled: 11/19/19 13:32
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/02/19
22:57
12/02/19
22:57
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:21
EPA 353.2
NO PREP
11/21/19 13:32
11/21/19
08:50
11/21/19
09:58
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
14:39
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
05/17/20
11/25/19
12:44
12/03/19
11:41
EPA 7470A
EPA 7470A
12/17/19
11/26/19
12:52
11/27/19
12:28
EPA 8260D
EPA 503013_MS
12/03/19
11/25/19
13:53
11/26/19
03:14
EPA 8260D
EPA 503013_MS
12/03/19
11/27/19
16:06
11/28/19
03:07
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
14:28
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
11:55
11/23/19
12:18
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
Client ID: 6301-MW3
(MS/MSD)
Lab ID: CC18642-03
Sampled: 11/19/19 11:56
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/02/19
17:39
12/02/19
17:39
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:10
EPA 353.2
NO PREP
11/21/19 11:56
11/21/19
08:50
11/21/19
09:49
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
13:06
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
05/17/20
11/25/19
12:52
12/03/19
12:54
EPA 7470A
EPA 7470A
12/17/19
11/26/19
12:52
11/27/19
12:14
EPA 8260D
EPA 503013_MS
12/03/19
11/26/19
15:54
11/27/19
12:02
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
14:44
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
13:28
11/23/19
13:54
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
Client ID: 6301-MW3
(MS/MSD)
Lab ID: CC18642-03RE1
Sampled: 11/19/19 11:56
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 8260D
EPA 503013_MS
12/03/19
11/26/19
00:00
11/26/19
12:31
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 3 Of 92

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW5
Lab ID: CC18642-04
Sampled: 11/19/19 10:02
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/02/19
23:15
12/02/19
23:15
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:22
EPA 353.2
NO PREP
11/21/19 10:02
11/21/19
08:50
11/21/19
09:59
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
14:40
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
05/17/20
11/25/19
12:44
12/03/19
11:44
EPA 6020B
EPA 3005A
O5/17/20
11/25/19
10:56
11/26/19
11:42
EPA 7470A
EPA 7470A
12/17/19
11/26/19
12:52
11/27/19
12:35
EPA 8260D
EPA 503013_MS
12/03/19
11/25/19
13:53
11/26/19
04:27
EPA 8260D
EPA 503013_MS
12/03/19
11/27/19
16:06
11/28/19
03:39
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
15:16
SM 2540C-2011
NO PREP
11/26/19
11/22/19
15:21
11/22/19
15:21
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
11:55
11/23/19
12:18
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
Client ID: 6301-MW14
Lab ID: CC18642-05
Sampled: 11/19/19 10:45
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/03/19
00:08
12/03/19
00:08
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:23
EPA 353.2
NO PREP
11/21/19 10:45
11/21/19
08:50
11/21/19
10:00
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
14:41
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
O5/17/20
11/25/19
12:44
12/03/19
11:46
EPA 6020E
EPA 3005A
05/17/20
11/25/19
10:56
11/26/19
11:46
EPA 7470A
EPA 7470A
12/17/19
11/26/19
12:52
11/27/19
12:37
EPA 8260D
EPA 503013_MS
12/03/19
11/25/19
13:53
11/26/19
05:03
EPA 8260D
EPA 5030B_MS
12/03/19
11/27/19
16:06
11/28/19
04:11
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
15:32
SM 2540C-2011
NO PREP
11/26/19
11/22/19
15:21
11/22/19
15:21
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
11:55
11/23/19
12:18
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
Client ID: 6301-MW14
Lab ID: CC18642-O5RE1
Sampled: 11/19/19 10:45
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(sl
Prep Date/Time(s)
Analysis
Date/Time(s)
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
16:36
Client ID: 6301-MW17S
Lab ID: CC18642-06
Sampled: 11/19/19 16:00
Received: 11/20/19
13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis
Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/03/19
00:26
12/03/19
00:26
EPA 310.2
NO PREP
12/03/19
11/22/19
13:48
11/22/19
17:23
EPA 353.2
NO PREP
11/21/19 16:00
11/21/19
08:50
11/21/19
10:00
EPA 353.2
NO PREP
12/17/19
12/05/19
09:20
12/05/19
14:42
EPA 353.2
NO PREP
08/14/22
12/06/19
15:08
12/06/19
15:08
EPA 6010D
EPA 3005A
05/17/20
11/25/19
12:44
12/03/19
11:49
EPA 6020E
EPA 3005A
05/17/20
11/25/19
10:56
11/26/19
11:50
EPA 7470A
EPA 7470A
12/17/19
11/26/19
12:52
11/27/19
12:40
EPA 8260D
EPA 503013_MS
12/03/19
11/27/19
16:06
11/28/19
04:44
RSK-175
Same
12/03/19
11/21/19
11:08
11/21/19
15:48
SM 2540C-2011
NO PREP
11/26/19
11/22/19
15:21
11/22/19
15:21
SM 450052 D-2011
NO PREP
11/26/19
11/23/19
11:55
11/23/19
12:18
SM 5310B-2011
Same
12/17/19
11/22/19
09:00
11/22/19
10:37
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 4 Of 92

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW17S
Lab ID: CC18642-06RE1
Sampled: 11/19/19 16:00
Received: 11/20/19 13:30
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/17/19
12/04/19 00:34
12/04/19 00:34
EPA 8260D
EPA 503013_MS
12/03/19
11/26/19 00:00
11/26/19 13:06
Client ID: 6301-MW4
Lab ID: CC19657-01
Sampled: 11/20/19 12:10
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/03/19 23:59
12/03/19 23:59
EPA 310.2
NO PREP
12/04/19
12/02/19 13:16
12/02/19 13:16
EPA 353.2
NO PREP
11/22/19 12:10
11/22/19 11:02
11/22/19 11:02
EPA 353.2
NO PREP
12/18/19
12/05/19 12:42
12/05/19 17:39
EPA 6010D
EPA 3005A
05/18/20
12/02/19 09:35
12/05/19 14:52
EPA 6020B
EPA 3005A
05/18/20
11/26/19 10:07
12/02/19 20:19
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:21
12/03/19 16:19
EPA 8260D
EPA 503013_MS
12/04/19
12/01/19 13:20
12/02/19 06:06
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:41
12/04/19 00:15
RSK-175
Same
12/04/19
12/03/19 13:51
12/03/19 16:34
SM 2540C-2011
NO PREP
11/27/19
11/27/19 17:42
11/27/19 17:42
SM 4500S2 D-2011
NO PREP
11/27/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/18/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW4
Lab ID: CC19657-01RE1
Sampled: 11/20/19 12:10
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:49
12/04/19 12:47
Client ID: 6301-MW6
Lab ID: CC19657-02
Sampled: 11/20/19 16:20
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/04/19 00:52
12/04/19 00:52
EPA 310.2
NO PREP
12/04/19
12/02/19 13:17
12/02/19 13:17
EPA 353.2
NO PREP
11/22/19 16:20
11/22/19 11:03
11/22/19 11:03
EPA 353.2
NO PREP
12/18/19
12/05/19 12:42
12/05/19 17:05
EPA 6010D
EPA 3005A
05/18/20
12/02/19 09:35
12/05/19 14:54
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:21
12/03/19 16:22
EPA 8260D
EPA 503013_MS
12/04/19
12/01/19 13:20
12/02/19 06:42
SM 4500S2 D-2011
NO PREP
11/27/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/18/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW6
Lab ID: CC19657-02RE1
Sampled: 11/20/19 16:20
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:49
12/04/19 13:18
RSK-175
Same
12/04/19
12/03/19 13:51
12/03/19 19:01
Client ID: 6301-MW6
Lab ID: CC19657-02RE2
Sampled: 11/20/19 16:20
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
RSK-175
Same
12/04/19
12/03/19 13:51
12/04/19 09:35
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in lull. I Page 5 Of 92

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW7
Lab ID: CC19657-03
Sampled: 11/20/19 11:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/04/19 02:56
12/04/19 02:56
EPA 310.2
NO PREP
12/04/19
12/02/19 13:18
12/02/19 13:18
EPA 353.2
NO PREP
11/22/19 11:30
11/22/19 11:04
11/22/19 11:04
EPA 353.2
NO PREP
12/18/19
12/05/19 12:42
12/05/19 17:41
EPA 6010D
EPA 3005A
05/18/20
12/02/19 09:35
12/05/19 14:57
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:21
12/03/19 16:24
EPA 8260D
EPA 503013_MS
12/04/19
12/01/19 13:20
12/02/19 07:19
RSK-175
Same
12/04/19
12/03/19 13:51
12/03/19 17:06
SM 4500S2 D-2011
NO PREP
11/27/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/18/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW7
Lab ID: CC19657-03RE1
Sampled: 11/20/19 11:30
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(sl
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:49
12/04/19 13:50
RSK-175
Same
12/04/19
12/03/19 13:51
12/03/19 19:17
Client ID: 6301-MW11SR
Lab ID: CC19657-04
Sampled: 11/20/19 13:36
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/18/19
12/04/19 03:49
12/04/19 03:49
EPA 310.2
NO PREP
12/04/19
12/02/19 13:18
12/02/19 13:18
EPA 353.2
NO PREP
11/22/19 13:36
11/22/19 11:06
11/22/19 11:06
EPA 353.2
NO PREP
12/18/19
12/05/19 12:42
12/05/19 17:42
EPA 6010D
EPA 3005A
05/18/20
12/03/19 10:18
12/05/19 15:33
EPA 6020E
EPA 3005A
05/18/20
11/26/19 10:07
12/02/19 20:23
EPA 7470A
EPA 7470A
12/18/19
12/02/19 12:21
12/03/19 16:26
EPA 8260D
EPA 503013_MS
12/04/19
12/01/19 13:20
12/02/19 07:55
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:41
12/04/19 01:51
RSK-175
Same
12/04/19
12/03/19 13:51
12/03/19 17:22
SM 254OC-2011
NO PREP
11/27/19
11/27/19 17:42
11/27/19 17:42
SM 4500S2 D-2011
NO PREP
11/27/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/18/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW11SR
Lab ID: CC19657-04RE1
Sampled: 11/20/19 13:36
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/04/19
12/03/19 13:49
12/04/19 14:21
Client ID: 6301-MW9
Lab ID: CC19664-01
Sampled: 11/21/19 09:53
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/04/19 04:06
12/04/19 04:06
EPA 310.2
NO PREP
12/05/19
12/02/19 13:19
12/02/19 13:19
EPA 353.2
NO PREP
11/23/19 09:53
11/22/19 11:07
11/22/19 11:07
EPA 353.2
NO PREP
12/19/19
12/05/19 12:42
12/05/19 17:44
EPA 6010D
EPA 3005A
05/19/20
12/03/19 10:18
12/05/19 15:36
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 16:29
EPA 8260D
EPA 503013_MS
12/05/19
12/02/19 00:00
12/02/19 12:12
RSK-175
Same
12/05/19
12/03/19 13:51
12/03/19 15:46
SM 4500S2 D-2011
NO PREP
11/28/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/19/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW9
Lab ID: CC19664-01RE1
Sampled: 11/21/19 09:53
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/13/19 21:55
12/13/19 21:55
EPA 8260D
EPA 503013_MS
12/05/19
12/05/19 14:08
12/05/19 20:09
RSK-175
Same
12/05/19
12/03/19 13:51
12/03/19 17:54
FINAL
This report
relates only to the sample as received by the laboratory, and may only be reproduced in full.
I Page 6 Of 92

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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW15R
Lab ID: CC19664-02
Sampled: 11/21/19 13:13
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 300.0
NO PREP
12/19/19
12/04/19 04:24
12/04/19 04:24
EPA 310.2
NO PREP
12/05/19
12/02/19 13:21
12/02/19 13:21
EPA 353.2
NO PREP
11/23/19 13:13
11/22/19 11:08
11/22/19 11:08
EPA 353.2
NO PREP
12/19/19
12/05/19 12:42
12/05/19 17:46
EPA 6010D
EPA 3005A
05/19/20
12/03/19 10:18
12/05/19 15:38
EPA 7470A
EPA 7470A
12/19/19
12/02/19 12:21
12/03/19 16:32
RSK-175
Same
12/05/19
12/03/19 13:51
12/03/19 16:18
SM 4500S2 D-2011
NO PREP
11/28/19
11/23/19 14:42
11/23/19 14:59
SM 531OB-2011
Same
12/19/19
11/26/19 12:00
11/26/19 13:36
Client ID: 6301-MW15R
Lab ID: CC19664-02RE1
Sampled: 11/21/19 13:13
Received: 11/22/19 07:00
Parameter
Preparation
Hold Date/Time(s)
Prep Date/Time(s)
Analysis Date/Time(s)
EPA 8260D
EPA 503013_MS
12/05/19
12/02/19 00:00
12/02/19 17:28
EPA 8260D
EPA 503013_MS
12/05/19
12/05/19 14:08
12/05/19 20:40
RSK-175
Same
12/05/19
12/03/19 13:51
12/03/19 18:45
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 7 Of 92

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW3
Lab ID:
CC18642-01
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dichlorobenzene
0.45
1
0.19
1.0
ug/L
EPA 8260D
Barium - Total
37.8
1.10
10.0
ug/L
EPA 6010D
Benzene
0.48
1
0.15
1.0
ug/L
EPA 8260D
Chloride
6900
2200
5000
ug/L
EPA 300.0
Chlorobenzene
3.7
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
0.72
1
0.15
1.0
ug/L
EPA 8260D
Methane
321
0.450
1.00
ug/L
RSK-175
Nitrate as N
510
25
100
ug/L
EPA 353.2
Nitrate/Nitrite as N
510
41
100
ug/L
EPA 353.2
Sulfate as SO4
11000
2900
5000
ug/L
EPA 300.0
Total Alkalinity as CaCO3
51000
14000
15000
ug/L
EPA 310.2
Total Organic Carbon
4300
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW3
Lab ID:
CC18642-01RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
2.3
0.80
2.0
ug/L
EPA 8260D
Client ID: 6301-MW2
Lab ID:
CC18642-02
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dichlorobenzene
1.2
0.19
1.0
ug/L
EPA 8260D
1,4-Dioxane
14
0.80
2.0
ug/L
EPA 8260D
Barium - Total
54.9
1.10
10.0
ug/L
EPA 6010D
Benzene
0.97
1
0.15
1.0
ug/L
EPA 8260D
Chloride
55000
2200
5000
ug/L
EPA 300.0
Chlorobenzene
2.6
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
0.84
1
0.15
1.0
ug/L
EPA 8260D
Methane
44.2
0.450
1.00
ug/L
RSK-175
Nitrate as N
880
25
100
ug/L
EPA 353.2
Nitrate/Nitrite as N
880
41
100
ug/L
EPA 353.2
Sulfate as SO4
7700
2900
5000
ug/L
EPA 300.0
Total Alkalinity as CaCO3
250000
D
28000
30000
ug/L
EPA 310.2
Total Organic Carbon
8800
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW3 (MS/MSD)
Lab ID:
CC18642-03
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
Barium - Total
38.5
1.10
10.0
ug/L
EPA 6010D
Chloride
5100
2200
5000
ug/L
EPA 300.0
Sulfate as SO4
9200
2900
5000
ug/L
EPA 300.0
Total Oraanic Carbon
1100
340
1000
ua/L
SM 531OB-2011
I Client ID: 6301-MW3 (MS/MSD) Lab ID: CC18642-03RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dioxane
1.1
1
0.80
2.0
ug/L
EPA 8260D
Client ID: 6301-MW5
Lab ID:
CC18642-04
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Barium - Total
14.5
1.10
10.0
ug/L
EPA 6010D
Manganese - Total
2.68
1
1.50
10.0
ug/L
EPA 6010D
Nitrate as N
420
25
100
ug/L
EPA 353.2
Nitrate/Nitrite as N
420
41
100
ug/L
EPA 353.2
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 8 Of 92

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW14
Lab ID:
CC18642-05
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,2-Dichlorobenzene
1.8
0.19
1.0
ug/L
EPA 8260D
1,4-Dichlorobenzene
5.6
0.19
1.0
ug/L
EPA 8260D
1,4-Dioxane
15
0.80
2.0
ug/L
EPA 8260D
Barium - Total
56.9
1.10
10.0
ug/L
EPA 6010D
Benzene
2.3
0.15
1.0
ug/L
EPA 8260D
Cadmium - Total
0.409
1
0.360
1.00
ug/L
EPA 6010D
Chloride
51000
2200
5000
ug/L
EPA 300.0
Chlorobenzene
5.1
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
3.9
0.15
1.0
ug/L
EPA 8260D
Ethylbenzene
0.58
1
0.13
1.0
ug/L
EPA 8260D
Iron - Total
152000
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
212
1.50
10.0
ug/L
EPA 6010D
Nitrate as N
67
1
25
100
ug/L
EPA 353.2
Nitrate/Nitrite as N
85
1
41
100
ug/L
EPA 353.2
Nitrite as N
18
1
17
100
ug/L
EPA 353.2
Sulfate as SO4
10000
2900
5000
ug/L
EPA 300.0
Sulfide
36
1
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
200000
D
28000
30000
ug/L
EPA 310.2
Total Dissolved Solids
350000
50000
50000
ug/L
SM 2540C-2011
Total Organic Carbon
12000
340
1000
ug/L
SM 531OB-2011
Vinyl chloride
2.5
0.32
1.0
ug/L
EPA 8260D
Zinc - Total
5.24
1
4.40
10.0
ug/L
EPA 6010D
Client ID: 6301-MW14
Lab ID:
CC18642-05RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Methane
1800
D
4.50
10.0
ug/L
RSK-175
Client ID: 6301-MW17S
Lab ID:
CC18642-06
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Barium - Total
68.3
1.10
10.0
ug/L
EPA 6010D
Chloride
24000
2200
5000
ug/L
EPA 300.0
cis-1,2-Dichloroethene
1.8
0.15
1.0
ug/L
EPA 8260D
Iron - Total
38400
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
117
1.50
10.0
ug/L
EPA 6010D
Methane
167
0.450
1.00
ug/L
RSK-175
Nitrate as N
300
25
100
ug/L
EPA 353.2
Nitrate/Nitrite as N
330
41
100
ug/L
EPA 353.2
Nitrite as N
35
1
17
100
ug/L
EPA 353.2
Total Alkalinity as CaCO3
64000
14000
15000
ug/L
EPA 310.2
Total Dissolved Solids
400000
50000
50000
ug/L
SM 2540C-2011
Total Organic Carbon
21000
340
1000
ua/L
SM 531OB-2011
Client ID: 6301-MW17S
Lab ID:
CC18642-06RE3
Anala
Results Flag MDL
POLL
Units Method Notes
1,4-Dioxane
1.6 1 0.80
2.0
ug/L EPA 8260D
Sulfate as SO4
140000 D 5800
10000
ug/L EPA 300.0
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 9 Of 92

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW4
Lab ID:
CC19657-01
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dioxane
2.0
0.80
2.0
ug/L
EPA 8260D
Barium - Total
53.9
1.10
10.0
ug/L
EPA 6010D
Chloride
18000
2200
5000
ug/L
EPA 300.0
Copper - Total
1.76
1
1.60
10.0
ug/L
EPA 6010D
Iron - Total
15500
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
131
1.50
10.0
ug/L
EPA 6010D
Methane
59.1
0.450
1.00
ug/L
RSK-175
Nitrate/Nitrite as N
1300
D
200
500
ug/L
EPA 353.2
Sulfate as SO4
26000
2900
5000
ug/L
EPA 300.0
Total Alkalinity as CaCO3
190000
14000
15000
ug/L
EPA 310.2
Total Dissolved Solids
290000
50000
50000
ug/L
SM 2540C-2011
Total Organic Carbon
27000
340
1000
ug/L
SM 531OB-2011
Vanadium - Total
1.92
1
1.40
10.0
ug/L
EPA 6010D
Zinc - Total
22.6
4.40
10.0
ug/L
EPA 6010D
Client ID: 6301-MW4
Lab ID:
CC19657-01RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,4-Dichlorobenzene
0.46
1
0.19
1.0
ug/L
EPA 8260D
cis-1.2-Dichloroethene
1.5
0.15
1.0
ua/L
EPA 8260D
I Client ID: 6301-MW6 Lab ID: CC19657-02
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
1.4
1
0.80
2.0
ug/L
EPA 8260D
Barium - Total
52.7
1.10
10.0
ug/L
EPA 6010D
Chloride
13000
2200
5000
ug/L
EPA 300.0
Nitrate/Nitrite as N
67
1
41
100
ug/L
EPA 353.2
Sulfate as SO4
13000
2900
5000
ug/L
EPA 300.0
Sulfide
97
1
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
260000
D
28000
30000
ug/L
EPA 310.2
Total Organic Carbon
13000
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW6
Lab ID:
CC19657-02RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dichlorobenzene
2.3
0.19
1.0
ug/L
EPA 8260D
Benzene
3.7
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
1.9
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
1.5
0.15
1.0
ug/L
EPA 8260D
Vinyl chloride
1.3
0.32
1.0
ug/L
EPA 8260D
Client ID: 6301-MW6
Lab ID:
CC19657-02RE2
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
Methane
1120
D
4.50
10.0
ug/L
RSK-175
Client ID: 6301-MW7
Lab ID:
CC19657-03
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
10
0.80
2.0
ug/L
EPA 8260D
Barium - Total
38.3
1.10
10.0
ug/L
EPA 6010D
Chloride
22000
2200
5000
ug/L
EPA 300.0
Nitrate/Nitrite as N
67
1
41
100
ug/L
EPA 353.2
Nitrite as N
28
1
17
100
ug/L
EPA 353.2
Sulfide
79
1
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
120000
14000
15000
ug/L
EPA 310.2
Total Organic Carbon
8500
340
1000
ug/L
SM 531OB-2011
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 10 Of 92

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW7
Lab ID:
CC19657-03RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,2-Dichlorobenzene
0.49
1
0.19
1.0
ug/L
EPA 8260D
1,4-Dichlorobenzene
3.0
0.19
1.0
ug/L
EPA 8260D
Acetone
12
1
10
20
ug/L
EPA 8260D
Benzene
1.6
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
4.1
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
2.0
0.15
1.0
ug/L
EPA 8260D
Methane
738
D
2.25
5.00
ug/L
RSK-175
Methylene chloride
0.64
1
0.23
1.0
ug/L
EPA 8260D
Vinyl chloride
1.3
0.32
1.0
ug/L
EPA 8260D
Client ID: 6301-MW11SR
Lab ID:
CC19657-04
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
4.8
0.80
2.0
ug/L
EPA 8260D
Barium - Total
71.2
1.10
10.0
ug/L
EPA 6010D
Chloride
25000
2200
5000
ug/L
EPA 300.0
Iron - Total
101000
22.0
50.0
ug/L
EPA 6010D
Manganese - Total
248
1.50
10.0
ug/L
EPA 6010D
Methane
244
0.450
1.00
ug/L
RSK-175
Nitrate/Nitrite as N
86
1
41
100
ug/L
EPA 353.2
Nitrite as N
38
1
17
100
ug/L
EPA 353.2
Sulfate as SO4
3300
1
2900
5000
ug/L
EPA 300.0
Sulfide
61
1
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
650000
D
70000
75000
ug/L
EPA 310.2
Total Dissolved Solids
590000
50000
50000
ug/L
SM 2540C-2011
Total Organic Carbon
22000
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW11SR
Lab ID:
CC19657-04RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dichlorobenzene
2.9
0.19
1.0
ug/L
EPA 8260D
Benzene
2.8
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
1.3
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
1.1
0.15
1.0
ug/L
EPA 8260D
Vinyl chloride
2.0
0.32
1.0
ug/L
EPA 8260D
Client ID: 6301-MW9
Lab ID:
CC19664-01
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,4-Dioxane
22
0.80
2.0
ug/L
EPA 8260D
QM-07
Arsenic - Total
36.5
7.60
10.0
ug/L
EPA 6010D
Barium - Total
117
1.10
10.0
ug/L
EPA 6010D
Nitrate/Nitrite as N
100
41
100
ug/L
EPA 353.2
Nitrite as N
35
1
17
100
ug/L
EPA 353.2
Sulfide
170
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
970000
D
140000
150000
ug/L
EPA 310.2
Total Organic Carbon
45000
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW9
Lab ID:
CC19664-01RE3
Anala
Results
Flag
MDL
POLL
Units
Method
Notes
1,2-Dichlorobenzene
0.41
1
0.19
1.0
ug/L
EPA 8260D
1,4-Dichlorobenzene
2.9
0.19
1.0
ug/L
EPA 8260D
Benzene
3.8
0.15
1.0
ug/L
EPA 8260D
Chloride
120000
D
4400
10000
ug/L
EPA 300.0
Chlorobenzene
11
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
0.43
1
0.15
1.0
ug/L
EPA 8260D
Methane
1500
D
4.50
10.0
ug/L
RSK-175
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 11 of 92

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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW15R
Lab ID:
CC19664-02
Anala
Results
Flag
MDL
POLL
Units
Method Notes
Barium - Total
19.8
1.10
10.0
ug/L
EPA 6010D
Nitrate/Nitrite as N
65
1
41
100
ug/L
EPA 353.2
Sulfate as SO4
9900
2900
5000
ug/L
EPA 300.0
Sulfide
370
10
100
ug/L
SM 450052 D-2011
Total Alkalinity as CaCO3
97000
14000
15000
ug/L
EPA 310.2
Total Organic Carbon
18000
340
1000
ug/L
SM 531OB-2011
Client ID: 6301-MW15R
Lab ID:
CC19664-02RE3
Anala
Results
Flag
MDL
POLL
Units
Method Notes
1,1-Dichloroethane
0.93
1
0.13
1.0
ug/L
EPA 8260D
1,4-Dichlorobenzene
5.8
0.19
1.0
ug/L
EPA 8260D
2-Butanone
5.7
1.3
5.0
ug/L
EPA 8260D
Acetone
190
10
20
ug/L
EPA 8260D
Benzene
5.7
0.15
1.0
ug/L
EPA 8260D
Chlorobenzene
0.91
1
0.17
1.0
ug/L
EPA 8260D
cis-1,2-Dichloroethene
0.76
1
0.15
1.0
ug/L
EPA 8260D
Methane
1080
D
4.50
10.0
ug/L
RSK-175
Toluene
0.43
1
0.14
1.0
ug/L
EPA 8260D
Vinyl chloride
0.74
1
0.32
1.0
ug/L
EPA 8260D
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 12 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW1 Lab Sample ID:CC18642-01 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:01 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte ICAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,1-Dichloroethane [75-34-3]1
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,1-Dichloroethene [75-35-4]1
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2,3-Trichloropropane [96-18-4]1
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2-Dibromoethane [106-93-4]1
0.66
U
ug/L
1
0.66
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2-Dichloroethane [107-06-2]1
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,2-Dichloropropane [78-87-5]1
0.10
U
ug/L
1
0.10
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
1,4-Dichlorobenzene [306-46-7]^
0.45
J
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91<27001
EPA 8260D
11/28/19
02:35
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91<27001
EPA 8260D
11/28/19
02:35
REF
Benzene [71-43-2]^
0.48
J
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Chlorobenzene [108-90-7]^
3.7
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
cis- 1,2-Dichloroethene [156-59-2]^
0.72
J
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
cis- 1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
91<27001
EPA 8260D
11/28/19
02:35
REF
Xylenes(Total)[1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
91<27001
EPA 8260D
11/28/19
02:35
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 13 Of 92

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW1 Lab Sample ID:CC18642-01 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:01 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
44
1
50.0
88 %
53-136
9K27001
EPA 8260D
11128119 02:35
REF
Dibromofluoromethane
53
1
50.0
107 %
67-129
9K27001
EPA 8260D
11128119 02:35
REF
Toluene-&
51
1
50.0
102 %
59-134
9K27001
EPA 8260D
11128119 02:35
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
91<21015
EPA 7470A
11/25/19 14:41
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
91(25033
EPA 6010D
12/03/19 11:39
]DH
Barium [7440-39-3]^
37.8
ug/L
1
1.10
10.0
9K25033
EPA 6010D
12/03/19 11:39
]DH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
91(25033
EPA 6010D
12/03/19 11:39
]DH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
91(25033
EPA 6010D
12/03/19 11:39
]DH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
91(25033
EPA 6010D
12/03/19 11:39
]DH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
91(25033
EPA 6010D
12/03/19 11:39
]DH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
91(25033
EPA 6010D
12/03/19 11:39
]DH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
6900
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/02/19 22:40
PDK
Nitrate as N [14797-55-8]^
530
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as IN
530
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 13:11
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
91(21007
EPA 353.2
11/21/19 09:57
AKF
Sulfate as SO4 [14808-79-8]^
11000
ug/L
1
2900
5000
9LO2037
EPA 300.0
12/02/19 22:40
PDK
Sulfide [18496-25-8]^
10
U
ug/L
1
10
100
91(23002 >M
4500S2 D-2011
11/23/19 12:18
30C
Total Alkalinity as CaCO3 [471-34-1]^
51000
ug/L
1
14000
15000
9K22033
EPA 310.2
11/22/19 17:21
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
2.3
ug/L
1
0.80
2.0
9K26030
EPA 8260D
11/26/19 11:57
KKW
Surrogates Results DF Snike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-& 5.2 1 5.00 104 % 75-125 9K26030 EPA 6260D 1112611911:57 KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 14 Of 92

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW1 Lab Sample ID:CC18642-01 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:01 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Classical Chemistry Parameters
A - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
4300
ug/L
1
340
1000
91<22006
SM 531OB-2011
11/22/19 10:37
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
91<21009
RSK-175
11/21/19 14:12
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
91<21009
RSK-175
11/21/19 14:12
LTS
Methane [74-82-8]
321
ug/L
1
0.450
1.00
91<21009
RSK-175
11/21/19 14:12
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 15 Of 92

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW2 Lab Sample ID:CC18642-02 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 13:32 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte ICAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,1-Dichloroethane [75-34-3]1
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,1-Dichloroethene [75-35-4]1
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2,3-Trichloropropane [96-18-4]1
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2-Dibromoethane [106-93-4]1
0.66
U
ug/L
1
0.66
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2-Dichloroethane [107-06-2]1
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,2-Dichloropropane [78-87-5]1
0.10
U
ug/L
1
0.10
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
1,4-Dichlorobenzene [306-46-7]^
1.2
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91<27001
EPA 8260D
11/28/19
03:07
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91<27001
EPA 8260D
11/28/19
03:07
REF
Benzene [71-43-2]^
0.97
J
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Chlorobenzene [108-90-7]^
2.6
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
cis- 1,2-Dichloroethene [156-59-2]^
0.84
J
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
cis- 1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
91<27001
EPA 8260D
11/28/19
03:07
REF
Xylenes(Total)[1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
91<27001
EPA 8260D
11/28/19
03:07
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 16 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW2 Lab Sample ID:CC18642-02 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 13:32 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
45
1
50.0
91 %
53-136
9K27001
EPA 8260D
11128119 03:07
REF
Dibromofluoromethane
56
1
50.0
112 %
67-129
9K27001
EPA 8260D
11128119 03:07
REF
Toluene-&
50
1
50.0
100 %
59-134
9K27001
EPA 8260D
11128119 03:07
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
91<26021
EPA 7470A
11/27/19 12:28
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
91(25033
EPA 6010D
12/03/19 11:41
]DH
Barium [7440-39-3]^
54.9
ug/L
1
1.10
10.0
9K25033
EPA 6010D
12/03/19 11:41
]DH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
91(25033
EPA 6010D
12/03/19 11:41
]DH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
91(25033
EPA 6010D
12/03/19 11:41
]DH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
91(25033
EPA 6010D
12/03/19 11:41
]DH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
91(25033
EPA 6010D
12/03/19 11:41
]DH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
91(25033
EPA 6010D
12/03/19 11:41
]DH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
55000
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/02/19 22:57
PDK
Nitrate as N [14797-55-8]^
880
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as IN
880
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 14:39
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
91(21007
EPA 353.2
11/21/19 09:58
AKF
Sulfate as SO4 [14808-79-8]^
7700
ug/L
1
2900
5000
9LO2037
EPA 300.0
12/02/19 22:57
PDK
Sulfide [18496-25-8]^
10
U
ug/L
1
10
100
91(23002 >M
4500S2 D-2011
11/23/19 12:18
30C
Total Alkalinity as CaCO3 [471-34-1]^
250000
D
ug/L
2
28000
30000
9K22033
EPA 310.2
11/22/19 17:21
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
14
ug/L
1
0.80
2.0
9K25041
EPA 8260D
11/26/19 03:14
KKW
Surrogates Results DF Snike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-& 5.7 1 5.00 114 % 75-125 9K25041 EPA 6260D 11126119 03:14 KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 17 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW2 Lab Sample ID:CC18642-02 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 13:32 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Classical Chemistry Parameters
A - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
8800
ug/L
1
340
1000
91<22006
SM 531OB-2011
11/22/19 10:37
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
91<21009
RSK-175
11/21/19 14:28
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
91<21009
RSK-175
11/21/19 14:28
LTS
Methane [74-82-8]
44.2
ug/L
1
0.450
1.00
91<21009
RSK-175
11/21/19 14:28
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 18 Of 92

00�
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ANALYTICAL RESULTS
Description: 6301-MW3 (MS/MSD) Lab Sample ID:CC18642-03 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 11:56 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
1,4-Dichlorobenzene [106-46-7]^
0.19
U
ug/L
1
0.19
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91<26036
EPA 8260D
11/27/19
12:02
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91<26036
EPA 8260D
11/27/19
12:02
REF
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
cis-1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Ethylbenzene[100-41-4]^
0.13
U
ug/L
1
0.13
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Styrene[100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF QL-02
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
91<26036
EPA 8260D
11/27/19
12:02
REF
Xylenes (Total) [1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
91<26036
EPA 8260D
11/27/19
12:02
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 19 of 92

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW3 (MS/MSD) Lab Sample ID:CC18642-03 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 11:56 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
49
1
50.0
97 %
53-136
9K26036
EPA 8260D
1112711912:02
REF
Dibromofluoromethane
49
1
50.0
98 %
67-129
9K26036
EPA 8260D
1112711912:02
REF
Toluene-&
52
1
50.0
103 %
59-134
9K26036
EPA 8260D
1112711912:02
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
91<26021
EPA 7470A
11/27/19 12:14
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
91(25034
EPA 6010D
12/03/19 12:54
]DH
Barium [7440-39-3]^
38.5
ug/L
1
1.10
10.0
9K25034
EPA 6010D
12/03/19 12:54
]DH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
91(25034
EPA 6010D
12/03/19 12:54
]DH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
91(25034
EPA 6010D
12/03/19 12:54
]DH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
91(25034
EPA 6010D
12/03/19 12:54
]DH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
91(25034
EPA 6010D
12/03/19 12:54
]DH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
91(25034
EPA 6010D
12/03/19 12:54
]DH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
5100
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/02/19 17:39
PDK
Nitrate as N [14797-55-8]^
25
U
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as N^
41
U
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 13:06
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
91(21007
EPA 353.2
11/21/19 09:49
AKF
Sulfate as SO4 [14808-79-8]^
9200
ug/L
1
2900
5000
9LO2037
EPA 300.0
12/02/19 17:39
PDK
Sulfide [18496-25-8]^
10
U
ug/L
1
10
100
91(23003 >M
4500S2 D-2011
11/23/19 13:54
30C
Total Alkalinity as CaCO3 [471-34-1]^
14000
U
ug/L
1
14000
15000
91(22033
EPA 310.2
11/22/19 17:10
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
1.1
J
ug/L
1
0.80
2.0
9K26030
EPA 8260D
11/26/19 12:31
KKW
Surrogates Results DF Snike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-& 5.5 1 5.00 110 % 75-125 9K26030 EPA 6260D 111261191221 KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 20 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW3 (MS/MSD) Lab Sample ID:CC18642-03 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 11:56 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Classical Chemistry Parameters
A - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
1100
ug/L
1
340
1000
91<22006
SM 531OB-2011
11/22/19 10:37
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
91<21009
RSK-175
11/21/19 14:44
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
91<21009
RSK-175
11/21/19 14:44
LTS
Methane [74-82-8]
0.450
u
ug/L
1
0.450
1.00
91<21009
RSK-175
11/21/19 14:44
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 21 of 92

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ANALYTICAL RESULTS
Description: 6301-MW5 Lab Sample ID:CC18642-04 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:02 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte ICAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,1-Dichloroethane [75-34-3]1
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,1-Dichloroethene [75-35-4]1
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2,3-Trichloropropane [96-18-4]1
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2-Dibromoethane [106-93-4]1
0.66
U
ug/L
1
0.66
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2-Dichloroethane [107-06-2]1
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,2-Dichloropropane [78-87-5]1
0.10
U
ug/L
1
0.10
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
1,4-Dichlorobenzene [106-46-7]1
0.19
U
ug/L
1
0.19
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF
2-Hexanone [591-78-6]1
0.88
U
ug/L
1
0.88
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91(27001
EPA 8260D
11/28/19
03:39
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91(27001
EPA 8260D
11/28/19
03:39
REF
Benzene [71-43-2]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Chlorobenzene [108-90-7]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
cis- 1,2-Dichloroethene [156-59-2]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
cis- 1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Naphthalene [91-20-3]^
0.11
U
ug/L
1
0.11
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91(27001
EPA 8260D
11/28/19
03:39
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91(27001
EPA 8260D
11/28/19
03:39
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 22 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW5 Lab Sample ID:CC18642-04 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:02 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Vinyl chloride [75-01-4]1 0.32 u ug/L 1 0.32 1.0 9K27001 EPA 8260D 11/28/19 03:39 REF
Xylenes(Total)[1330-20-7]^ 0.45 u ug/L 1 0.45 3.0 9K27001 EPA 8260D 11/28/19 03:39 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
44
1
50.0
88 %
53-136
9K27001
EPA 8260D
11128119 03:39
REF
Dlbromofluoromethane
53
1
50.0
106 %
67-129
9K27001
EPA 6260D
11128119 03:39
REF
Toluene-d8
50
1
50.0
100 %
59-134
9K27001
EPA 8260D
11128119 0339
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
PQL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
u
ug/L
1
0.150
0.200
9K26021
EPA 7470A
11/27/19 12:35
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
u
ug/L
2
0.740
2.00
9K25027
EPA 6020B
11/26/19 11:42
RLF
Arsenic[7440-38-2]^
7.60
u
ug/L
1
7.60
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Barium [7440-39-3]^
14.5
ug/L
1
1.10
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Beryllium [7440-41-7]^
0.160
u
ug/L
1
0.160
1.00
9K25033
EPA 6010D
12/03/19 11:44
JDH
Cadmium [7440-43-9]^
0.360
u
ug/L
1
0.360
1.00
9K25033
EPA 6010D
12/03/19 11:44
JDH
Chromium [7440-47-3]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Cobalt[7440-48-4]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Copper[7440-50-8]^
1.60
u
ug/L
1
1.60
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Iron [7439-89-6]^
22.0
u
ug/L
1
22.0
50.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Lead [7439-92-1]^
3.10
u
ug/L
1
3.10
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Manganese [7439-96-5]^
2.68
J
ug/L
1
1.50
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Nickel[7440-02-0]^
2.20
u
ug/L
1
2.20
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Selenium [7782-49-2]^
6.20
u
ug/L
1
6.20
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Silver[7440-22-4]^
1.90
u
ug/L
1
1.90
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Thallium [7440-28-0]^
0.220
u
ug/L
2
0.220
2.00
9K25027
EPA 6020B
11/26/19 11:42
RLF
Vanadium [7440-62-2]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Zinc[7440-66-6]^
4.40
u
ug/L
1
4.40
10.0
9K25033
EPA 6010D
12/03/19 11:44
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Chloride[16887-00-6]^
2200
u
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/02/19 23:15
PDK
Nitrate as N [14797-55-8]^
420
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as N^
420
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 14:40
AKF
Nitrite as N [14797-65-0]^
17
u
ug/L
1
17
100
9K21007
EPA 353.2
11/21/19 09:59
AKF
Sulfate as SO4 [14808-79-8]^
2900
u
ug/L
1
2900
5000
9LO2037
EPA 300.0
12/02/19 23:15
PDK
Sulfide [18496-25-8]^
10
u
ug/L
1
10
100
9K23002
iM 450052 D-2011
11/23/19 12:18
JOC
Total Alkalinity as CaCO3 [471-34-1]^
14000
u
ug/L
1
14000
15000
9K22033
EPA 310.2
11/22/19 17:22
AKF
Total Dissolved Solids^
50000
u
ug/L
1
50000
50000
9K22006
SM 2540C-2011
11/22/19 15:21
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 23 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW5 Lab Sample ID:CC18642-04 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:02 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte MAS Numberl Results Flao Units DF MDL P L Batch Method Analyzed By Notes
1,4-Dioxane [123-91-1]^ 0.80 U ug/L 1 0.80 2.0 91<25041 EPA 8260D 11/26/19 04:27 KKW
Surrogates Results
DF
Spike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-& 6.0
1
5.00
120 %
75-125
9K25041
EPA 8260D
11126119 04:27
KKW
Classical Chemistry Parameters
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl Results
Flaa
Units
DF
MDL POLL
Batch
Method
Analyzed
Ay Notes
Total Organic Carbon^ 340
u
ug/L
1
340 1000
9K22006
SM 531OB-2011
11/22/19 10:37
JSS
Dissolved Gases by GC
Analyte fCAS Numberl
Results
Flaa
Units
DF
MDL
POLL
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
9K21009
RSK-175
11/21/19 15:16
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
9K21009
RSK-175
11/21/19 15:16
LTS
Methane [74-82-8]
0.450
u
ug/L
1
0.450
1.00
9K21009
RSK-175
11/21/19 15:16
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 24 of 92

00�
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW14 Lab Sample ID:CC18642-05 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:45 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2-Dichlorobenzene [95-50-1]A
1.8
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
1,4-Dichlorobenzene [106-46-7]A
5.6
ug/L
1
0.19
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91<27001
EPA 8260D
11/28/19
04:11
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91<27001
EPA 8260D
11/28/19
04:11
REF
Benzene [71-43-2]A
2.3
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Chlorobenzene [308-90-7]A
5.1
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
cis-1,2-Dichloroethene [156-59-2]^
3.9
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Ethylbenzene [300-41-4]A
0.58
1
ug/L
1
0.13
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Naphthalene [91-20-3]^
0.11
U
ug/L
1
0.11
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Styrene[100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91<27001
EPA 8260D
11/28/19
04:11
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91<27001
EPA 8260D
11/28/19
04:11
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 25 of 92

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ANALYTICAL RESULTS
Description: 6301-MW14 Lab Sample ID:CC18642-05 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:45 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Vinyl chloride [75-01-4]^ 2.5 ug/L 1 0.32 1.0 9K27001 EPA 8260D 11/28/19 04:11 REF
Xylenes(Total)[1330-20-7]^ 0.45 u ug/L 1 0.45 3.0 9K27001 EPA 8260D 11/28/19 04:11 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
43
1
50.0
85 %
53-136
9K27001
EPA 8260D
11128119 04:11
REF
Dlbromofluoromethane
54
1
50.0
108 %
67-129
9K27001
EPA 6260D
11128119 04:11
REF
Toluene-d8
54
1
50.0
108 %
59-134
9K27001
EPA 8260D
11128119 04:11
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
PQL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
u
ug/L
1
0.150
0.200
9K26021
EPA 7470A
11/27/19 12:37
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
u
ug/L
2
0.740
2.00
9K25027
EPA 6020B
11/26/19 11:46
RLF
Arsenic[7440-38-2]^
7.60
u
ug/L
1
7.60
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Barium [7440-39-3]^
56.9
ug/L
1
1.10
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Beryllium [7440-41-7]^
0.160
u
ug/L
1
0.160
1.00
9K25033
EPA 6010D
12/03/19 11:46
JDH
Cadmium [7440-43-9]^
0.409
J
ug/L
1
0.360
1.00
9K25033
EPA 6010D
12/03/19 11:46
JDH
Chromium [7440-47-3]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Cobalt[7440-48-4]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Copper[7440-50-8]^
1.60
u
ug/L
1
1.60
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Iron [7439-89-6]^
152000
ug/L
1
22.0
50.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Lead [7439-92-1]^
3.10
u
ug/L
1
3.10
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Manganese [7439-96-5]^
212
ug/L
1
1.50
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Nickel[7440-02-0]^
2.20
u
ug/L
1
2.20
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Selenium [7782-49-2]^
6.20
u
ug/L
1
6.20
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Silver[7440-22-4]^
1.90
u
ug/L
1
1.90
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Thallium [7440-28-0]^
0.220
u
ug/L
2
0.220
2.00
9K25027
EPA 6020B
11/26/19 11:46
RLF
Vanadium [7440-62-2]^
1.40
u
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Zinc[7440-66-6]^
5.24
J
ug/L
1
4.40
10.0
9K25033
EPA 6010D
12/03/19 11:46
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Chloride [16887-00-6]^
51000
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/03/19 00:08
PDK
Nitrate as N [14797-55-8]^
67
J
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as N^
85
J
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 14:41
AKF
Nitrite as N [14797-65-0]^
18
J
ug/L
1
17
100
9K21007
EPA 353.2
11/21/19 10:00
AKF
Sulfate as SO4 [14808-79-8]^
10000
ug/L
1
2900
5000
9LO2037
EPA 300.0
12/03/19 00:08
PDK
Sulfide [18496-25-8]^
36
J
ug/L
1
10
100
9K23002
iM 4500S2 D-2011
11/23/19 12:18
JOC
Total Alkalinity as CaCO3 [471-34-1]^
200000
D
ug/L
2
28000
30000
9K22033
EPA 310.2
11/22/19 17:23
AKF
Total Dissolved Solids^
350000
ug/L
1
50000
50000
9K22006
SM 2540C-2011
11/22/19 15:21
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 26 Of 92

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW14 Lab Sample ID:CC18642-05 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 10:45 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1,4-Dioxane [123-91-1]^ 1s ug/L 1 0.80 2.0 91<25041 EPA 8260D 11/26/19 05:03 KKW
Surrogates Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-& 5.2
1 5.00
104 %
75-125
9K25041
EPA 8260D
11126119 05:03
KKW
Classical Chemistry Parameters
^ - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl Results
Flag Units
DF
MDL POLL
Batch
Method
Analyzed
Ay Notes
Total Organic Carbon^ 12000
ug/L
1
340 1000
91<22006
SM 531OB-2011
11/22/19 10:37
JSS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
9K21009
RSK-175
11/21/19 15:32
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
9K21009
RSK-175
11/21/19 15:32
LTS
Methane [74-82-8]
1800
D
ug/L
10
4.50
10.0
91<21009
RSK-175
11/21/19 16:36
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 27 Of 92

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW17S Lab Sample ID:CC18642-06 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:00 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte ICAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,1-Dichloroethane [75-34-3]1
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,1-Dichloroethene [75-35-4]1
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2,3-Trichloropropane [96-18-4]1
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2-Dibromoethane [106-93-4]1
0.66
U
ug/L
1
0.66
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2-Dichloroethane [107-06-2]1
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,2-Dichloropropane [78-87-5]1
0.10
U
ug/L
1
0.10
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
1,4-Dichlorobenzene [106-46-7]1
0.19
U
ug/L
1
0.19
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF
2-Hexanone [591-78-6]1
0.88
U
ug/L
1
0.88
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
91(27001
EPA 8260D
11/28/19
04:44
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
91(27001
EPA 8260D
11/28/19
04:44
REF
Benzene [71-43-2]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF QV-01
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Chlorobenzene [108-90-7]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
cis- 1,2-Dichloroethene [156-59-2]^
1.8
ug/L
1
0.15
1.0
91<27001
EPA 8260D
11/28/19
04:44
REF
cis- 1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF QV-01
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
91(27001
EPA 8260D
11/28/19
04:44
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
91(27001
EPA 8260D
11/28/19
04:44
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 28 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW17S Lab Sample ID:CC18642-06 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:00 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9K27001 EPA 8260D 11/28/19 04:44 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
43
1
50.0
86 %
53-136
9K27001
EPA 8260D
11128119 04:44
REF
Dlbromofluoromethane
55
1
50.0
110 %
67-129
9K27001
EPA 6260D
11128119 04:44
REF
Toluene-d8
52
1
50.0
104 %
59-134
9K27001
EPA 8260D
11128119 04:44
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9K26021
EPA 7470A
11/27/19 12:40
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9K25027
EPA 6020B
11/26/19 11:50
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Barium [7440-39-3]^
68.3
ug/L
1
1.10
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9K25033
EPA 6010D
12/03/19 11:49
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9K25033
EPA 6010D
12/03/19 11:49
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Copper[7440-50-8]^
1.60
U
ug/L
1
1.60
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Iron [7439-89-6]^
38400
ug/L
1
22.0
50.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Manganese [7439-96-5]^
117
ug/L
1
1.50
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9K25027
EPA 6020B
11/26/19 11:50
RLF
Vanadium [7440-62-2]^
1.40
U
ug/L
1
1.40
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Zinc[7440-66-6]^
4.40
U
ug/L
1
4.40
10.0
9K25033
EPA 6010D
12/03/19 11:49
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analvte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
Ay
Notes
Chloride [16887-00-6]^
24000
ug/L
1
2200
5000
9LO2037
EPA 300.0
12/03/19 00:26
PDK
Nitrate as N [14797-55-8]^
300
ug/L
1
25
100
9LO6037
EPA 353.2
12/06/19 15:08
MKS
Nitrate/Nitrite as N^
330
ug/L
1
41
100
9LO5016
EPA 353.2
12/05/19 14:42
AKF
Nitrite as N [14797-65-0]^
35
J
ug/L
1
17
100
9K21007
EPA 353.2
11/21/19 10:00
AKF
Sulfate as SO4 [14808-79-8]^
140000
D
ug/L
2
5800
10000
9LO3017
EPA 300.0
12/04/19 00:34
PDK
Sulfide [18496-25-8]^
10
U
ug/L
1
10
100
9K23002
iM 4500S2 D-2011
11/23/19 12:18
JOC
Total Alkalinity as CaCO3 [471-34-1]^
64000
ug/L
1
14000
15000
9K22033
EPA 310.2
11/22/19 17:23
AKF
Total Dissolved Solids^
400000
ug/L
1
50000
50000
9K22006
SM 2540C-2011
11/22/19 15:21
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 29 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW17S Lab Sample ID:CC18642-06 Received: 11/20/19 13:30
Matrix: Ground Water Sampled:11/19/19 16:00 Work Order: CC18642
Project: Moore County LF Sampled By: Nicolas Tejada
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1,4-Dioxane [123-91-1]^ 1.6 J ug/L 1 0.80 2.0 91<26030 EPA 8260D 11/26/19 13:06 KKW
Surrogates Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-& 5.2
1 5.00
104 %
75-125
9K26030
EPA 8260D
1112611913:06
KKW
Classical Chemistry Parameters
^ - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl Results
Flag Units
DF
MDL POLL
Batch
Method
Analyzed
Ay Notes
Total Organic Carbon^ 21000
ug/L
1
340 1000
91<22006
SM 531OB-2011
11/22/19 10:37
JSS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flag Units
DF
MDL
POLL
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u ug/L
1
1.30
2.00
9K21009
RSK-175
11/21/19 15:48
LTS
Ethene [74-85-1]
1.50
u ug/L
1
1.50
3.00
9K21009
RSK-175
11/21/19 15:48
LTS
Methane [74-82-8]
167
ug/L
1
0.450
1.00
91<21009
RSK-175
11/21/19 15:48
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 30 Of 92

0Nk"q09
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ANALYTICAL RESULTS
Description: 6301-MW4 Lab Sample ID:CC19657-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 12:10 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
1,4-Dichlorobenzene [106-46-7]A
0.46
J
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
12:47
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
12:47
REF
Benzene[71-43-2]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Chlorobenzene[108-90-7]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
cis-1,2-Dichloroethene [156-59-2]^
1.5
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
9LO3036
EPA 8260D
12/04/19
00:15
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO3039
EPA 8260D
12/04/19
12:47
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 31 Of 92

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW4 Lab Sample ID:CC19657-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 12:10 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Xylenes(Total)[1330-20-7]^ 0.45 U ug/L 1 0.45 3.0 9LO3039 EPA 8260D 12/04/19 12:47 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
51
1
50.0
102 %
53-136
9LO3039
EPA 8260D
12104119 12:47
REF
Dlbromofluoromethane
51
1
50.0
102 %
67-129
9LO3039
EPA 6260D
1210411912:47
REF
Toluene-d8
44
1
50.0
88 %
59-134
9LO3039
EPA 8260D
1210411912:47
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:19
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
U
ug/L
2
0.740
2.00
9K26013
EPA 6020B
12/02/19 20:19
RLF
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Barium [7440-39-3]^
53.9
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Beryllium [7440-41-7]^
0.160
U
ug/L
1
0.160
1.00
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Cobalt[7440-48-4]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Copper[7440-50-8]^
1.76
J
ug/L
1
1.60
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Iron [7439-89-6]^
15500
ug/L
1
22.0
50.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Manganese [7439-96-5]^
131
ug/L
1
1.50
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Nickel[7440-02-0]^
2.20
U
ug/L
1
2.20
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Thallium [7440-28-0]^
0.220
U
ug/L
2
0.220
2.00
9K26013
EPA 6020B
12/02/19 20:19
RLF
Vanadium [7440-62-2]^
1.92
J
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Zinc [7440-66-6]^
22.6
ug/L
1
4.40
10.0
9LO2012
EPA 6010D
12/05/19 14:52
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
18000
ug/L
1
2200
5000
9LO3017
EPA 300.0
12/03/19 23:59
PDK
Nitrate/Nitrite as N^
1300
D
ug/L
5
200
500
9LO5042
EPA 353.2
12/05/19 17:39
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
9K22014
EPA 353.2
11/22/19 11:02
AKF
Sulfate as SO4 [14808-79-8]^
26000
ug/L
1
2900
5000
9LO3017
EPA 300.0
12/03/19 23:59
PDK
Sulfide [18496-25-8]^
10
U
ug/L
1
10
100
9K23005
iM 4500S2 D-2011
11/23/19 14:59
JOC
Total Alkalinity as CaCO3 [471-34-1]^
190000
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:16
AKF
Total Dissolved Solids^
290000
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 32 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW4 Lab Sample ID:CC19657-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 12:10 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1,4-Dioxane [123-91-1]^ 2.0 ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 06:06 M3H
Surrogates Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-& 5.3
1 5.00
105 %
75-125
9L01004
EPA 8260D
12102119 06:06
MJH
Classical Chemistry Parameters
^ - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl Results
Flag Units
DF
MDL POLL
Batch
Method
Analyzed
Ay Notes
Total Organic Carbon^ 27000
ug/L
1
340 1000
91<26002
SM 531OB-2011
11/26/19 13:36
iss
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flag Units
DF
MDL
POLL
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 16:34
LTS
Ethene [74-85-1]
1.50
u ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 16:34
LTS
Methane [74-82-8]
59.1
ug/L
1
0.450
1.00
9LO3012
RSK-175
12/03/19 16:34
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 33 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW6 Lab Sample ID:CC19657-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 16:20 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
1,4-Dichlorobenzene [106-46-7]A
2.3
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
13:18
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
13:18
REF
Benzene [71-43-2]A
3.7
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Chlorobenzene [108-90-7]A
1.9
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
cis-1,2-Dichloroethene [156-59-2]^
1.5
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Vinyl chloride [75-01-4]A
1.3
ug/L
1
0.32
1.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
Xylenes(Total)[1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3039
EPA 8260D
12/04/19
13:18
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 34 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW6 Lab Sample ID:CC19657-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 16:20 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
50
1
50.0
99 %
53-136
9L03039
EPA 8260D
12104119 13:18
REF
Dibromofluoromethane
51
1
50.0
102 %
67-129
9L03039
EPA 8260D
1210411913:18
REF
Toluene-&
45
1
50.0
90 %
59-134
9L03039
EPA 8260D
1210411913:18
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:22
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Barium [7440-39-3]^
52.7
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:54
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
13000
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 00:52
PDK
Nitrate/Nitrite as IN
67
J
ug/L
1
41
100
9LO5042
EPA 353.2
12/05/19 17:05
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
91<22014
EPA 353.2
11/22/19 11:03
AKF
Sulfate as SO4 [14808-79-8]^
13000
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 00:52
PDK
Sulfide [18496-25-8]^
97
J
ug/L
1
10
100
91<23005 >M
450052 D-2011
11/23/19 14:59
JOC
Total Alkalinity as CaCO3 [471-34-1]^
260000
D
ug/L
2
28000
30000
9LO2007
EPA 310.2
12/02/19 13:17
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
1.4
J
ug/L
1
0.80
2.0
9LO1004
EPA 8260D
12/02/19 06:42
MJH
Surrogates Results DF Spike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-d8 5.0 1 5.00 99 % 75-125 9L01004 EPA 8260D 12102119 06:42 MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 35 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW6 Lab Sample ID:CC19657-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 16:20 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Classical Chemistry Parameters
A - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
13000
ug/L
1
340
1000
91<26002
SM 531OB-2011
11/26/19 13:36
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 19:01
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 19:01
LTS
Methane [74-82-8]
1120
D
ug/L
10
4.50
10.0
9LO3012
RSK-175
12/04/19 09:35
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 36 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW7 Lab Sample ID:CC19657-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2-Dichlorobenzene [95-50-1]A
0.49
J
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
1,4-Dichlorobenzene [106-46-7]A
3.0
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Acetone [67-64-1]A
12
J
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
13:50
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
13:50
REF
Benzene [71-43-2]A
1.6
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Chlorobenzene [108-90-7]A
4.1
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
cis-1,2-Dichloroethene [156-59-2]^
2.0
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Methylene chloride [75-09-2]A
0.64
J
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Vinyl chloride [75-01-4]A
1.3
ug/L
1
0.32
1.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
Xylenes (Total) [1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO3039
EPA 8260D
12/04/19
13:50
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 37 Of 92

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW7 Lab Sample ID:CC19657-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
49
1
50.0
98 %
53-136
9L03039
EPA 8260D
12104119 13:50
REF
Dibromofluoromethane
51
1
50.0
102 %
67-129
9L03039
EPA 8260D
1210411913:50
REF
Toluene-&
45
1
50.0
89 %
59-134
9L03039
EPA 8260D
1210411913:50
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:24
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Barium [7440-39-3]^
38.3
ug/L
1
1.10
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO2012
EPA 6010D
12/05/19 14:57
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
22000
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 02:56
PDK
Nitrate/Nitrite as IN
67
J
ug/L
1
41
100
9LO5042
EPA 353.2
12/05/19 17:41
AKF
Nitrite as N [14797-65-0]^
28
J
ug/L
1
17
100
91<22014
EPA 353.2
11/22/19 11:04
AKF
Sulfate as SO4 [14808-79-8]^
2900
U
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 02:56
PDK
Sulfide [18496-25-8]^
79
J
ug/L
1
10
100
91<23005 >M
450052 D-2011
11/23/19 14:59
JOC
Total Alkalinity as CaCO3 [471-34-1]^
120000
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:18
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
10
ug/L
1
0.80
2.0
9LO1004
EPA 8260D
12/02/19 07:19
MJH
Surrogates Results DF Spike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-d8 4.9 1 5.00 98 % 75-125 9L01004 EPA 8260D 12102119 07:19 MJH
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 38 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW7 Lab Sample ID:CC19657-03 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 11:30 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Classical Chemistry Parameters
A - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
8500
ug/L
1
340
1000
91<26002
SM 531OB-2011
11/26/19 13:36
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
U
ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 17:06
LTS
Ethene [74-85-1]
1.50
U
ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 17:06
LTS
Methane [74-82-8]
738
D
ug/L
5
2.25
5.00
9LO3012
RSK-175
12/03/19 19:17
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 39 Of 92

0Nk"q09
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW11SR Lab Sample ID:CC19657-04 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 13:36 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
U
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
1,4-Dichlorobenzene [106-46-7]A
2.9
ug/L
1
0.19
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO3039
EPA 8260D
12/04/19
14:21
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO3039
EPA 8260D
12/04/19
14:21
REF
Benzene [71-43-2]A
2.8
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Chlorobenzene [108-90-7]A
1.3
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
cis-1,2-Dichloroethene [156-59-2]^
1.1
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Ethylbenzene [100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Naphthalene [91-20-3]^
0.11
U
ug/L
1
0.11
1.0
9LO3036
EPA 8260D
12/04/19
01:51
REF
Styrene [100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Tetrahydrofuran [109-99-9]^
0.53
U
ug/L
1
0.53
1.0
9LO3036
EPA 8260D
12/04/19
01:51
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO3039
EPA 8260D
12/04/19
14:21
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 40 Of 92

(� �Eo
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW11SR Lab Sample ID:CC19657-04 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 13:36 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
Vinyl chloride [75-01-4]^ 2.0 ug/L 1 0.32 1.0 9LO3039 EPA 8260D 12/04/19 14:21 REF
Xylenes(Total)[1330-20-7]^ 0.45 u ug/L 1 0.45 3.0 9LO3039 EPA 8260D 12/04/19 14:21 REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy
Notes
4-Bromofluorobenzene
49
1
50.0
99 %
53-136
9LO3039
EPA 8260D
12104119 14:21
REF
Dlbromofluoromethane
51
1
50.0
102 %
67-129
9LO3039
EPA 6260D
12104119 14:21
REF
Toluene-d8
44
1
50.0
89 %
59-134
9LO3039
EPA 8260D
12104119 14:21
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
PQL
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
u
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:26
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Antimony [7440-36-0]^
0.740
u
ug/L
2
0.740
2.00
9K26013
EPA 6020B
12/02/19 20:23
RLF
Arsenic[7440-38-2]^
7.60
u
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Barium [7440-39-3]^
71.2
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Beryllium [7440-41-7]^
0.160
u
ug/L
1
0.160
1.00
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Cadmium [7440-43-9]^
0.360
u
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Chromium [7440-47-3]^
1.40
u
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Cobalt[7440-48-4]^
1.40
u
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Copper[7440-50-8]^
1.60
u
ug/L
1
1.60
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Iron [7439-89-6]^
101000
ug/L
1
22.0
50.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Lead [7439-92-1]^
3.10
u
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Manganese [7439-96-5]^
248
ug/L
1
1.50
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Nickel[7440-02-0]^
2.20
u
ug/L
1
2.20
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Selenium [7782-49-2]^
6.20
u
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Silver[7440-22-4]^
1.90
u
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Thallium [7440-28-0]^
0.220
u
ug/L
2
0.220
2.00
9K26013
EPA 6020B
12/02/19 20:23
RLF
Vanadium [7440-62-2]^
1.40
u
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Zinc[7440-66-6]^
4.40
u
ug/L
1
4.40
10.0
9LO3016
EPA 6010D
12/05/19 15:33
JDH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
POLL
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
25000
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 03:49
PDK
Nitrate/Nitrite as N^
86
J
ug/L
1
41
100
9LO5042
EPA 353.2
12/05/19 17:42
AKF
Nitrite as N [14797-65-0]^
38
J
ug/L
1
17
100
9K22014
EPA 353.2
11/22/19 11:06
AKF
Sulfate as SO4 [14808-79-8]^
3300
J
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 03:49
PDK
Sulfide [18496-25-8]^
61
J
ug/L
1
10
100
9K23005
iM 4500S2 D-2011
11/23/19 14:59
JOC
Total Alkalinity as CaCO3 [471-34-1]^
650000
D
ug/L
5
70000
75000
9LO2007
EPA 310.2
12/02/19 13:18
AKF
Total Dissolved Solids^
590000
ug/L
1
50000
50000
9K27004
SM 2540C-2011
11/27/19 17:42
JOC
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 41 of 92

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ANALYTICAL RESULTS
Description: 6301-MW11SR Lab Sample ID:CC19657-04 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/20/19 13:36 Work Order: CC19657
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl Results Flag Units DF MDL P L Batch Method Analyzed By Notes
1,4-Dioxane [123-91-1]^ 4.8 ug/L 1 0.80 2.0 9LO1004 EPA 8260D 12/02/19 07:55 M3H
Surrogates Results
DF Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
Toluene-& 4.7
1 5.00
94 %
75-125
9LO1004
EPA 8260D
12102119 07:55
MJH
Classical Chemistry Parameters
^ - ENCO Orlando certified analyte [NC 424]
Analyte rCAS Numberl Results
Flag Units
DF
MDL POLL
Batch
Method
Analyzed
Ay Notes
Total Organic Carbon^ 22000
ug/L
1
340 1000
91<26002
SM 531OB-2011
11/26/19 13:36
JSS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flag Units
DF
MDL
POLL
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 17:22
LTS
Ethene [74-85-1]
1.50
u ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 17:22
LTS
Methane [74-82-8]
244
ug/L
1
0.450
1.00
9LO3012
RSK-175
12/03/19 17:22
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 42 Of 92

0Nk"q09
www.encolabs.com
ANALYTICAL RESULTS
Description: 6301-MW9 Lab Sample ID:CC19664-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 09:53 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
U
ug/L
1
0.12
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
U
ug/L
1
0.28
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,1-Dichloroethane [75-34-3]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,1-Dichloroethene [75-35-4]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
U
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2-Dibromoethane [106-93-4]^
0.66
U
ug/L
1
0.66
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2-Dichlorobenzene [95-50-1]A
0.41
J
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2-Dichloroethane [107-06-2]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,2-Dichloropropane [78-87-5]^
0.10
U
ug/L
1
0.10
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
1,4-Dichlorobenzene [106-46-7]A
2.9
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
2-Butanone [78-93-3]^
1.3
U
ug/L
1
1.3
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
2-Hexanone [591-78-6]^
0.88
U
ug/L
1
0.88
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
U
ug/L
1
1.1
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Acetone [67-64-1]^
10
U
ug/L
1
10
20
9LO5039
EPA 8260D
12/05/19
20:09
REF
Acrylonitrile [107-13-1]^
3.5
U
ug/L
1
3.5
10
9LO5039
EPA 8260D
12/05/19
20:09
REF
Benzene [71-43-2]A
3.8
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Bromochloromethane [74-97-5]^
0.48
U
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Bromodichloromethane [75-27-4]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Bromoform [75-25-2]^
0.22
U
ug/L
1
0.22
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Bromomethane [74-83-9]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Carbon disulfide [75-15-0]^
1.5
U
ug/L
1
1.5
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Carbon tetrachloride [56-23-5]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Chlorobenzene [108-90-7]A
11
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Chloroethane [75-00-3]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Chloroform [67-66-3]^
0.18
U
ug/L
1
0.18
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Chloromethane [74-87-3]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
cis-1,2-Dichloroethene [156-59-2]^
0.43
J
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
U
ug/L
1
0.20
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Dibromochloromethane [124-48-1]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Dibromomethane [74-95-3]^
0.27
U
ug/L
1
0.27
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Ethylbenzene[100-41-4]^
0.13
U
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Iodomethane [74-88-4]^
1.7
U
ug/L
1
1.7
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Methylene chloride [75-09-2]^
0.23
U
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Styrene[100-42-5]^
0.11
U
ug/L
1
0.11
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Tetrachloroethene [127-18-4]^
0.17
U
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Toluene [108-88-3]^
0.14
U
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
trans-1,2-Dichloroethene [156-60-5]^
0.21
U
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
U
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
U
ug/L
1
0.70
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Trichloroethene [79-01-6]^
0.15
U
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Trichlorofluoromethane [75-69-4]^
0.24
U
ug/L
1
0.24
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Vinyl acetate [108-05-4]^
0.95
U
ug/L
1
0.95
5.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Vinyl chloride [75-01-4]^
0.32
U
ug/L
1
0.32
1.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
Xylenes (Total) [1330-20-7]^
0.45
U
ug/L
1
0.45
3.0
9LO5039
EPA 8260D
12/05/19
20:09
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 43 Of 92

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW9 Lab Sample ID:CC19664-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 09:53 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
49
1
50.0
99 %
53-136
9LO5039
EPA 8260D
12105119 20:09
REF
Dibromofluoromethane
49
1
50.0
99 %
67-129
9LO5039
EPA 8260D
12105119 20:09
REF
Toluene-&
45
1
50.0
90 %
59-134
9LO5039
EPA 8260D
12105119 20:09
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:29
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic [7440-38-2]^
36.5
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Barium [7440-39-3]^
117
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:36
]DH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride [16887-00-6]^
120000
D
ug/L
2
4400
10000
9LO6012
EPA 300.0
12/13/19 21:55
-31
Nitrate/Nitrite as IN
100
ug/L
1
41
100
9LO5042
EPA 353.2
12/05/19 17:44
AKF
Nitrite as N [14797-65-0]^
35
J
ug/L
1
17
100
91<22014
EPA 353.2
11/22/19 11:07
AKF
Sulfate as SO4 [14808-79-8]^
2900
U
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 04:06
PDK
Sulfide [18496-25-8]^
170
ug/L
1
10
100
91<23005 >M
4500S2 D-2011
11/23/19 14:59
30C
Total Alkalinity as CaCO3 [471-34-1]^
970000
D
ug/L
10
140000
150000
9LO2007
EPA 310.2
12/02/19 13:19
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
22
ug/L
1
0.80
2.0
9LO2040
EPA 8260D
12/02/19 12:12
KKW
QM-07
Surrogates Results DF Spike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-d8 4.9 1 5.00 98 % 75-125 9LO2040 EPA 6260D 1210211912:12 KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 44 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW9 Lab Sample ID:CC19664-01 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 09:53 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Classical Chemistry Parameters
A - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
45000
ug/L
1
340
1000
91<26002
SM 531OB-2011
11/26/19 13:36
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 15:46
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 15:46
LTS
Methane [74-82-8]
1500
D
ug/L
10
4.50
10.0
9LO3012
RSK-175
12/03/19 17:54
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 45 Of 92

0Nk"q09
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ANALYTICAL RESULTS
Description: 6301-MW15R Lab Sample ID:CC19664-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 13:13 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds
by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte rCAS Numberl
Results
Flag
Units
DF
MDL
I'Q
Batch
Method
Analyzed
By Notes
1,1,1,2-Tetrachloroethane [630-20-6]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,1,1-Trichloroethane [71-55-6]^
0.12
u
ug/L
1
0.12
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,1,2,2-Tetrachloroethane [79-34-5]^
0.28
u
ug/L
1
0.28
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,1,2-Trichloroethane [79-00-5]^
0.14
u
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,1-Dichloroethane [75-34-3]A
0.93
J
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,1-Dichloroethene [75-35-4]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2,3-Trichloropropane [96-18-4]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2-Dibromo-3-chloropropane [96-12-8]^
0.48
u
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2-Dibromoethane [106-93-4]^
0.66
u
ug/L
1
0.66
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2-Dichlorobenzene [95-50-1]^
0.19
u
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2-Dichloroethane [107-06-2]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,2-Dichloropropane [78-87-5]^
0.10
u
ug/L
1
0.10
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
1,4-Dichlorobenzene [106-46-7]A
5.8
ug/L
1
0.19
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
2-Butanone [78-93-3]A
5.7
ug/L
1
1.3
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
2-Hexanone [591-78-6]^
0.88
u
ug/L
1
0.88
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
4-Methyl-2-pentanone [108-10-1]^
1.1
u
ug/L
1
1.1
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Acetone [67-64-1]A
190
ug/L
1
10
20
9LO5039
EPA 8260D
12/05/19
20:40
REF
Acrylonitrile [107-13-1]^
3.5
u
ug/L
1
3.5
10
9LO5039
EPA 8260D
12/05/19
20:40
REF
Benzene [71-43-2]A
5.7
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Bromochloromethane [74-97-5]^
0.48
u
ug/L
1
0.48
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Bromodichloromethane [75-27-4]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Bromoform [75-25-2]^
0.22
u
ug/L
1
0.22
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Bromomethane [74-83-9]^
0.14
u
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Carbon disulfide [75-15-0]^
1.5
u
ug/L
1
1.5
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Carbon tetrachloride [56-23-5]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Chlorobenzene [108-90-7]A
0.91
J
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Chloroethane [75-00-3]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Chloroform [67-66-3]^
0.18
u
ug/L
1
0.18
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Chloromethane [74-87-3]^
0.13
u
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
cis-1,2-Dichloroethene [156-59-2]^
0.76
J
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
cis-1,3-Dichloropropene [10061-01-5]^
0.20
u
ug/L
1
0.20
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Dibromochloromethane [124-48-1]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Dibromomethane [74-95-3]^
0.27
u
ug/L
1
0.27
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Ethylbenzene[100-41-4]^
0.13
u
ug/L
1
0.13
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Iodomethane [74-88-4]^
1.7
u
ug/L
1
1.7
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Methylene chloride [75-09-2]^
0.23
u
ug/L
1
0.23
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Styrene[100-42-5]^
0.11
u
ug/L
1
0.11
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Tetrachloroethene [127-18-4]^
0.17
u
ug/L
1
0.17
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Toluene [108-88-3]A
0.43
J
ug/L
1
0.14
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
trans- l,2-Dichloroethene [156-60-5]^
0.21
u
ug/L
1
0.21
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
trans-1,3-Dichloropropene [10061-02-6]^
0.15
u
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
trans-1,4-Dichloro-2-butene [110-57-6]^
0.70
u
ug/L
1
0.70
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Trichloroethene [79-01-6]^
0.15
u
ug/L
1
0.15
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Trichlorofluoromethane [75-69-4]^
0.24
u
ug/L
1
0.24
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Vinyl acetate [108-05-4]^
0.95
u
ug/L
1
0.95
5.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Vinyl chloride [75-01-4]A
0.74
J
ug/L
1
0.32
1.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
Xylenes (Total) [1330-20-7]^
0.45
u
ug/L
1
0.45
3.0
9LO5039
EPA 8260D
12/05/19
20:40
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 46 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW15R Lab Sample ID:CC19664-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 13:13 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
Notes
4-Bromofluorobenzene
50
1
50.0
100 %
53-136
9LO5039
EPA 8260D
12105119 20:40
REF
Dibromofluoromethane
51
1
50.0
101 %
67-129
9LO5039
EPA 8260D
12105119 20:40
REF
Toluene-&
45
1
50.0
89 %
59-134
9LO5039
EPA 8260D
12105119 20:40
REF
Metals by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Mercury [7439-97-6]^
0.150
U
ug/L
1
0.150
0.200
9LO2030
EPA 7470A
12/03/19 16:32
KAH
Metals (total recoverable) by EPA 6000/7000 Series Methods
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Arsenic[7440-38-2]^
7.60
U
ug/L
1
7.60
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Barium [7440-39-3]^
19.8
ug/L
1
1.10
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Cadmium [7440-43-9]^
0.360
U
ug/L
1
0.360
1.00
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Chromium [7440-47-3]^
1.40
U
ug/L
1
1.40
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Lead [7439-92-1]^
3.10
U
ug/L
1
3.10
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Selenium [7782-49-2]^
6.20
U
ug/L
1
6.20
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Silver[7440-22-4]^
1.90
U
ug/L
1
1.90
10.0
9LO3016
EPA 6010D
12/05/19 15:38
]DH
Classical Chemistry Parameters
^ - ENCO Cary certified analyte [NC 591]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
Chloride[16887-00-6]^
2200
U
ug/L
1
2200
5000
9LO3027
EPA 300.0
12/04/19 04:24
PDK
Nitrate/Nitrite as IN
65
J
ug/L
1
41
100
9LO5042
EPA 353.2
12/05/19 17:46
AKF
Nitrite as N [14797-65-0]^
17
U
ug/L
1
17
100
91<22014
EPA 353.2
11/22/19 11:08
AKF
Sulfate as SO4 [14808-79-8]^
9900
ug/L
1
2900
5000
9LO3027
EPA 300.0
12/04/19 04:24
PDK
Sulfide [18496-25-8]^
370
ug/L
1
10
100
91<23005 >M
4500S2 D-2011
11/23/19 14:59
30C
Total Alkalinity as CaCO3 [471-34-1]^
97000
ug/L
1
14000
15000
9LO2007
EPA 310.2
12/02/19 13:21
AKF
Volatile Organic Compounds by GCMS SIM Isotope Dilution
^ - ENCO Orlando certified analyte [NC 424]
Analyte fCAS Numberl
Results
Flag
Units
DF
MDL
P L
Batch
Method
Analyzed
By
Notes
1,4-Dioxane [123-91-1]^
0.80
U
ug/L
1
0.80
2.0
9LO2040
EPA 8260D
12/02/19 17:28
KKW
Surrogates Results DF Spike Lv/ % Rec % Rec Limits Batch Method Ana/vzed ffy Notes
Toluene-d8 4.8 1 5.00 95 % 75-125 9LO2040 EPA 6260D 12102119 17:28 KKW
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 47 Of 92

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ANALYTICAL RESULTS
Description: 6301-MW15R Lab Sample ID:CC19664-02 Received: 11/22/19 07:00
Matrix: Ground Water Sampled:11/21/19 13:13 Work Order: CC19664
Project: Moore County LF Sampled By: Erik Vasko
Classical Chemistry Parameters
A - ENCO Orlando Certified analyte [NC 424]
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Total Organic CarbonA
18000
ug/L
1
340
1000
91<26002
SM 531OB-2011
11/26/19 13:36
]SS
Dissolved Gases by GC
Analyte rCAS Numberl
Results
Flao
Units
DF
MDL
P L
Batch
Method
Analyzed
By Notes
Ethane [74-84-0]
1.30
u
ug/L
1
1.30
2.00
9LO3012
RSK-175
12/03/19 16:18
LTS
Ethene [74-85-1]
1.50
u
ug/L
1
1.50
3.00
9LO3012
RSK-175
12/03/19 16:18
LTS
Methane [74-82-8]
1080
D
ug/L
10
4.50
10.0
9LO3012
RSK-175
12/03/19 18:45
LTS
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 48 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9K26036 - EPA 50308 MS
Blank (9K26036-BLKI) Prepared: 11/26/2019 15:54 Analyzed: 11/27/2019 11:30
Analvte
Result
Flaa
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene
Dibromofluoromethane
FINAL
50 u9/L 50.0 100 53-136
49 u9/L 50.0 99 67-129
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 49 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9K26036 - EPA 5030E MS - Continued
Blank (9K26036-BLKI) Continued Prepared: 11/26/2019 15:54 Analyzed: 11/27/2019 11:30
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Toluene-d8 53 u91L 50.0 105 59-134
LCS (9K26036-BSI) Prepared: 11/26/2019 15:54 Analyzed: 11/27/2019 09:21
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
1,1-Dichloroethene
16
1.0
ug/L
20.0
81
75-133
Benzene
20
1.0
ug/L
20.0
100
80-134
Chlorobenzene
18
1.0
ug/L
20.0
90
80-120
Toluene
18
1.0
ug/L
20.0
91
71-120
Trichloroethene
24
1.0
ug/L
20.0
121
74-120
QL-02
Matrix Spike (9K26036-MS1)
Prepared: 11/26/2019 15:54 Analyzed: 11/27/2019 09:53
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
0.21 U
90
75-133
Benzene
19
1.0
ug/L
20.0
0.15 U
96
80-134
Chlorobenzene
16
1.0
ug/L
20.0
0.17 U
81
80-120
Toluene
16
1.0
ug/L
20.0
0.14 U
80
71-120
Trichloroethene
18
1.0
ug/L
20.0
0.15 U
91
74-120
Matrix Spike Dup (9K26036-MSD1)
Prepared: 11/26/2019 15:54 Analyzed: 11/27/2019 10:25
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
1,1-Dichloroethene
19
1.0
ug/L
20.0
0.21 U
95
75-133
5
20
Benzene
19
1.0
ug/L
20.0
0.15 U
96
80-134
0.05
17
Chlorobenzene
17
1.0
ug/L
20.0
0.17 U
83
80-120
2
16
Toluene
17
1.0
ug/L
20.0
0.14 U
83
71-120
4
17
Trichloroethene
18
1.0
ug/L
20.0
0.15 U
92
74-120
0.05
22
Batch 9K27001 - EPA 5030E MS
Blank (9K27001-BLK1)
Prepared: 11/27/2019 16:06 Analyzed: 11/28/2019 00:58
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units Level Result %REC Limits RPD Limit Notes
1,1,1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 50 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9K27001 - EPA 5030E MS - Continued
Blank (9K27001-BLKI) Continued Prepared: 11/27/2019 16:06 Analyzed: 11/28/2019 00:58
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Naphthalene
0.11
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Tetrahydrofuran
0.53
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
4-Bromofluorobenzene
46
ug/L
50.0
97
53-136
Dibromofluoromethane
51
u9/L
50.0
101
67-129
Toluene-d8
53
u91L
50.0
106
59-134
LCS (9K27001-BS1)
Prepared: 11/27/2019 16:06 Analyzed: 11/27/2019 22:49
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
20
1.0
ug/L
20.0
99
75-133
Benzene
20
1.0
ug/L
20.0
101
80-134
Chlorobenzene
18
1.0
ug/L
20.0
90
80-120
Toluene
18
1.0
ug/L
20.0
92
71-120
Trichloroethene
22
1.0
ug/L
20.0
109
74-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 51 of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9K27001 - EPA 5030E MS - Continued
Matrix Spike (9K27001-MS3)
Prepared: 11/27/2019 16:06 Analyzed: 11/27/2019 23:21
Source: CC19756-07
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
19
1.0
ug/L
20.0
0.21 U
97
75-133
Benzene
19
1.0
ug/L
20.0
0.15 U
96
80-134
Chlorobenzene
17
1.0
ug/L
20.0
0.17 U
86
80-120
Toluene
18
1.0
ug/L
20.0
0.14 U
88
71-120
Trichloroethene
21
1.0
ug/L
20.0
0.15 U
106
74-120
Matrix Spike Dup (9K27001-MSD1)
Prepared: 11/27/2019 16:06 Analyzed: 11/27/2019 23:53
Source: CC19756-07
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
21
1.0
ug/L
20.0
0.21 U
106
75-133 8
20
Benzene
20
1.0
ug/L
20.0
0.15 U
98
80-134 2
17
Chlorobenzene
18
1.0
ug/L
20.0
0.17 U
92
80-120 6
16
Toluene
18
1.0
ug/L
20.0
0.14 U
91
71-120 4
17
Trichloroethene
23
1.0
ug/L
20.0
0.15 U
115
74-120 8
22
Batch A03036 -EPA 50305 MS
Blank (91-03036-BLK3)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
Analvte
Result
Flaq
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 52 Of 92

QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03036 - EPA 50306 MS - Continued
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Blank (9L03036-BLK3) Continued Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 18:52
Analvte
Result
Flaq
POL
Units
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Naphthalene
0.11
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Tetrahydrofuran
0.53
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene 47
u9/L
50.0 93 53-136
Dibromofluoromethane 54
u9/L
50.0 107 67-129
Toluene-d8 53
u9/L
50.0 106 59-134
LCS (91-03036-BS1)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 16:43
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
23
1.0
ug/L
20.0
116
75-133
Benzene
23
1.0
ug/L
20.0
116
80-134
Chlorobenzene
19
1.0
ug/L
20.0
94
80-120
Toluene
19
1.0
ug/L
20.0
94
71-120
Trichloroethene
23
1.0
ug/L
20.0
117
74-120
Matrix Spike (91-03036-MS1)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:15
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result Flaa
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,1-Dichloroethene
24
1.0
ug/L
20.0
0.21 U
122
75-133
Benzene
25
1.0
ug/L
20.0
0.15 U
125
80-134
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
93
80-120
Toluene
19
1.0
ug/L
20.0
0.14 U
97
71-120
Trichloroethene
21
1.0
ug/L
20.0
0.15 U
106
74-120
Matrix Spike Dup (91-03036-MS131)
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:47
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
25
1.0
ug/L
20.0
0.21 U
127
75-133
4
20
Benzene
24
1.0
ug/L
20.0
0.15 U
120
80-134
4
17
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
93
80-120
0.2
16
FINAL
This report relates only to
the sample as received by the
laboratory, and
may only be
reproduced in
full.
Page 53 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03036 - EPA 50308 MS - Continued
Matrix Spike Dup (9L03036-MSD3) Continued
Prepared: 12/03/2019 13:41 Analyzed: 12/03/2019 17:47
Source: CC18494-01
Spike Source %REC
RPD
Analvte Result Flaq
POL Units
Level Result %REC Limits RPD
Limit Notes
Toluene 20
1.0 ug/L
20.0 0.14 U 98 71-120 1
17
Trichloroethene 22
1.0 ug/L
20.0 0.15 U 112 74-120 5
22
Batch 9103038 - EPA 5030E MS
Blank (9L03038-BLK1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 08:20
Analvte
Result
Flaq
POL
Units
1, 1, 1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 54 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03038 - EPA 50308 MS - Continued
Blank (9L03038-BLK3) Continued Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 08:20
Analvte
Result
Flaq
POL
Units
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-8romofluorobenzene 43
u9/L
50.0 86 53-136
Dlbromofluoromethane 55
u9/L
50.0 111 67-129
Toluene-d8 54
u9/L
50.0 107 59-134
LCS (9L03038-BS3)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 06:11
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
23
1.0
ug/L
20.0
114
75-133
Benzene
22
1.0
ug/L
20.0
112
80-134
Chlorobenzene
18
1.0
ug/L
20.0
88
80-120
Toluene
19
1.0
ug/L
20.0
93
71-120
Trichloroethene
24
1.0
ug/L
20.0
119
74-120
Matrix Spike (9L03038-MS1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 06:43
Source: CC18500-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
27
1.0
ug/L
20.0
0.21 U
133
75-133
Benzene
23
1.0
ug/L
20.0
0.15 U
117
80-134
Chlorobenzene
18
1.0
ug/L
20.0
0.17 U
90
80-120
Toluene
19
1.0
ug/L
20.0
0.14 U
96
71-120
Trichloroethene
22
1.0
ug/L
20.0
0.15 U
110
74-120
Matrix Spike Dup (91-03038-MSD1)
Prepared: 12/03/2019 13:48 Analyzed: 12/04/2019 07:15
Source: CC38500-01
Spike
Source
%REC
RPD
Analvte
Result Flan
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene
26
1.0
ug/L
20.0
0.21 U
129
75-133
2
20
Benzene
24
1.0
ug/L
20.0
0.15 U
121
80-134
4
17
Chlorobenzene
19
1.0
ug/L
20.0
0.17 U
95
80-120
5
16
Toluene
20
1.0
ug/L
20.0
0.14 U
102
71-120
6
17
Trichloroethene
24
1.0
ug/L
20.0
0.15 U
119
74-120
8
22
Batch 9L03039 - EPA 5030E MS
Blank (9L03039-BLK3)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 08:37
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units Level Result %REC Limits RPD Limit Notes
1,1,1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 55 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L03039 - EPA 50308 MS - Continued
Blank (9111-03039-BLK3) Continued Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 08:37
Analvte
Result
Flaq
POL
Units
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene
50
u9/L
50.0 100 53-136
Dibromofluoromethane
50
u9/L
50.0 100 67-129
Toluene-d8
44
u9/L
50.0 87 59-134
LCS (91-03039-BS1)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 06:32
Spike Source %REC
RPD
Analvte
Result Flaq POL
Units
Level Result %REC Limits RPD
Limit Notes
1,1-Dichloroethene
18 1.0
ug/L
20.0 88 75-133
FINAL
This report relates only to the sample as received by the
laboratory, and may only be reproduced in full.
Page 56 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9LO3039 - EPA 50308 MS - Continued
LCS (9LO3039-BS3) Continued
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 06:32
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD Limit Notes
Benzene
21
1.0
ug/L
20.0
106
80-134
Chlorobenzene
21
1.0
ug/L
20.0
104
80-120
Toluene
21
1.0
ug/L
20.0
107
71-120
Trichloroethene
22
1.0
ug/L
20.0
112
74-120
Matrix Spike (911-03039-MS1)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 07:04
Source: CC19707-02
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0
0.21 U
90
75-133
Benzene
21
1.0
ug/L
20.0
0.15 U
107
80-134
Chlorobenzene
21
1.0
ug/L
20.0
0.17 U
105
80-120
Toluene
21
1.0
ug/L
20.0
0.14 U
106
71-120
Trichloroethene
20
1.0
ug/L
20.0
0.46
99
74-120
Matrix Spike Dup (9L03039-MSD1)
Prepared: 12/03/2019 13:49 Analyzed: 12/04/2019 07:35
Source: CC19707-02
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD Limit Notes
1,1-Dichloroethene
19
1.0
ug/L
20.0
0.21 U
93
75-133
4 20
Benzene
22
1.0
ug/L
20.0
0.15 U
109
80-134
2 17
Chlorobenzene
21
1.0
ug/L
20.0
0.17 U
104
80-120
1 16
Toluene
21
1.0
ug/L
20.0
0.14 U
107
71-120
1 17
Trichloroethene
20
1.0
ug/L
20.0
0.46
98
74-120
0.9 22
Batch 9L05039 - EPA 5030E MS
Blank (9LOS039-BLK1)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 17:33
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD Limit Notes
1,1,1,2-Tetrachloroethane
0.17
U
1.0
ug/L
1,1,1-Trichloroethane
0.12
U
1.0
ug/L
1,1,2,2-Tetrachloroethane
0.28
U
1.0
ug/L
1,1,2-Trichloroethane
0.14
U
1.0
ug/L
1,1-Dichloroethane
0.13
U
1.0
ug/L
1,1-Dichloroethene
0.21
U
1.0
ug/L
1,2,3-Trichloropropane
0.23
U
1.0
ug/L
1,2-Dibromo-3-chloropropane
0.48
U
1.0
ug/L
1,2-Dibromoethane
0.66
U
1.0
ug/L
1,2-Dichlorobenzene
0.19
U
1.0
ug/L
1,2-Dichloroethane
0.21
U
1.0
ug/L
1,2-Dichloropropane
0.10
U
1.0
ug/L
1,4-Dichlorobenzene
0.19
U
1.0
ug/L
2-Butanone
1.3
U
5.0
ug/L
2-Hexanone
0.88
U
5.0
ug/L
4-Methyl-2-pentanone
1.1
U
5.0
ug/L
Acetone
10
U
20
ug/L
Acrylonitrile
3.5
U
10
ug/L
Benzene
0.15
U
1.0
ug/L
Bromochloromethane
0.48
U
1.0
ug/L
Bromodichloromethane
0.17
U
1.0
ug/L
FINAL
This report relates only to the
sample as received by the
laboratory, and
may only be
reproduced in
full.
Page 57 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L05039 - EPA 50308 MS - Continued
Blank (9111-05039-BLK3) Continued Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 17:33
Analvte
Result
Flaq
POL
Units
Bromoform
0.22
U
1.0
ug/L
Bromomethane
0.14
U
1.0
ug/L
Carbon disulfide
1.5
U
5.0
ug/L
Carbon tetrachloride
0.17
U
1.0
ug/L
Chlorobenzene
0.17
U
1.0
ug/L
Chloroethane
0.23
U
1.0
ug/L
Chloroform
0.18
U
1.0
ug/L
Chloromethane
0.13
U
1.0
ug/L
cis- 1,2-Dichloroethene
0.15
U
1.0
ug/L
cis- 1,3-Dichloropropene
0.20
U
1.0
ug/L
Dibromochloromethane
0.17
U
1.0
ug/L
Dibromomethane
0.27
U
1.0
ug/L
Ethylbenzene
0.13
U
1.0
ug/L
Iodomethane
1.7
U
5.0
ug/L
Methylene chloride
0.23
U
1.0
ug/L
Styrene
0.11
U
1.0
ug/L
Tetrachloroethene
0.17
U
1.0
ug/L
Toluene
0.14
U
1.0
ug/L
trans-1,2-Dichloroethene
0.21
U
1.0
ug/L
trans-1,3-Dichloropropene
0.15
U
1.0
ug/L
trans-1,4-Dichloro-2-butene
0.70
U
1.0
ug/L
Trichloroethene
0.15
U
1.0
ug/L
Trichlorofluoromethane
0.24
U
1.0
ug/L
Vinyl acetate
0.95
U
5.0
ug/L
Vinyl chloride
0.32
U
1.0
ug/L
Xylenes (Total)
0.45
U
3.0
ug/L
Spike Source %REC RPD
Level Result %REC Limits RPD Limit Notes
4-Bromofluorobenzene 46
u9/L
50.0 96 53-136
Dibromofluoromethane 51
u9/L
50.0 101 67-129
Toluene-d8 45
u9/L
50.0 90 59-134
LCS (91-05039-BS1)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 15:28
Spike Source %REC RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD Limit Notes
1,1-Dichloroethene
18
1.0
ug/L
20.0 91 75-133
Benzene
22
1.0
ug/L
20.0 112 80-134
Chlorobenzene
21
1.0
ug/L
20.0 106 80-120
Toluene
22
1.0
ug/L
20.0 110 71-120
Trichloroethene
21
1.0
ug/L
20.0 103 74-120
Matrix Spike (91-05039-MS1)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 15:59
Source: CC20745-01
Spike
Source
%REC
Analvte
Result Flaa
POL
Units
Level
Result
%REC
Limits RPD
1,1-Dichloroethene
16
1.0
ug/L
20.0
0.21 U
81
75-133
Benzene
20
1.0
ug/L
20.0
0.15 U
101
80-134
Chlorobenzene
20
1.0
ug/L
20.0
0.17 U
100
80-120
Toluene
21
1.0
ug/L
20.0
0.14 U
105
71-120
Trichloroethene
19
1.0
ug/L
20.0
0.15 U
93
74-120
RPD
Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full.
Page 58 of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch 9L05039 - EPA 50308 MS - Continued
Matrix Spike Dup (9L05039-MSDI)
Prepared: 12/05/2019 14:08 Analyzed: 12/05/2019 16:31
Source: CC20745-01
Spike
Source
%REC
RPD
Analvte Result Flag
POL
Units
Level
Result
%REC
Limits
RPD
Limit Notes
1,1-Dichloroethene 18
1.0
ug/L
20.0
0.21 U
88
75-133
8
20
Benzene 22
1.0
ug/L
20.0
0.15 U
109
80-134
7
17
Chlorobenzene 21
1.0
ug/L
20.0
0.17 U
106
80-120
6
16
Toluene 22
1.0
ug/L
20.0
0.14 U
108
71-120
4
17
Trichloroethene 20
1.0
ug/L
20.0
0.15 U
99
74-120
6
22
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9K21015 - EPA 7470A
Blank (9K23015-BLK1) Prepared: 11/21/2019 10:14 Analyzed: 11/25/2019 13:24
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Mercury 0.150 U 0.200 ug/L
LCS (9K21015-BS3) Prepared: 11/21/2019 10:14 Analyzed: 11/25/2019 13:26
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
4.68
0.200
ug/L
5.00 94 80-120
Matrix Spike (9K21015-MS1)
Prepared: 11/21/2019 10:14 Analyzed: 11/25/2019 13:36
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flag
POLL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
4.85
0.200
ug/L
5.00 0.150 U 97 75-125
Matrix Spike Dup (9K23015-MSD1)
Prepared: 11/21/2019 10:14 Analyzed: 11/25/2019 13:39
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
4.91
0.200
ug/L
5.00 0.150 U 98 75-125 1
25
Post Spike (9K21015-PS1)
Prepared: 11/21/2019 10:14 Analyzed: 11/25/2019 13:41
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Mercury
3.59
0.200
ug/L
5.00 0.0340 71 75-125
QM-08
Batch 9K26021 - EPA 7470A
Blank (9K26021-BLK1) Prepared: 11/26/2019 12:52 Analyzed: 11/27/2019 12:10
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Mercury 0.150 U 0.200 ug/L
LCS (9K26021-BS1) Prepared: 11/26/2019 12:52 Analyzed: 11/27/2019 12:12
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Mercury 4.80 0.200 ug/L 5.00 96 80-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 59 Of 92

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QUALITY CONTROL DATA
Metals by EPA 6000/7000 Series Methods - Quality Control
Batch 9K26021 - EPA 7470A - Continued
Matrix Spike (9K26021-MS3)
Prepared: 11/26/2019 12:52 Analyzed: 11/27/2019 12:17
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result Flaq
Q
Units
Level Result %REC Limits RPD
Limit Notes
Mercury
4.98
0.200
ug/L
5.00 0.150 U 100 75-125
Matrix Spike Dup (9K26021-MSDI)
Prepared: 11/26/2019 12:52 Analyzed: 11/27/2019 12:19
Source: CCI8642-03
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Mercury
4.97
0.200
ug/L
5.00 0.150 U 99 75-125 0.2
25
Post Spike (9K26021-PS1)
Prepared: 11/26/2019 12:52 Analyzed: 11/27/2019 12:21
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Mercury
6.06
0.200
ug/L
5.00 0.0290 121 75-125
Batch 9L02030 - EPA 7470A
Blank (9L02030-BLK3) Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:20
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Mercury 0.150 U 0.200 ug/L
LCS (9L02030-BSI) Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:23
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
5.04
0.200
ug/L
5.00
101
80-120
Matrix Spike (9L02030-MS1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:28
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.62
0.200
ug/L
5.00
0.150 U
92
75-125
Matrix Spike Dup (9L02030-MSD1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:30
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.21
0.200
ug/L
5.00
0.150 U
84
75-125 9
25
Post Spike (9L02030-PS1)
Prepared: 12/02/2019 12:21 Analyzed: 12/03/2019 15:32
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Mercury
4.46
0.200
ug/L
5.00
0.0430
88
75-125
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K25027 - EPA 3005A
Blank (9K25027-BLKI) Prepared: 11/25/2019 10:56 Analyzed: 11/26/2019 10:42
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Antimony
Thallium
FINAL
0.370 U 1.00 ug/L
0.110 U 1.00 ug/L
This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 60 Of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K25027 - EPA 3005A - Continued
LCS (9K25027-BS3) Prepared: 11/25/2019 10:56 Analyzed: 11/26/2019 10:46
Spike Source %REC
RPD
Analvte
Result
Flag
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
21.4
1.00
ug/L
20.0 107 80-120
Thallium
21.1
1.00
ug/L
20.0 106 80-120
Matrix Spike (9K25027-MSI)
Prepared: 11/25/2019 10:56 Analyzed: 11/26/2019 10:50
Source: CC18996-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
44.4
2.00
ug/L
40.0 0.740 U 111 75-125
Thallium
41.8
2.00
ug/L
40.0 0.220 U 105 75-125
Matrix Spike Dup (9K25027-MSD3)
Prepared: 11/25/2019 10:56 Analyzed: 11/26/2019 10:54
Source: CC18996-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
44.0
2.00
ug/L
40.0 0.740 U 110 75-125 0.7
20
Thallium
41.6
2.00
ug/L
40.0 0.220 U 104 75-125 0.6
20
Post Spike (9K25027-PS3)
Prepared: 11/25/2019 10:56 Analyzed: 11/26/2019 10:59
Source: CC18996-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Antimony
22.0
1.00
ug/L
20.0 0.0322 110 75-125
Thallium
20.7
1.00
ug/L
20.0 0.0143 104 75-125
Batch 9K25033 - EPA 3005A
Blank (9K25033-BLKS) Prepared: 11/25/2019 12:44 Analyzed: 12/03/2019 10:49
Spike Source %REC RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Beryllium
0.160
U
1.00
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Cobalt
1.40
U
10.0
ug/L
Copper
1.60
U
10.0
ug/L
Iron
22.0
U
50.0
ug/L
Lead
3.10
U
10.0
ug/L
Manganese
1.50
U
10.0
ug/L
Nickel
2.20
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
Vanadium
1.40
U
10.0
ug/L
Zinc
4.40
U
10.0
ug/L
LCS (9K25033-BS1)
Prepared: 11/25/2019 12:44 Analyzed: 12/03/2019 11:00
Spike
Source
%REC
RPD
Analvte
Result Flag
POL
Units
Level
Result %REC
Limits
RPD Limit Notes
Arsenic
191
10.0
ug/L
200
95
80-120
Barium
192
10.0
ug/L
200
96
80-120
Beryllium
18.4
1.00
ug/L
20.0
92
80-120
FINAL
This report relates only to
the sample as received by the
laboratory, and
may only be reproduced in
full.
Page 61 of 92

(� �Eo
www.encolabs.com
QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K25033 - EPA 3005A - Continued
LCS (9K25033-BS3) Continued Prepared: 11/25/2019 12:44 Analyzed: 12/03/2019 11:00
Spike
Source
%REC
RPD
Analvte
Result Flaa
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Cadmium
18.6
1.00
ug/L
20.0
93
80-120
Chromium
189
10.0
ug/L
200
94
80-120
Cobalt
194
10.0
ug/L
200
97
80-120
Copper
188
10.0
ug/L
200
94
80-120
Iron
987
50.0
ug/L
1000
99
80-120
Lead
187
10.0
ug/L
200
93
80-120
Manganese
190
10.0
ug/L
200
95
80-120
Nickel
190
10.0
ug/L
200
95
80-120
Selenium
194
10.0
ug/L
200
97
80-120
Silver
192
10.0
ug/L
200
96
80-120
Vanadium
190
10.0
ug/L
200
95
80-120
Zinc
188
10.0
ug/L
200
94
80-120
Matrix Spike (9K25033-MS1)
Prepared:
11/25/2019
12:44 Analyzed: 12/03/2019 11:03
Source: CC18499-01
Spike
Source
%REC
RPD
Analvte
Result Flaa
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Arsenic
206
10.0
ug/L
200
7.60 U
103
75-125
Barium
280
10.0
ug/L
200
75.4
102
75-125
Beryllium
20.6
1.00
ug/L
20.0
0.160 U
103
75-125
Cadmium
20.6
1.00
ug/L
20.0
0.360 U
103
75-125
Chromium
206
10.0
ug/L
200
1.40 U
103
75-125
Cobalt
214
10.0
ug/L
200
1.40 U
107
75-125
Copper
206
10.0
ug/L
200
1.60 U
103
75-125
Iron
1150
50.0
ug/L
1000
76.2
108
75-125
Lead
205
10.0
ug/L
200
3.10 U
103
75-125
Manganese
212
10.0
ug/L
200
5.11
103
75-125
Nickel
208
10.0
ug/L
200
2.20 U
104
75-125
Selenium
217
10.0
ug/L
200
6.20 U
108
75-125
Silver
212
10.0
ug/L
200
1.90 U
106
75-125
Vanadium
209
10.0
ug/L
200
1.40 U
104
75-125
Zinc
217
10.0
ug/L
200
11.7
103
75-125
Matrix Spike Dup (9K25033-MSD3)
Prepared:
11/25/2019
12:44 Analyzed: 12/03/2019 11:05
Source: CC18499-01
Spike
Source
%REC
RPD
Analvte
Result Flaa
Q
Units
Level
Result
%REC
Limits
RPD
Limit Notes
Arsenic
208
10.0
ug/L
200
7.60 U
104
75-125
0.9
20
Barium
284
10.0
ug/L
200
75.4
104
75-125
1
20
Beryllium
20.8
1.00
ug/L
20.0
0.160 U
104
75-125
1
20
Cadmium
20.6
1.00
ug/L
20.0
0.360 U
103
75-125
0.07
20
Chromium
209
10.0
ug/L
200
1.40 U
104
75-125
1
20
Cobalt
214
10.0
ug/L
200
1.40 U
107
75-125
0.2
20
Copper
209
10.0
ug/L
200
1.60 U
105
75-125
2
20
Iron
1170
50.0
ug/L
1000
76.2
109
75-125
1
20
Lead
207
10.0
ug/L
200
3.10 U
103
75-125
0.7
20
Manganese
215
10.0
ug/L
200
5.11
105
75-125
1
20
Nickel
212
10.0
ug/L
200
2.20 U
106
75-125
2
20
Selenium
223
10.0
ug/L
200
6.20 U
111
75-125
3
20
Silver
224
10.0
ug/L
200
1.90 U
112
75-125
5
20
Vanadium
211
10.0
ug/L
200
1.40 U
106
75-125
1
20
FINAL
This report relates only to the sample as received by the
laboratory, and
may only be
reproduced in
full.
Page 62 Of 92

(� �Eo
www.encolabs.com
QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K25033 - EPA 3005A - Continued
Matrix Spike Dup (9K25033-MSD3) Continued Prepared: 11/25/2019 12:44 Analyzed: 12/03/2019 11:05
Source: CC18499-01
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Zinc 221 10.0 ug/L 200 11.7 105 75-125 2 20
Post Spike (9K25033-PSI) Prepared: 11/25/2019 12:44 Analyzed: 12/03/2019 11:08
Source: CC18499-01
Spike
Source
%REC RPD
Analvte
Result
Flaq POL
Units
Level
Result
%REC
Limits RPD Limit Notes
Arsenic
0.207
0.0100
mg/L
0.200
-0.00421
103
80-120
Barium
0.281
0.0100
mg/L
0.200
0.0754
103
80-120
Beryllium
0.0205
0.00100
mg/L
0.0200
-7.25E-5
103
80-120
Cadmium
0.0206
0.00100
mg/L
0.0200
-5.95E-5
103
80-120
Chromium
0.207
0.0100
mg/L
0.200
0.000619
103
80-120
Cobalt
0.213
0.0100
mg/L
0.200
7.72E-5
107
80-120
Copper
0.206
0.0100
mg/L
0.200
0.00152
102
80-120
Iron
1.16
0.0500
mg/L
1.00
0.0762
108
80-120
Lead
0.207
0.0100
mg/L
0.200
0.00144
103
80-120
Manganese
0.213
0.0100
mg/L
0.200
0.00511
104
80-120
Nickel
0.209
0.0100
mg/L
0.200
0.000890
104
80-120
Selenium
0.216
0.0100
mg/L
0.200
0.00105
107
80-120
Silver
0.214
0.0100
mg/L
0.200
-8.70E-5
107
80-120
Vanadium
0.209
0.0100
mg/L
0.200
0.00101
104
80-120
Zinc
0.220
0.0100
mg/L
0.200
0.0117
104
80-120
Batch 9K25034 - EPA 3005A
Blank (9K25034-BLKS)
Prepared:
11/25/2019
12:52 Analyzed: 12/03/2019 12:47
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Lead
3.10
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
LCS (9K25034-BS1)
Prepared: 11/25/2019 12:52 Analyzed: 12/03/2019 12:56
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC Limits RPD
Limit Notes
Arsenic
185
10.0
ug/L
200
93 80-120
Barium
189
10.0
ug/L
200
95 80-120
Cadmium
18.3
1.00
ug/L
20.0
92 80-120
Chromium
190
10.0
ug/L
200
95 80-120
Lead
179
10.0
ug/L
200
90 80-120
Selenium
188
10.0
ug/L
200
94 80-120
Silver
194
10.0
ug/L
200
97 80-120
Matrix Spike (9K25034-MS1)
Prepared:
11/25/2019
12:52 Analyzed: 12/03/2019 13:00
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
Q
Units
Level
Result
%REC Limits RPD
Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 63 Of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K25034 - EPA 3005A - Continued
Matrix Spike (9K25034-MS3) Continued
Prepared:
11/25/2019
12:52 Analyzed: 12/03/2019 13:00
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC Limits RPD
Limit Notes
Arsenic
199
10.0
ug/L
200
7.60 U
100 75-125
Barium
238
10.0
ug/L
200
38.5
100 75-125
Cadmium
19.7
1.00
ug/L
20.0
0.360 U
98 75-125
Chromium
198
10.0
ug/L
200
1.40 U
99 75-125
Lead
196
10.0
ug/L
200
3.10 U
98 75-125
Selenium
207
10.0
ug/L
200
6.20 U
103 75-125
Silver
206
10.0
ug/L
200
1.90 U
103 75-125
Matrix Spike Dup (9K25034-MSD3)
Prepared:
11/25/2019
12:52 Analyzed: 12/03/2019 13:02
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC Limits RPD
Limit Notes
Arsenic
199
10.0
ug/L
200
7.60 U
100 75-125 0.0004
20
Barium
241
10.0
ug/L
200
38.5
101 75-125 1
20
Cadmium
20.1
1.00
ug/L
20.0
0.360 U
101 75-125 2
20
Chromium
200
10.0
ug/L
200
1.40 U
100 75-125 1
20
Lead
201
10.0
ug/L
200
3.10 U
100 75-125 2
20
Selenium
204
10.0
ug/L
200
6.20 U
102 75-125 2
20
Silver
210
10.0
ug/L
200
1.90 U
105 75-125 2
20
Post Spike (9K25034-PS1)
Prepared:
11/25/2019
12:52 Analyzed: 12/03/2019 13:12
Source: CC18642-03
Spike
Source
%REC RPD
Analvte
Result
Flaq POL
Units
Level
Result
%REC
Limits RPD Limit Notes
Arsenic
0.194
0.0100
mg/L
0.200
0.00124
97
80-120
Barium
0.234
0.0100
mg/L
0.200
0.0385
98
80-120
Cadmium
0.0198
0.00100
mg/L
0.0200
0.000166
98
80-120
Chromium
0.194
0.0100
mg/L
0.200
-0.000137
97
80-120
Lead
0.195
0.0100
mg/L
0.200
-0.000145
97
80-120
Selenium
0.206
0.0100
mg/L
0.200
-0.00177
103
80-120
Silver
0.201
0.0100
mg/L
0.200
0.000138
101
80-120
Batch 9K26013 - EPA 3005A
Blank (9K26013-BLK1)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:20
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Antimony 0.370 U 1.00 ug/L
Thallium 0.110 U 1.00 ug/L
LCS (9K26013-BS3) Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:24
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Antimony
22.3
1.00
ug/L
20.0
112
80-120
Thallium
21.8
1.00
ug/L
20.0
109
80-120
Matrix Spike (9K26013-MS3)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:28
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Antimony
44.6
2.00
ug/L
40.0
0.740 U
112
75-125
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 64 of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9K26013 - EPA 3005A - Continued
Matrix Spike (9K26013-MS3) Continued
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:28
Source: CC18513-03
Spike Source %REC
RPD
Analvte
Result Flaq
Q
Units
Level Result %REC Limits RPD
Limit Notes
Thallium
42.9
2.00
ug/L
40.0 0.220 U 107 75-125
Matrix Spike Dup (9K26013-MSD3)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:32
Source: CCIS513-03
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Antimony
45.1
2.00
ug/L
40.0 0.740 U 113 75-125 1
20
Thallium
42.6
2.00
ug/L
40.0 0.220 U 107 75-125 0.6
20
Post Spike (9K26013-PSI)
Prepared: 11/26/2019 10:07 Analyzed: 12/02/2019 18:37
Source: CC18513-03
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
Antimony
23.0
1.00
ug/L
20.0-0.00221 115 75-125
Thallium
21.8
1.00
ug/L
20.0 0.0188 109 75-125
Batch 9L02012 - EPA 3005A
Blank (9L02012-BLK1) Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 10:29
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Beryllium
0.160
U
1.00
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Cobalt
1.40
U
10.0
ug/L
Copper
1.60
U
10.0
ug/L
Iron
22.0
U
50.0
ug/L
Lead
3.10
U
10.0
ug/L
Manganese
1.50
U
10.0
ug/L
Nickel
2.20
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
Vanadium
1.40
U
10.0
ug/L
Zinc
4.40
U
10.0
ug/L
LCS (911-02012-BSI)
Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:16
Spike
Source
%REC RPD
Analvte
Result Flaq
POL
Units
Level
Result %REC
Limits RPD Limit Notes
Arsenic
187
10.0
ug/L
200
94
80-120
Barium
183
10.0
ug/L
200
91
80-120
Beryllium
18.6
1.00
ug/L
20.0
93
80-120
Cadmium
18.4
1.00
ug/L
20.0
92
80-120
Chromium
184
10.0
ug/L
200
92
80-120
Cobalt
189
10.0
ug/L
200
94
80-120
Copper
184
10.0
ug/L
200
92
80-120
Iron
913
50.0
ug/L
1000
91
80-120
Lead
185
10.0
ug/L
200
92
80-120
Manganese
185
10.0
ug/L
200
92
80-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 65 Of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02012 - EPA 3005A - Continued
LCS (9L02012-BS3) Continued Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:16
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Nickel
184
10.0
ug/L
200
92
80-120
Selenium
185
10.0
ug/L
200
92
80-120
Silver
192
10.0
ug/L
200
96
80-120
Vanadium
186
10.0
ug/L
200
93
80-120
Zinc
191
10.0
ug/L
200
95
80-120
Matrix Spike (911-02012-MS1)
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:19
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
182
10.0
ug/L
200
7.60 U
91
75-125
Barium
215
10.0
ug/L
200
32.4
92
75-125
Beryllium
18.9
1.00
ug/L
20.0
0.160 U
95
75-125
Cadmium
18.2
1.00
ug/L
20.0
0.360 U
91
75-125
Chromium
186
10.0
ug/L
200
1.40 U
93
75-125
Cobalt
188
10.0
ug/L
200
1.40 U
94
75-125
Copper
189
10.0
ug/L
200
1.60 U
94
75-125
Iron
942
50.0
ug/L
1000
124
82
75-125
Lead
186
10.0
ug/L
200
3.10 U
93
75-125
Manganese
229
10.0
ug/L
200
44.8
92
75-125
Nickel
184
10.0
ug/L
200
2.20 U
92
75-125
Selenium
186
10.0
ug/L
200
6.20 U
93
75-125
Silver
194
10.0
ug/L
200
1.90 U
97
75-125
Vanadium
190
10.0
ug/L
200
2.12
94
75-125
Zinc
190
10.0
ug/L
200
4.40 U
95
75-125
Matrix Spike Dup (9L02012-MSD1)
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:22
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
185
10.0
ug/L
200
7.60 U
92
75-125
1
20
Barium
221
10.0
ug/L
200
32.4
95
75-125
3
20
Beryllium
19.4
1.00
ug/L
20.0
0.160 U
97
75-125
2
20
Cadmium
18.5
1.00
ug/L
20.0
0.360 U
93
75-125
2
20
Chromium
191
10.0
ug/L
200
1.40 U
96
75-125
3
20
Cobalt
193
10.0
ug/L
200
1.40 U
96
75-125
2
20
Copper
194
10.0
ug/L
200
1.60 U
97
75-125
3
20
Iron
1010
50.0
ug/L
1000
124
89
75-125
7
20
Lead
188
10.0
ug/L
200
3.10 U
94
75-125
0.8
20
Manganese
236
10.0
ug/L
200
44.8
95
75-125
3
20
Nickel
190
10.0
ug/L
200
2.20 U
95
75-125
4
20
Selenium
182
10.0
ug/L
200
6.20 U
91
75-125
2
20
Silver
199
10.0
ug/L
200
1.90 U
100
75-125
3
20
Vanadium
196
10.0
ug/L
200
2.12
97
75-125
3
20
Zinc
196
10.0
ug/L
200
4.40 U
98
75-125
3
20
Post Spike (911-02012-PSI)
Prepared:
12/02/2019
09:35 Analyzed: 12/05/2019 13:24
Source: CC18513-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
0.185
0.0100
mg/L
0.200
-0.00934
93
80-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 66 Of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L02012 - EPA 3005A - Continued
Post Spike (911-02012-PSI) Continued Prepared: 12/02/2019 09:35 Analyzed: 12/05/2019 13:24
Source: CC18513-03
Spike
Source
%REC
Analvte
Result
Flaq POL
Units
Level
Result
%REC
Limits RPD
Barium
0.221
0.0100
mg/L
0.200
0.0324
94
80-120
Beryllium
0.0197
0.00100
mg/L
0.0200
8.06E-5
98
80-120
Cadmium
0.0190
0.00100
mg/L
0.0200
-0.000194
95
80-120
Chromium
0.193
0.0100
mg/L
0.200
0.000391
96
80-120
Cobalt
0.196
0.0100
mg/L
0.200
-0.000223
98
80-120
Copper
0.195
0.0100
mg/L
0.200
-0.000112
98
80-120
Iron
1.02
0.0500
mg/L
1.00
0.124
89
80-120
Lead
0.196
0.0100
mg/L
0.200
0.000195
98
80-120
Manganese
0.236
0.0100
mg/L
0.200
0.0448
96
80-120
Nickel
0.191
0.0100
mg/L
0.200
0.00162
95
80-120
Selenium
0.187
0.0100
mg/L
0.200
-0.00931
93
80-120
Silver
0.210
0.0100
mg/L
0.200
0.000488
105
80-120
Vanadium
0.197
0.0100
mg/L
0.200
0.00212
97
80-120
Zinc
0.199
0.0100
mg/L
0.200
0.00338
98
80-120
Batch 9L03016 - EPA 3005A
Blank (9L03016-BLK1) Prepared: 12/03/2019 10:18 Analyzed: 12/05/2019 10:39
RPD
Limit Notes
Spike Source %REC RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD Limit Notes
Arsenic
7.60
U
10.0
ug/L
Barium
1.10
U
10.0
ug/L
Beryllium
0.160
U
1.00
ug/L
Cadmium
0.360
U
1.00
ug/L
Chromium
1.40
U
10.0
ug/L
Cobalt
1.40
U
10.0
ug/L
Copper
1.60
U
10.0
ug/L
Iron
22.0
U
50.0
ug/L
Lead
3.10
U
10.0
ug/L
Manganese
1.50
U
10.0
ug/L
Nickel
2.20
U
10.0
ug/L
Selenium
6.20
U
10.0
ug/L
Silver
1.90
U
10.0
ug/L
Vanadium
1.40
U
10.0
ug/L
Zinc
4.40
U
10.0
ug/L
LCS (911-03016-BSI)
Prepared: 12/03/2019 10:18 Analyzed: 12/05/2019 15:02
Spike
Source
%REC
Analvte
Result Flaq
POL
Units
Level
Result %REC
Limits
Arsenic
211
10.0
ug/L
200
106
80-120
Barium
216
10.0
ug/L
200
108
80-120
Beryllium
20.8
1.00
ug/L
20.0
104
80-120
Cadmium
20.4
1.00
ug/L
20.0
102
80-120
Chromium
207
10.0
ug/L
200
104
80-120
Cobalt
213
10.0
ug/L
200
106
80-120
Copper
211
10.0
ug/L
200
105
80-120
Iron
1040
50.0
ug/L
1000
104
80-120
Lead
208
10.0
ug/L
200
104
80-120
Manganese
208
10.0
ug/L
200
104
80-120
RPD
RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full
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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L03016 - EPA 3005A - Continued
LCS (9L03016-BS3) Continued Prepared: 12/03/2019 10:18 Analyzed: 12/05/2019 15:02
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Nickel
206
10.0
ug/L
200
103
80-120
Selenium
206
10.0
ug/L
200
103
80-120
Silver
216
10.0
ug/L
200
108
80-120
Vanadium
209
10.0
ug/L
200
104
80-120
Zinc
216
10.0
ug/L
200
108
80-120
Matrix Spike (9L03016-MS3)
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:05
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
199
10.0
ug/L
200
7.60 U
100
75-125
Barium
408
10.0
ug/L
200
200
104
75-125
Beryllium
21.5
1.00
ug/L
20.0
1.11
102
75-125
Cadmium
19.7
1.00
ug/L
20.0
0.360 U
99
75-125
Chromium
202
10.0
ug/L
200
1.40 U
101
75-125
Cobalt
211
10.0
ug/L
200
3.81
103
75-125
Copper
218
10.0
ug/L
200
10.7
104
75-125
Iron
5700
50.0
ug/L
1000
5220
48
75-125
QM-07
Lead
212
10.0
ug/L
200
7.59
102
75-125
Manganese
253
10.0
ug/L
200
55.1
99
75-125
Nickel
204
10.0
ug/L
200
4.12
100
75-125
Selenium
205
10.0
ug/L
200
6.20 U
102
75-125
Silver
211
10.0
ug/L
200
1.90 U
105
75-125
Vanadium
207
10.0
ug/L
200
4.04
102
75-125
Zinc
214
10.0
ug/L
200
8.00
103
75-125
Matrix Spike Dup (9L03016-MSD1)
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:07
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
198
10.0
ug/L
200
7.60 U
99
75-125
0.6
20
Barium
407
10.0
ug/L
200
200
103
75-125
0.2
20
Beryllium
21.0
1.00
ug/L
20.0
1.11
99
75-125
2
20
Cadmium
19.0
1.00
ug/L
20.0
0.360 U
95
75-125
4
20
Chromium
197
10.0
ug/L
200
1.40 U
99
75-125
2
20
Cobalt
203
10.0
ug/L
200
3.81
100
75-125
3
20
Copper
210
10.0
ug/L
200
10.7
100
75-125
4
20
Iron
5790
50.0
ug/L
1000
5220
57
75-125
2
20
QM-07
Lead
196
10.0
ug/L
200
7.59
94
75-125
8
20
Manganese
250
10.0
ug/L
200
55.1
97
75-125
1
20
Nickel
199
10.0
ug/L
200
4.12
98
75-125
2
20
Selenium
201
10.0
ug/L
200
6.20 U
100
75-125
2
20
Silver
205
10.0
ug/L
200
1.90 U
102
75-125
3
20
Vanadium
202
10.0
ug/L
200
4.04
99
75-125
3
20
Zinc
207
10.0
ug/L
200
8.00
100
75-125
3
20
Post Spike (911-03016-PSI)
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:10
Source: CC19724-01
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits
RPD
Limit
Notes
Arsenic
0.195
0.0100
mg/L
0.200
0.00559
94
80-120
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 68 Of 92

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QUALITY CONTROL DATA
Metals (total recoverable) by EPA 6000/7000 Series Methods - Quality Control
Batch 9L03016 - EPA 3005A - Continued
Post Spike (911-03016-PSI) Continued
Prepared:
12/03/2019
10:18 Analyzed: 12/05/2019 15:10
Source: CC19724-01
Spike
Source
%REC RPD
Analvte
Result Flag
POL
Units
Level
Result
%REC
Limits RPD Limit Notes
Barium
0.375
0.0100
mg/L
0.200
0.200
88
80-120
Beryllium
0.0201
0.00100
mg/L
0.0200
0.00111
95
80-120
Cadmium
0.0183
0.00100
mg/L
0.0200
-0.000125
92
80-120
Chromium
0.190
0.0100
mg/L
0.200
0.00103
94
80-120
Cobalt
0.194
0.0100
mg/L
0.200
0.00381
95
80-120
Copper
0.198
0.0100
mg/L
0.200
0.0107
94
80-120
Iron
5.79
0.0500
mg/L
1.00
5.22
57
80-120 QM-07
Lead
0.188
0.0100
mg/L
0.200
0.00759
90
80-120
Manganese
0.243
0.0100
mg/L
0.200
0.0551
94
80-120
Nickel
0.192
0.0100
mg/L
0.200
0.00412
94
80-120
Selenium
0.192
0.0100
mg/L
0.200
-0.00212
96
80-120
Silver
0.205
0.0100
mg/L
0.200
0.000380
102
80-120
Vanadium
0.195
0.0100
mg/L
0.200
0.00404
96
80-120
Zinc
0.193
0.0100
mg/L
0.200
0.00800
93
80-120
Classical Chemistry Parameters
- Quality Control
Batch 9K21007 - NO PREP
Blank (9K23007-BLK1) Prepared: 11/21/2019 08:50 Analyzed: 11/21/2019 09:48
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Nitrite as N 17 U 100 ug/L
LCS (9K21007-BS3) Prepared: 11/21/2019 08:50 Analyzed: 11/21/2019 09:40
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1.0
0.10
mg/L
1.00 101 90-110
Matrix Spike (9K21007-MS3)
Prepared: 11/21/2019 08:50 Analyzed: 11/21/2019 09:50
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1100
100
ug/L
1000 17 U 112 90-110
QM-07
Matrix Spike Dup (9K23007-MSD3)
Prepared: 11/21/2019 08:50 Analyzed: 11/21/2019 09:51
111
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1100
100
ug/L
1000 17 U 114 90-110 1
10 QM-07
Batch 9K22006 - NO PREP
Blank (9K22006-BLKS)
Prepared & Analyzed: 11/22/2019 15:21
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Total Dissolved Solids
50000 U
50000
ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 69 Of 92

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K22006 - NO PREP - Continued
LCS (9K22006-BS3) Prepared & Analyzed: 11/22/2019 15:21
Spike Source %REC
RPD
Analvte
Result Flag
Q
Units
Level Result %REC Limits
RPD
Limit
Notes
Total Dissolved Solids
990
50
mg/L
1000 99 80-120
Duplicate (9K22006-DUPi)
Prepared & Analyzed: 11/22/2019 15:21
Source: CC18494-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Total Dissolved Solids
540000
50000
ug/L
550000
2
20
Duplicate (9K22006-DUP2)
Prepared & Analyzed: 11/22/2019 15:21
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Total Dissolved Solids
74000
50000
ug/L
52000
35
20
QM-12
Batch 9K22014 - NO PREP
Blank (9K22014-BLK1) Prepared: 11/22/2019 10:51 Analyzed: 11/22/2019 10:51
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Nitrite as N 17 U 100 ug/L
LCS (9K22014-BS3) Prepared: 11/22/2019 11:05 Analyzed: 11/22/2019 11:05
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1.0
0.10
mg/L
1.00 105 90-110
Matrix Spike (9K22014-MSI)
Prepared: 11/22/2019 10:53 Analyzed: 11/22/2019 10:53
Source: CC14689-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1100
100
ug/L
1000 78 102 90-110
Matrix Spike (9K22014-MS2)
Prepared: 11/22/2019 10:56 Analyzed: 11/22/2019 10:56
Source: CC18333-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Nitrite as N
1000
100
ug/L
1000 17 U 103 90-110
Matrix Spike Dup (9K22014-MSD3)
Prepared: 11/22/2019 10:54 Analyzed: 11/22/2019 10:54
Source: CC14689-01
Spike
Source
%REC
RPD
Analvte
Result Flag
POL
Units
Level
Result
%REC Limits RPD
Limit Notes
Nitrite as N
1100
100
ug/L
1000
78
99 90-110 2
10
Batch 9K22033 - NO PREP
Blank (9K22033-BLKS)
Prepared: 11/22/2019 13:48 Analyzed: 11/22/2019 17:04
Spike
Source
%REC
RPD
Analvte
Result Flag
POL
Units
Level
Result
%REC Limits RPD
Limit Notes
Total Alkalinity as CaCO3
14000 U
15000
ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 7O Of 92

QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K22033 - NO PREP - Continued
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LCS (9K22033-BS3) Prepared: 11/22/2019 13:48 Analyzed: 11/22/2019 17:06
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
99
15
mg/L
100 99 80-120
Matrix Spike (9K22033-MSi)
Prepared: 11/22/2019 13:48 Analyzed: 11/22/2019 17:07
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
72000
15000
ug/L
37800 22000 132 80-120
QM-07
Matrix Spike (9K22033-MS2)
Prepared: 11/22/2019 13:48 Analyzed: 11/22/2019 17:11
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
46000
15000
ug/L
37800 14000 U 121 80-120
QM-07
Matrix Spike Dup (9K22033-MSD3)
Prepared: 11/22/2019 13:48 Analyzed: 11/22/2019 17:08
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
71000
15000
ug/L
37800 22000 128 80-120 2
25
QM-07
Batch 9K23002 - NO PREP
Blank (9K23002-BLK1) Prepared: 11/23/2019 11:55 Analyzed: 11/23/2019 12:18
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Sulfide 10 U 100 ug/L
LCS (9K23002-BS3) Prepared: 11/23/2019 11:55 Analyzed: 11/23/2019 12:18
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
0.35
0.10
mg/L
0.401 88 80-120
Duplicate (9K23002-DUPl)
Prepared: 11/23/2019 11:55 Analyzed: 11/23/2019 12:18
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
10
U
100
ug/L
10 U
25
Matrix Spike (9K23002-MSi)
Prepared: 11/23/2019 11:55 Analyzed: 11/23/2019 12:18
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
340
100
ug/L
401 10 U 85 80-120
Matrix Spike Dup (9K23002-MSD3)
Prepared: 11/23/2019 11:55 Analyzed: 11/23/2019 12:18
Source: CC18499-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
340
100
ug/L
401 10 U 86 80-120 1
25
Batch 9K23003 - NO PREP
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 71 of 92

QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K23003 - NO PREP - Continued
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Blank (9K23003-BLKI) Prepared: 11/23/2019 13:28 Analyzed: 11/23/2019 13:54
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Sulfide 10 U 100 ug/L
LCS (9K23003-BSI) Prepared: 11/23/2019 13:28 Analyzed: 11/23/2019 13:54
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
0.35
0.10
mg/L
0.401 88 80-120
Duplicate (9K23003-DUPI)
Prepared: 11/23/2019 13:28 Analyzed: 11/23/2019 13:54
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
10
U
100
ug/L
10 U
25
Matrix Spike (9K23003-MS3)
Prepared: 11/23/2019 13:28 Analyzed: 11/23/2019 13:54
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flaq
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
340
100
ug/L
401 10 U 85 80-120
Matrix Spike Dup (9K23003-MSD3)
Prepared: 11/23/2019 13:28 Analyzed: 11/23/2019 13:54
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
340
100
ug/L
401 10 U 86 80-120 1
25
Batch 9K23005 - NO PREP
Blank (9K23005-BLKS) Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Sulfide 10 U 100 ug/L
LCS (9K23005-BS3) Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
0.35
0.10
mg/L
0.401 87 80-120
Duplicate (9K23005-DUP3)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
10
U
100
ug/L
10 U
25
Matrix Spike (9K23005-MSI)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Sulfide
260
100
ug/L
401 10 U 64 80-120
QM-07
Matrix Spike Dup (9K23005-MSD3)
Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. F Page 72 Of 92

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K23005 - NO PREP - Continued
Matrix Spike Dup (9K23005-MSD3) Continued Prepared: 11/23/2019 14:42 Analyzed: 11/23/2019 14:59
Source: CC18501-07
Spike Source %REC RPD
Analvte Result Flag Q Units Level Result %REC Limits RPD Limit Notes
Sulfide 320 100 ug/L 401 10 U 80 80-120 22 25
Batch 9K27004 - NO PREP
Blank (9K27004-BLK1) Prepared & Analyzed: 11/27/2019 17:42
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Total Dissolved Solids 50000 U 50000 ug/L
LCS (9K27004-BS3) Prepared & Analyzed: 11/27/2019 17:42
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
980
50
mg/L
1000 98 80-120
Duplicate (9K27004-DUPl)
Prepared & Analyzed: 11/27/2019 17:42
Source: CC16655-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
270000
50000
ug/L
270000
1
20
Duplicate (9K27004-DUP2)
Prepared & Analyzed: 11/27/2019 17:42
Source: CC16869-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits
RPD
Limit Notes
Total Dissolved Solids
2300000
50000
ug/L
2400000
2
20
Batch 9LO2007 - NO PREP
Blank (9L02007-BLK1) Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:05
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Total Alkalinity as CaCO3 14000 U 15000 ug/L
LCS (9L02007-BS3) Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:06
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
100
15
mg/L
100
101
80-120
Matrix Spike (911-02007-MS3)
Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:07
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
410000
DE
30000
ug/L
37800
380000
61
80-120
QM-07
Matrix Spike Dup (911-02007-MSDl)
Prepared: 12/02/2019 09:20 Analyzed: 12/02/2019 13:08
Source: CC18494-01
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Alkalinity as CaCO3
420000
DE
30000
ug/L
37800
380000
84
80-120 2
25
Batch 9LO2037 - NO PREP
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 73 Of 92

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO2037 - NO PREP - Continued
Blank (9L02037-BLK3) Prepared: 12/02/2019 14:00 Analyzed: 12/02/2019 17:04
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
Sulfate as SO4 2900 U 5000 ug/L
LCS (911-02037-BSI) Prepared: 12/02/2019 14:00 Analyzed: 12/02/2019 17:21
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
48000
5000
ug/L
50000
97
90-110
Sulfate as SO4
48000
5000
ug/L
50000
95
90-110
Matrix Spike (911-02037-MS1)
Prepared: 12/02/2019 14:00 Analyzed: 12/02/2019 17:57
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
24000
5000
ug/L
20000
5100
94
90-110
Sulfate as SO4
28000
5000
ug/L
20000
9200
96
90-110
Matrix Spike (91-02037-MS2)
Prepared: 12/02/2019 14:00 Analyzed: 12/02/2019 18:50
Source: CC18496-07
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
88000
5000
ug/L
20000
68000
98
90-110
Sulfate as SO4
63000
5000
ug/L
20000
43000
101
90-110
Matrix Spike Dup (9L02037-MSD1)
Prepared: 12/02/2019 14:00 Analyzed: 12/02/2019 18:14
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result
Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
24000
5000
ug/L
20000
5100
96
90-110 1
10
Sulfate as SO4
29000
5000
ug/L
20000
9200
97
90-110 1
10
Batch 9LO3017 - NO PREP
Blank (9L03017-BLK3) Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 15:44
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
Sulfate as SO4 2900 U 5000 ug/L
LCS (9L03017-BS3) Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:02
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Chloride 49000 5000 ug/L 50000 99 90-110
Sulfate as SO4 51000 5000 ug/L 50000 101 90-110
Matrix Spike (911-03017-MS1) Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:37
Source: CC18494-01
Spike
Source
%REC RPD
Analvte Result Flaq POL Units
Level
Result
%REC Limits RPD Limit Notes
Chloride 67000 5000 ug/L
20000
47000
104 90-110
Sulfate as SO4 37000 5000 ug/L
20000
16000
104 90-110
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 74 Of 92

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO3017 - NO PREP - Continued
Matrix Spike (911-03017-MS2)
Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 17:30
Source: CC18500-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
20000
5000
ug/L
20000 2200 U 102 90-110
Sulfate as SO4
21000
5000
ug/L
20000 2900 U 106 90-110
Matrix Spike Dup (9L03017-MSD1)
Prepared: 12/03/2019 10:48 Analyzed: 12/03/2019 16:55
Source: CC18494-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Chloride
68000
5000
ug/L
20000 47000 108 90-110 1
10
Sulfate as SO4
37000
5000
ug/L
20000 16000 106 90-110 0.9
10
Batch 9LO3027 - NO PREP
Blank (9L03027-BLK3) Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 01:10
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
Sulfate as SO4 2900 U 5000 ug/L
LCS (9L03027-BS3) Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 01:27
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
50000
5000
ug/L
50000
100
90-110
Sulfate as SO4
51000
5000
ug/L
50000
102
90-110
Matrix Spike (911-03027-MS1)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 02:20
Source: CC19657-02
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
32000
5000
ug/L
20000
13000
100
90-110
Sulfate as SO4
34000
5000
ug/L
20000
13000
104
90-110
Matrix Spike (911-03027-MS2)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 03:13
Source: CC19657-03
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
43000
5000
ug/L
26700
22000
77
90-110
QM-07
Sulfate as SO4
19000
5000
ug/L
26700
2900 U
73
90-110
QM-07
Matrix Spike Dup (9L03027-MSDI)
Prepared: 12/03/2019 11:54 Analyzed: 12/04/2019 02:38
Source: CC19657-02
Spike
Source
%REC
RPD
Analvte
Result
Flag
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Chloride
33000
5000
ug/L
20000
13000
100
90-110 0.3
10
Sulfate as SO4
34000
5000
ug/L
20000
13000
105
90-110 0.3
10
Batch 9LO5016 - NO PREP
Blank (9L05016-BLK1) Prepared: 12/05/2019 09:20 Analyzed: 12/05/2019 13:02
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Nitrate/Nitrite as N 41 U 100 ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 75 Of 92

QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO5016 - NO PREP - Continued
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LCS (9L05016-BS3) Prepared: 12/05/2019 09:20 Analyzed: 12/05/2019 13:04
Spike Source %REC
RPD
Analvte
Result
Flag
Q
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
1.3
0.10
mg/L
1.25 102 90-110
Matrix Spike (911-05016-MS3)
Prepared: 12/05/2019 09:20 Analyzed: 12/05/2019 13:08
Source: CCI8642-03
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
510
100
ug/L
521 41 U 99 90-110
Matrix Spike (911-05016-MS2)
Prepared: 12/05/2019 09:20 Analyzed: 12/05/2019 13:13
Source: CC18642-01
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
1100
100
ug/L
521 510 106 90-110
Matrix Spike Dup (9L05016-MSD3)
Prepared: 12/05/2019 09:20 Analyzed: 12/05/2019 13:09
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
530
100
ug/L
521 41 U 101 90-110 2
10
Batch 9LO5042 - NO PREP
Blank (911-05042-BLK3) Prepared: 12/05/2019 12:42 Analyzed: 12/05/2019 16:56
Spike Source %REC RPD
Analvte Result Flag POL Units Level Result %REC Limits RPD Limit Notes
Nitrate/Nitrite as N 41 U 100 ug/L
LCS (911-05042-BSI) Prepared: 12/05/2019 12:42 Analyzed: 12/05/2019 16:57
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
1.2
0.10
mg/L
1.25 100 90-110
Matrix Spike (9L05042-MS3)
Prepared: 12/05/2019 12:42 Analyzed: 12/05/2019 17:01
Source: CC18337-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
520
100
ug/L
521 41 U 99 90-110
Matrix Spike (911-05042-MS2)
Prepared: 12/05/2019 12:42 Analyzed: 12/05/2019 17:07
Source: CC19657-02
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit
Notes
Nitrate/Nitrite as N
480
100
ug/L
521 67 80 90-110
QM-07
Matrix Spike Dup (9L05042-MSDI)
Prepared: 12/05/2019 12:42 Analyzed: 12/05/2019 17:03
Ill
Source: CC18337-01
Analvte
Nitrate/Nitrite as N
Batch 9LO6012 - NO PREP
Spike Source %REC
Result Flag POL Units Level Result %REC Limits RPD
490 100 ug/L 521 41 U 95 90-110 5
RPD
Limit Notes
10
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 76 Of 92

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QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9LO6012 - NO PREP - Continued
Blank (9L06012-BLK3) Prepared & Analyzed: 12/13/2019 15:08
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Chloride 2200 U 5000 ug/L
LCS (911-06012-BSI) Prepared & Analyzed: 12/13/2019 15:26
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Chloride
49000
5000
ug/L
50000 98 90-110
Matrix Spike (911-06012-MS3)
Prepared & Analyzed: 12/13/2019 16:19
Source: CC07847-02
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Chloride
140000
10000
ug/L
40000 110000 93 90-110
Matrix Spike (91-06012-MS2)
Prepared & Analyzed: 12/13/2019 17:47
Source: CC07847-01
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Chloride
76000
5000
ug/L
20000 57000 99 90-110
Matrix Spike Dup (91-06012-MS131)
Prepared & Analyzed: 12/13/2019 16:36
Source: CC07847-02
Spike Source %REC
RPD
Analvte
Result
Flaq
POL
Units
Level Result %REC Limits
RPD
Limit
Notes
Chloride
140000
10000
ug/L
40000 110000 95 90-110
0.5
10
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9K25041 - EPA 5030E MS
Blank (9K25041-BLK1)
Prepared: 11/25/2019 13:53 Analyzed: 11/26/2019 00:14
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 0.80 U 2.0 ug/L
Toluene-d8 5.7 u91L 5.00 114 75-125
LCS (9K25041-BS1) Prepared: 11/25/2019 13:53 Analyzed: 11/25/2019 21:52
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,4-Dioxane
25
2.0
ug/L
25.0
101
80-133
Toluene-d8
5.5
ug/L
5.00
109
75-125
Matrix Spike (9K25041-MS1)
Prepared: 11/25/2019 13:53 Analyzed: 11/25/2019 22:28
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,4-Dioxane
25
2.0
ug/L
25.0
1.3
95
80-133
Toluene-& 5.3 ug/L 5.00 106 75-125
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 77 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9K25041 - EPA 5030E MS - Continued
Matrix Spike Dup (9K25041-MSD3) Prepared: 11/25/2019 13:53 Analyzed: 11/25/2019 23:05
Source: CC18642-03
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 28 2.0 ug/L 25.0 1.3 105 80-133 10 19
Toluene-d8 5.8 u91L 5.00 116 75-125
Batch 9K26030 - EPA 5030B MS
Blank (9K26030-BLKS) Prepared: 11/26/2019 00:00 Analyzed: 11/26/2019 10:52
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 0.80 U 2.0 ug/L
Toluene-d8 5.2 u91L 5.00 104 75-125
LCS (9K26030-BS1) Prepared: 11/26/2019 00:00 Analyzed: 11/26/2019 09:47
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,4-Dioxane
25
2.0
ug/L
25.0
99
80-133
Toluene-d8
5.1
u91L
5.00
102
75-125
Matrix Spike (9K26030-MS1)
Prepared: 11/26/2019 00:00 Analyzed: 11/26/2019 19:44
Source: AC08215-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
1,4-Dioxane
22
2.0
ug/L
25.0
0.80 U
89
80-133
Toluene-d8
4.6
u91L
5.00 93 75-125
Matrix Spike Dup (9K26030-MSD1)
Prepared: 11/26/2019 00:00 Analyzed: 11/26/2019 20:21
Source: AC08215-01
Spike Source %REC RPD
Analvte
Result Flaq POL
Units
Level Result %REC Limits RPD Limit Notes
1,4-Dioxane
24 2.0
ug/L
25.0 0.80 U 94 80-133 6 19
Toluene-d8
4.9
u91L
5.00 97 75-125
Batch 9L01004 - EPA 5030E MS
Blank (9L01004-BLK3)
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 23:22
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 0.80 U 2.0 ug/L
Toluene-d8 5.5 u91L 5.00 109 75-125
LCS (9L01004-BS1) Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 20:57
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
1,4-Dioxane 23 2.0 ug/L 25.0 92 80-133
Toluene-d8 4.8 u91L 5.00 96 75-125
Matrix Spike (9L03004-MS1) Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 21:33
Source: AC08266-11
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 78 Of 92

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QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS SIM Isotope Dilution - Quality Control
Batch 9L01004 - EPA 50308 MS - Continued
Matrix Spike (9L01004-MS3) Continued
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 21:33
Source: AC08266-11
Spike
Source
%REC
RPD
Analvte Result Flaq
POL Units
Level
Result
%REC Limits RPD
Limit Notes
1,4-Dioxane 23
2.0 ug/L
25.0
0.80 U
92 80-133
Toluene-d8 5.5
u91L
5.00
110 75-125
Matrix Spike Dup (9L01004-MSDI)
Prepared: 12/01/2019 13:20 Analyzed: 12/01/2019 22:09
Source: AC08266-11
Spike
Source
%REC
RPD
Analvte Result Flaq
POL Units
Level
Result
%REC Limits RPD
Limit Notes
1,4-Dioxane 23
2.0 ug/L
25.0
0.80 U
92 80-133 0.5
19
Toluene-d8
5.0
u9/L
5.00 100 75-125
Batch 9L02040 - EPA 50308 MS
Blank (9L02040-BLK3)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 11:40
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
1,4-Dioxane
0.80 U
2.0
ug/L
Toluene-d8
4.8
u91L
5.00 95 75-125
LCS (911-02040-BSI)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 10:30
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit Notes
1,4-Dioxane
24
2.0
ug/L
25.0 94 80-133
Toluene-d8
4.9
u9/L
5.00 97 75-125
Matrix Spike (9L02040-MS1)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 15:37
Source: CC19664-01
Spike Source %REC
RPD
Analvte
Result Flaa
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
42
2.0
ug/L
25.0 22 78 80-133
QM-07
Toluene-d8
4.7
u91L
5.00 95 75-125
Matrix Spike Dup (911-02040-MSD1)
Prepared: 12/02/2019 00:00 Analyzed: 12/02/2019 16:15
Source: CC19664-01
Spike Source %REC
RPD
Analvte
Result Flaq
POL
Units
Level Result %REC Limits RPD
Limit
Notes
1,4-Dioxane
41
2.0
ug/L
25.0 22 75 80-133 2
19
QM-07
Toluene-d8 4.9 u9/L 5.00 97 75-125
Classical Chemistry Parameters - Quality Control
Batch 9K22006 - NO PREP
Blank (9K22006-BLK1) Prepared: 11/22/2019 09:00 Analyzed: 11/22/2019 10:37
Spike Source %REC RPD
Analvte Result Flaq POL Units Level Result %REC Limits RPD Limit Notes
Total Organic Carbon 340 U 1000 ug/L
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 79 Of 92

QUALITY CONTROL DATA
Classical Chemistry Parameters - Quality Control
Batch 9K22006 - NO PREP - Continued
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LCS (9K22006-BS3) Prepared: 11/22/2019 09:00 Analyzed: 11/22/2019 10:37
Spike
Source
%REC
RPD
Analvte
Result Flaq
Q
Units
Level
Result
%REC
Limits RPD
Limit Notes
Total Organic Carbon
38000
1000
ug/L
40000
95
85-115
Matrix Spike (9K22006-MSi)
Prepared: 11/22/2019 09:00 Analyzed: 11/22/2019 10:37
Source: CC38642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Total Organic Carbon
41000
1000
ug/L
40000
1100
99
85-115
Matrix Spike Dup (9K22006-MSD3)
Prepared: 11/22/2019 09:00 Analyzed: 11/22/2019 10:37
Source: CC18642-03
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit Notes
Total Organic Carbon
39000
1000
ug/L
40000
1100
95
85-115 4
21
Batch 9K26002 - NO PREP
Blank (9K26002-BLK1) Prepared: 11/26/2019 12:00 Analyzed: 11/26/2019 13:36
Spike Source %REC RPD
Analvte Result Flaq Q Units Level Result %REC Limits RPD Limit Notes
Total Organic Carbon 340 U 1000 ug/L
LCS (9K26002-BS3) Prepared: 11/26/2019 12:00 Analyzed: 11/26/2019 13:36
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Organic Carbon
36000
1000
ug/L
40000
90
85-115
Matrix Spike (9K26002-MSI)
Prepared: 11/26/2019 12:00 Analyzed: 11/26/2019 13:36
Source: AC08201-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Organic Carbon
90000
1000
ug/L
40000
58000
81
85-115
QM-07
Matrix Spike Dup (9K26002-MSD3)
Prepared: 11/26/2019 12:00 Analyzed: 11/26/2019 13:36
Source: AC08201-01
Spike
Source
%REC
RPD
Analvte
Result Flaq
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Total Organic Carbon
95000
1000
ug/L
40000
58000
93
85-115 5
21
Dissolved Gases by GC - Quality Control
Batch 9K21009 - Same
Blank (9K23009-BLK1)
Prepared: 11/21/2019 11:08 Analyzed: 11/21/2019 12:20
Spike Source %REC
RPD
Analvte
Result
Flaq
Q
Units
Level Result %REC Limits RPD
Limit Notes
Ethane
1.30
U
2.00
ug/L
Ethene
1.50
U
3.00
ug/L
Methane
0.450
U
1.00
ug/L
LCS (9K21009-BS1)
Prepared: 11/21/2019 11:08 Analyzed: 11/21/2019 12:36
Spike Source %REC
RPD
Analvte
Result
Flaq
Q
Units
Level Result %REC Limits RPD
Limit Notes
FINAL
This report relates only to the sample as received by the
laboratory, and may only be reproduced in full.
Page 80 of 92

0Nk"q09
www.encolabs.com
QUALITY CONTROL DATA
Dissolved Gases by GC - Quality Control
Batch 9K21009 - Same - Continued
LCS (9K21009-BSI) Continued Prepared: 11/21/2019 11:08 Analyzed: 11/21/2019 12:36
Spike Source %REC RPD
Analvte
Result
Flag POL
Units
Level Result %REC Limits RPD Limit Notes
Ethane
0.326
0.00200
mg/L
0.323 101 80-120
Ethene
0.315
0.00300
mg/L
0.302 104 80-120
Methane
0.161
0.00100
mg/L
0.172 94 80-120
LCS Dup (9K21009-BSD1)
Prepared: 11/21/2019 11:08 Analyzed: 11/21/2019 12:52
Spike Source %REC
RPD
Analvte
Result
Flag POL
Units
Level Result %REC Limits RPD
Limit Notes
Ethane
0.331
0.00200
mg/L
0.323 102 80-120 1
25
Ethene
0.312
0.00300
mg/L
0.302 103 80-120 0.9
25
Methane
0.165
0.00100
mg/L
0.172 96 80-120 2
25
Duplicate (9K21009-DUPi)
Prepared: 11/21/2019 11:08 Analyzed: 11/21/2019 15:00
Source: CC18642-03
Spike Source %REC
RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Ethane
1.30
U
2.00
ug/L
1.30 U
25
Ethene
1.50
U
3.00
ug/L
1.50 U
25
Methane
0.450
U
1.00
ug/L
0.450 U
25
Batch 9L03012 - Same
Blank (9L03012-BLKi)
Prepared: 12/03/2019 13:51 Analyzed: 12/03/2019 14:48
Spike Source %REC RPD
Analvte
Result
Flag
POL
Units
Level Result %REC Limits RPD Limit Notes
Ethane
1.30
U
2.00
ug/L
Ethene
1.50
U
3.00
ug/L
Methane
0.450
U
1.00
ug/L
LCS (91-03012-BSI)
Prepared: 12/03/2019 13:51 Analyzed: 12/03/2019 15:04
Spike Source %REC RPD
Analvte
Result
Flag POL
Units
Level Result %REC Limits RPD Limit Notes
Ethane
0.313
0.00200
mg/L
0.323 97 80-120
Ethene
0.293
0.00300
mg/L
0.302 97 80-120
Methane
0.161
0.00100
mg/L
0.172 94 80-120
LCS Dup (9L03012-BSD1)
Prepared: 12/03/2019 13:51 Analyzed: 12/03/2019 15:20
Spike Source %REC
RPD
Analvte
Result
Flag POL
Units
Level Result %REC Limits RPD
Limit Notes
Ethane
0.329
0.00200
mg/L
0.323 102 80-120 5
25
Ethene
0.310
0.00300
mg/L
0.302 103 80-120 6
25
Methane
0.168
0.00100
mg/L
0.172 98 80-120 4
25
Duplicate (911-03012-DUPi)
Prepared: 12/03/2019 13:51 Analyzed: 12/03/2019 16:02
Source: CC19664-01
Spike Source %REC
RPD
Analvte
Result Flag
POL
Units
Level Result %REC Limits RPD
Limit Notes
Ethane
1.30 U
2.00
ug/L
1.30 U
25
Ethene
1.50 U
3.00
ug/L
1.50 U
25
Methane
1730
1.00
ug/L
1070 47
25 QM-02
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 81 Of 92

(� �Eo
www.encolabs.com
FLAGS/NOTES AND DEFINITIONS
B The analyte was detected in the associated method blank.
D The sample was analyzed at dilution.
J The reported value is between the laboratory method detection limit (MDL) and the laboratory method
reporting limit (MRL), adjusted for actual sample preparation data and moisture content, where applicable.
U The analyte was analyzed for but not detected to the level shown, adjusted for actual sample preparation
data and moisture content, where applicable.
E The concentration indicated for this analyte is an estimated value above the calibration range of the
instrument. This value is considered an estimate.
MRL Method Reporting Limit. The MRL is roughly equivalent to the practical quantitation limit (PQL) and is
based on the low point of the calibration curve, when applicable, sample preparation factor, dilution
factor, and, in the case of soil samples, moisture content.
PQL PQL: Practical Quantitation Limit. The PQL presented is the laboratory MRL.
N The analysis indicates the presence of an analyte for which there is presumptive evidence (85% or greater
confidence) to make a "tentative identification".
P Greater than 25% concentration difference was observed between the primary and secondary GC column.
The lower concentration is reported.
[CALC] Calculated analyte - MDL/MRL reported to the highest reporting limit of the component analyses.
QL-02 The associated laboratory control sample exhibited high bias; since the result is ND, there is no impact.
QM-02 The RPD and/or percent recovery for this QC spike sample cannot be accurately calculated due to the high
concentration of analyte present in the sample.
QM-07 The spike recovery was outside acceptance limits for the MS and/or MSD. The batch was accepted based
on acceptable LCS recovery.
QM-08 Post -digestion spike did not meet method requirements due to confirmed matrix effects (dilution test).
QM-11 Precision between duplicate matrix spikes of the same sample was outside acceptance limits.
QM-12 Precision between duplicate samples was outside acceptance limits.
QV-01 The associated continuing calibration verification standard exhibited high bias; since the result is ND, there
is no impact.
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 82 of 92

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Sample Preservation Verification
ENCO Cary
ENCO
Work Order: CC18642 Project! Moore County LF
Client: Golder Associates, Inc. (GO007) Project #: 0739615018.100
Logged In: 20-Nov-19 13:58 o� Logged By: Rachel Ann onishj
Preservation Check Performed By: �'k DatelTime: .6 I l 01`�` '
CC18642-01
Cont
Type
Pres (pH)
Requirement
pH Checked/
fn Control
pH Adjusted Datemme
Adiusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
Y '/ N I NA
Y! N NA
F
250mLP+HNO3
<2
LY)/ N I NA
Y N I NA
G
250mLP+ZnAc+NaOH
>9
Y / N / NA
Y / N NA
CC 18642-02
Cant
Type
Pres (pH)
Requirement
pH Checked /
Jn Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
E
250mLP+H2504
<2
Y/ N I NA
Y / NA
F
250mLP+HNO3
<2
Y / N / NA
Y / 1 NA
G
250mLP+ZnAc+NaOH
>9
Y N/ NA
Y I N I NA
CC18642-03
Cont
Type
Pres (pH)
Requirement
pH Checked 1
..In Control
pH Adjusted DatelTime
Adjusted
Reagent Used/Comments
H
250mLP4­l2SO4
<2
Y N/ NA
Y tj 1 NA
I
250mLP+HNO3
<2
Y N / NA
Y /
! NA
J
250mLP+HNO3
<2
Y/ N/ NA
Y 1(1;TY
NA
K
25pmLP+ZnAc+NaOH
>9
Y N / NA
Y / ! NA
L
250mLP+ZnAc+NaOH
>9
N I NA
Y I N I NA
CC18642-04
Cont
Type
Pres (pH)
pH Checked /
pH Adjusted Date)Time
Reagent Used/Comments
Requirement
In Control
Adjusted
E
250mLP+H2SO4
<2
Y/ N I NA
Y li N NA
F
250mLP+HNO3
<2
Y I N/ NA
Y/fNA
G
254mLP+ZnAc+NaOH
>9
Y I N I NA
Y! N NA
CC 18642-05
Cont
Type
Pres (pH)
Requirement
pH Checked I
In Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
,^
250mLP+H2SO4
<2
Y ! N / NA
Y 1 .N NA
F
250mLP+HNO3
<2
Y/ N/ NA
Y 1 N/ NA
G
250mLP+ZnAc+NaOH
>9
Y 1 N/ NA
Y/ N NA
Page 85 of 92
C:lelmntlPrintlwko_PreservationCheck.rpt .ge o

Sample Preservation Verification
ENCO Cary
Work Order: CC18642 Project: Moore County LF
Client: Golder Associates, Inc. (GO007) Project#: 0739615018.100
Logged In: 20-Nov-19 13:58 Logged By: Rachel Ann 44Yonis 1
Preservation Check Performed By: Date/Time: Il �' l q
CC18642-06
Cont
Type
Pres (pH)
Requirement
pH Checked /
In Control.
pH Adjusted DateMme
Adjusted
Reagent Used/Comments
E
25OmLP+H2SO4
<2
N I NA
Y I / NA
F
250mLP+HNO3
<2
Y N I NA
Y /0
NA
G
250mLP+ZnAc+NaOH
1 9
Y N/ NA
Y
N I NA
Rea ent Name 1D
1
2
Reaclent Name ID
3
4
Rea ent Name ID
5
6
pH Strip ID:
PH Strips C9J0537 Page 86 of 92
C:lelmntlPrintlwko_PreservationCheck.rpt 2

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Page 88 of 92

Sample Preservation Verification
ENCO Cary
Work Order: CC19657
Client: Golder Associates, Inc. iG00 7)
Logged ln: 22-Nov-19 08:36
Preservation Check Performed By:
CC19667-01
Project:
Project #;
Logged By:
EJ�ICO
Moore County LF
0739615018,100
John C King pp !
DatelTime: f f '22-,- 1 ILeO
Cont
Type
Pres (pH)
Requirement
pH Checked(
In Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
I N/ NA
Y I 1 NA
F
250mLP+HNO3
<2
Y I N I NA
Y I 1 NA
G
250mLP+ZnAc+NaOH
>9
I N I NA
Y I I NA
CC19657-02
Cant
Type
Pres (pH)
Requirement
pH Checked /
In Control
pH Adjusted Date/fjme
Adjusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
� / N 1 NA
Y /(E)1 NA
F
250mLP+HNO3
<2
I N I NA
Y I 1 NA
G
250mLP+ZnAc+NaOH
79
Y/ N 1 NA
Y/ 1 NA
CC19657-03
Coni
Type
YP
Pres (pH)
Requirement
pH Checked /
In Control
Date/Time
pH Adjusted Adjusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
Y I N I NA
Y /Lf4)/ NA
F
250mLP+HNO3
<2
Y/ N I NA
Y (3/ NA
G
250mLP+ZnAc+NaOH
>9
Y / N 1 NA
Y /(t / NA
CC19657-04
Cant
Type
yP
Pres (pH)
Requirement
pH Checked /
In Control
Date/Time
pH Adjusted Adjusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
Y'/ N I NA
Y /0 1 NA
F
250mLP+HNO3
<2
I N 1 NA
Y / NA
G
25DmLP+ZnAc+NaOH
>9
I N I NA
Y/ I NA
Rea ent Name ID
1
2
pH Strip I D:
Rea ent Name ID
3
4
Reaclent Name ID
5
6
C:\ELMNT\Print\wko—PreservationCheck.rpt
Page 89 of 92
Page 1 of 1

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Sample Preservation Verification
ENCO Cary
Work Order: CC19664
Client: Golder Associates, Inc. (G0007)
Logged In: 22-Nov-19 08:46
Preservation Check Performed By:
CC 19664-01
I
ENCO
Project: Moore County LF
Project #: 0739615018.100
Logged By: John C King
Date/Time: M Z-r /006
Cont
Type
Pres (pH)
Requirement
pH Checked /
In Control
pH Adjusted Date/Time
Adjusted
Reagent Used/Comments
E
250mLP+H2SO4
<2
Y N / NA
Y /U/ NA
F
250mLP+HNO3
<2
(9/ N / NA
Y O / NA
G
250mLP+ZnAc+NaOH
>9
uy / N / NA
Y / & / NA
CC19664-02
Cont
Type
Pres (pH)
Requirement
pH Checked /
In Control
pH Adjusted Dateffime
Adjusted
Reagent Used/Comments
E
250rnLP+H2SO4
<2
Yjl N I NA
Y / / NA
F
250mLP+HNO3
<2
1' / N ! NA
Y / / NA
G
250mLP+ZnAc+NaOH
>9l
N 1 NA
Y / �/ NA
Rea ent Name ID
1
2
PH Strip ID. Og)-05_�
Rea ent Name ID
3
4
Rea ent Name 1 D
5
6
C:IELMNTIPrintlwko_Preservation Check. rpt
Page 92 of 92
Page 1 of

WORK ORDER Printed: 12/18/2019 2:09:08PM
CC18642
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore County LF Project Number: 0739615018.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By:
Timothy J. Parker
Date Received: 20-Nov-19 13:30
Logged In By:
Rachel Ann Yonish
Date Logged In: 20-Nov-19 13:58
Work Order Comments:
C-1844 received at 0.6°C
Containers Intact
Y
Containers Properly Preserved
Y
Proper Containers Received Y All Samples in PreLog Received
Y
COC/Labels Agree
Y
Custody Seals Intact
Y
Volatile Containers Preserved
Y
Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl
N
Received On Ice
Y
Temnerature Corrected
Y
Default Cooler
Containers Intact
Y
Containers Properly Preserved
Y
Proper Containers Received Y All Samples in PreLog Received
Y
COC/Labels Agree
Y
Custody Seals Intact
Y
Volatile Containers Preserved
Y
Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl
N
Received On Ice
Y
Temoeratme Corrected
Y
Default Cooler
Containers Intact
Y
Containers Properly Preserved
Y
Proper Containers Received Y All Samples in PreLog Received
Y
COC/Labels Agree
Y
Custody Seals Intact
Y
Volatile Containers Preserved
Y
Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl
N
Received On Ice
Y
Temnerature Corrected
Y
Reviewed By Date I Page 1 of 1

WORK ORDER Printed: 12/18/2019 2:08:50PM
CC19657
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore County LF Project Number: 19127453.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: John C King Date Received: 22-Nov-19 07:00
Logged In By: John C King Date Logged In: 22-Nov-19 08:36
Work Order Comments:
C-1844 received at 1.1°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temoeratme Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Reviewed By
Date
Page 1 of 1

WORK ORDER Printed: 12/18/2019 2:08:34PM
CC19664
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore County LF Project Number: 19127453.100
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: John C King Date Received: 22-Nov-19 07:00
Logged In By: John C King Date Logged In: 22-Nov-19 08:46
Work Order Comments:
C-1844 received at 0.5°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temoeratme Corrected Y
Default Cooler
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received Y COC/Labels Agree Y
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice Y
Temnerature Corrected Y
Reviewed By
Date
Page 1 of 1

GOLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY CONTROL
LABORATORY DATA REVIEW
Page 1 of 4
Project Name: Moore County Landfill
Project Reference Number: 19127453.100
Sampling Event Date: November 19-21,2019
Review Date: December 27,2019
Report #: CC18642,CC19657,CC19664
Signature:
QA/QC Sign Off:
Date:
Date:
GOLDER
Initials: NTT
Person(s) performing the review are to initial each item on this form as acknowledgement
of data acceptance, or as acknowledgement of a review issue. In the case of the latter, a
brief explanation should follow the applicable item.
Golder Associates Inc. has reviewed the laboratory certificates of analysis, chain -of -custody form,
and laboratory provided sample group quality assurance and quality control data for the above
referenced sample group to identify potential bias or inaccuracy, in general accordance with the
following United States Environmental Protection Agency documents:
• Region III Modifications to Functional Guidelines for Organic Data Review Multi -Media,
Multi -Concentration, September 1994;
• Region III Modifications to the Laboratory Data Validation Functional Guidelines for
Evaluating Inorganic Analyses, April 1993; and
• Laboratory Data Validation Functional Guidelines for Evaluating Inorganic Analyses, July
1998.
COMPLIANCE ANALYTE LIST(S) (check all that apply)
NC Closed Facility/C & D List
X NC Appendix I VOAs and NC RCRA Metals
NC Appendix I + Detects
X MNA Parameters
X NC Appendix II + C&D + MNA
NC Subtitle D Leachate List
Other:
1.0 CHAIN OF CUSTODY (COC) REVIEW
NTT COC was properly signed by all parties.
NTT Correct project name and number are on the form.
Incorrect project number, correct project number should be 19127453.100
NTT Sample receipt condition at laboratory was acceptable.
NTT Each sample and blank submitted for analysis appears in the report.

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 2 of 4
2.0 SAMPLE HOLDING TIMES
NTT Holding times for extraction and/or analysis were met for each analytical
Method (see below for reference).
GOLDER
Review Criteria
Method
Analytes
Holding Time
SW-846 Method 8260 and 8011
VOCs
14 days
SW-846 Methods 8270, 8080,
8081, 8082, and 8151
SVOCs, PCBs,
pesticides and
herbicides
7 days for extraction, 40 days
from extraction for analysis
SW-846 Methods 6000 and 7000
Series
Metals except mercury
6 months (no temperature
requirements)
SW-846 Method 7470
Mercury
28 days
SM18 4500-S2 D
Sulfide
7 days
SW-846 Method 9010
Cyanide
14 days
EPA Method 300
Nitrate/Sulfate
48 hours/28 days
EPA Method 405.1
BOD
48 hours
EPA Method 410.4
COD
28 days
EPA Method 365.4
Phosphorous
28 days
3.0 LABORATORY QUALITY CONTROL REVIEW
NTT Laboratory analyzed at least one internal blank for each method, where applicable.
NTT Laboratory blank is interference -free.
NTT Surrogate recoveries are provided for each analytical method, where applicable.
NTT Surrogate recoveries for each method are within the acceptable limits (i.e., at least
50% of the surrogates were within range).
NTT MS/MSD/LCS data results are provided for each analytical method.
NTT MS/MSD/LCS recoveries for each method are within the acceptable limits (i.e., at least
1 of the 3 were within range).
The spike recovery of 1,4-Dioxane was outside of control limits for the 8260D SIM ID MS and
MSD samples. The QC batch was approved based on acceptable LCS recovery of this
analyte. The spike recovery of Trichloroethene was outside of control limits for the 8260D
LCS sample, indicating a possible high bias; however, this analyte was not detected in the
associated sample, reducing the impact of the deviation. The Continuing Calibration
Verification sample (CCV) exhibited a high bias for 1,1-Dichloroethene, Carbon disulfide,
and Trichlorofluoromethane; however, these analytes were not detected in the associated
samples.
Precision between duplicate analyses of Methane exceeded acceptance criteria for the RSK-
175 analysis. The QC batch was approved based on acceptable LCS recovery of this
analyte.
j- The spike recoveries of Iron and Mercury were outside of control limits for the MS, MSD,

OLDER ASSOCIATES NC, INC.
GOLDER
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 3 of 4
and/or Post spike samples. The QC batches were approved based on acceptable LCS
recovery of these elements.
➢ The spike recoveries of Alkalinity, Chloride, Nitrate/Nitrite (NOx), Nitrite, Sulfate, Sulfide, and
TOC were outside of control limits for the MS and/or MSD samples, and precision between
duplicate TDS analyses exceeded acceptance criteria. The QC batches were approved
based on acceptable LCS recovery of these analytes.
4.0 ANALYTE LISTS/METHODS
NTT The proper number of constituents are present for each analyte list as identified above
(including detects where applicable).
NTT Proper EPA SW-846 analytical methods were used for analysis.
Notes:
5.0 DATA REPORTING
NTT All analytical reporting associated with the event was performed by the contracted lab
NTT Trip, field and/or equipment, and laboratory blank results have all been reported. All
detects for blanks are listed below by constituent. All laboratory method blanks, if any,
have been `flagged' with a `B' where detected in other samples as appropriate and a
laboratory narrative was provided. If the sample was flagged by the laboratory and is
not within 5X of the concentration in the blank (or 1 OX for commonly detected laboratory
contaminants -acetone, methylene chloride and phthalates), list below with explanation
if flags should be removed. If flags need to be added for samples, also list below.
NTT It is clear from the laboratory report that samples have or have not been diluted during
analysis, and if the samples have been diluted, the result is reported as a multiple of
the dilution (e.g., a sample diluted 1 Ox resulting in an analytical detection of 1.0 should
be reported as 10). Those that have been diluted are listed below with the dilution
factor.
➢ Total Alkalinity as CaCO3: 2x in MW-2, MW-14, & MW-6
➢ Total Alkalinity as CaCO3: 5x in MW-11SR
➢ Total Alkalinity as CaCO3: 10x in MW-9
➢ Thallium: 2x in MW-4, MW-5, MW-11SR, MW-14, & MW-17S
➢ Antimony: 2x in MW-4, MW-5, MW-11SR, MW-14, & MW-17S
➢ Methane: 10x in MW-6, MW-9, MW-14, & MW-15SR
➢ Sulfate as SO4: 2x in MW-17S
➢ Nitrate: 5x in MW-4
➢ Methane: 5x in MW-7
➢ Chloride: 2x in MW-9
NTT The report provides the reporting limit for each constituent.
NTT The results were reported at or below their proper reporting limits. Those that are not
reported correctly are listed below (by constituent) with the proper reporting limit listed
beside them. State if the reporting limit error is due to dilutions.
NTT No inorganic or organic constituents were reported above their respective NC 2L

OLDER ASSOCIATES NC, INC.
GOLDER
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 4 of 4
Drinking Water Standards or IMAC standards in wells, surface points, or
field/equipment/trip blanks.
➢ Benzene (NC2L = 1 ug/L)
• MWA1SIR @4.8 ug/L
• MW-6 @ 3.7 ug/L
• MW-14 @ 15 ug/L
• MW-7 @ 1.6 ug/L
• MW-9 @ 3.8 ug/L
• MWA 1SR @ 2.8 ug/L
➢ Iron (NC2L = 300 ug/L)
• MW-14 @ 2.3 ug/L
• MW-4 @ 15500 ug/L
• MW-15R @5.7 ug/L
MW-11SR @ 101000 ug/L
• MW-14 @ 152000 ug/L
➢ Vinyl Chloride (NC2L = 0.03 ug/L)
MW-17S @ 38400 ug/L
• MW-6 @ 1.3 ug/L
• MW-7 @ 1.3ug/L
➢ Manganese (NC2L = 50 ug/L)
• MWA1SR @ 2.0 ug/L
MW-4 @ 131 ug/L
• MW-14 @ 2.5 ug/L
0 MW-11SR @ 248 ug/L
• MW-15 @ 0.74 ug/L (J)
0 MW-14 @ 212 ug/L
• MW-17S @ 117 ug/L
➢ 1,4 Dioxane (NC2L = 3.0 ug/L)
• MW-2 @ 14 ug/L
➢ Vanadium (NC 2L IMAC = 0.3 ug/L)
• MW-7 @ 10 ug/L
MW-4 @ 1.21 ug/L (J)
• MW-9 @ 22 ug/L
NTT No quantifiable inorganic or organic constituents were detected in a well or surface
water point at concentrations outside of their historical range (more than 5X previous
concentrations or first-time detections).
1s' time detection of 1,4-dioxane on MW-1(2.3 ug/L), MW-3 (1.1 ug/L), and MW-17S (1.6
ug/L)
1s' time detection of Toluene in MW-15R (0.43 ug/L (J))
1s'time detection of Methylene Chloride in MW-7 (0.64 ug/L (J))
1s' time detection of 1,1-Dichloroethane in MW-15R (0.93 ug/L (J))
1s' time detection of 1,2-Dichloroebenzene in MW-7 (0.49 ug/L (J))
1st time detection of Acetone in MW-15R (190 ug/L)
1ST time detection of Iron in MW-17S (38400 ug/L)
NTT Other report issues/Communications with laboratory/etc.:

2�SQ p[CgF� ENCO Laboratories
9g
Accurate, Timely. Respousive. luuavatxve.
102-A Woodwinds Industrial Court
Cary NC, 27511
Phone: [phone] FAX: [phone]
Friday, January 17, 2020
Golder Associates, Inc. (GO007)
Attn: Ben Draper
5B Oak Branch Drive
Greensboro, NC 27407
RE: Laboratory Results for
Project Number: 19127453, Project Name/Desc: Moore County LF
ENCO Workorder(s): CD00604
Dear Ben Draper,
Enclosed is a copy of your laboratory report for test samples received by our laboratory on
Thursday, January 9, 2020.
Unless otherwise noted in an attached project narrative, all samples were received in
acceptable condition and processed in accordance with the referenced methods/procedures.
Results for these procedures apply only to the samples as submitted.
The analytical results contained in this report are in compliance with NELAC standards, except
as noted in the project narrative if applicable. This report shall not be reproduced except in
full, without the written approval of the Laboratory.
This report contains only those analyses performed by Environmental Conservation
Laboratories. Unless otherwise noted, all analyses were performed at ENCO Cary. Data from
outside organizations will be reported under separate cover.
If you have any questions or require further information, please do not hesitate to contact me.
Sincerely,
Meghan K Shea
Project Manager
Enclosure(s)
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 1 of

PROJECT NARRATIVE
Date: 17 January
Client: Golder Associates, Inc. (G0007)
Project: Moore County LF
Lab ID: CDO0604
Overview
(� �Eo
www.encolabs.com
Environmental Conservation Laboratories, Inc. (ENCO) analyzed all submitted samples in accordance with the methods
referenced in the laboratory report. Any particular difficulties encountered during sample handling by ENCO are discussed in
the QC Remarks section below.
Quality Control Samples
No Comments
Quality Control Remarks
No Comments
Other Comments
All samples received under this work order arrived in acceptable conditions. The samples were not checked for residual
chlorine, as it is not required.
The analytical data presented in this report are consistent with the methods as referenced in the analytical report. Any
exceptions or deviations are noted in the QC remarks section of this narrative or in the Flags/Notes and Definitions section of
the report.
Released By:
Environmental Conservation Laboratories, Inc.
Meghan Shea
Project Manager
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 2 of 8

(� �Eo
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SAMPLE SUMMARY/LABORATORY CHRONICLE
Client ID: 6301-MW15R Lab ID: CD00604-01 Sampled: 01/08/20 12:55 Received: 01/09/20 12:20
Parameter Preparation Hold Date/Time(s)
EPA 8260D EPA 503013_MS O1/22/20
Prep Date/Time(s) Analysis Date/Time(s)
O1/13/20 15:11 01/14/20 01:28
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 3 Of S

(� �Eo
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SAMPLE DETECTION SUMMARY
Client ID: 6301-MW15R
Lab ID:
CDO0604-01
Anala
Results Flag MDL
POLL
Units Method Notes
Benzene
1.5 0.57
1.0
ug/L EPA 8260D
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 4 Of 8

(� �Eo
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ANALYTICAL RESULTS
Description: 6301-MW15R Lab Sample ID:CDO0604-01 Received: 01/09/20 12:20
Matrix: Ground Water Sampled:01/08/20 12:55 Work Order: CDO0604
Project: Moore County LF Sampled By: Nicolas Tejada-Torres
Volatile Organic Compounds by GCMS
^ - ENCO Cary certified analyte [NC 591]
Analyte MAS Numberl
Results
Flag
Units
DF
MDL P L
Batch
Method
Analyzed
By Notes
Benzene [71-43-2]A
1.5
ug/L
1
0.57 1.0
OA13041
EPA 8260D
01/14/20 01:28
REF
Surrogates
Results
DF
Soike Lv/
% Rec
% Rec Limits
Batch
Method
Ana/vzed
ffy Notes
4-Bromofluorobenzene
52
1
50.0
103 %
53-136
OA13041
EPA 8260D
01114120 01:28
REF
Dlbromofluoromethane
54
1
50.0
109 %
67-129
OA13041
EPA 6260D
01114120 01:28
REF
Toluene-&
48
1
50.0
97 %
59-134
OA13041
EPA 6260D
01114120 01:28
REF
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Pager) Of S

0 F. Nk"q 09)
www.encolabs.com
QUALITY CONTROL DATA
Volatile Organic Compounds by GCMS - Quality Control
Batch OA13O41 - EPA 5O3OB MS
Blank (OA13041-BLK3)
Prepared: 01/13/2020 15:11 Analyzed: O1/13/2020 18:39
Spike
Source
%REC
RPD
Analvte
Result
Flao
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Benzene
0.57
U
1.0
ug/L
4-8romofluorobenzene
50
u9/L
50.0
100
53-136
Dibromofluoromethane
52
u9/L
50.0
104
67-129
Toluene-&
48
u9/L
50.0
96
59-134
LCS (OA13041-BS1)
Prepared: 01/13/2020 15:11 Analyzed: 01/13/2020 16:34
Spike
Source
%REC
RPD
Analvte
Result
Flao
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Benzene
18
1.0
ug/L
20.0
91
80-134
Toluene
18
1.0
ug/L
20.0
90
71-120
4-8romofluorobenzene
52
u9/L
50.0
105
53-136
Dibromofluoromethane
51
u9/L
50.0
101
67-129
Toluene-d8
48
u9/L
50.0
96
59-134
Matrix Spike (OA13041-MS1)
Prepared: 01/13/2020 15:11 Analyzed: 01/13/2020 17:05
Source: CD00596-09
Spike
Source
%REC
RPD
Analvte
Result
Flaa
POL
Units
Level
Result
%REC
Limi RPD
Lima
Notes
Benzene
20
1.0
ug/L
20.0
0.57 U
102
80-134
Toluene
20
1.0
ug/L
20.0
0.57 U
100
71-120
4-8romofluorobenzene
51
u9/L
50.0
102
53-136
Dibromofluoromethane
50
u9/L
50.0
99
67-129
Toluene-&
46
u9/L
50.0
96
59-134
Matrix Spike Dup (OA13041-MSD1)
Prepared: 01/13/2020 15:11 Analyzed: O1/13/2020 17:37
Source: CD00596-09
Spike
Source
%REC
RPD
Analvte
Result
Flao
POL
Units
Level
Result
%REC
Limits RPD
Limit
Notes
Benzene
18
1.0
ug/L
20.0
0.57 U
92
80-134 9
17
Toluene
18
1.0
ug/L
20.0
0.57 U
91
71-120 9
17
4-8romofluorobenzene
52
u9/L
50.0
103
53-136
Dibromofluoromethane
51
u9/L
50.0
101
67-129
Toluene-d8
47
u9/L
50.0
94
59-134
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 6 Of 8

(� �Eo
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FLAGS/NOTES AND DEFINITIONS
B The analyte was detected in the associated method blank.
D The sample was analyzed at dilution.
J The reported value is between the laboratory method detection limit (MDL) and the laboratory method
reporting limit (MRL), adjusted for actual sample preparation data and moisture content, where applicable.
U The analyte was analyzed for but not detected to the level shown, adjusted for actual sample preparation
data and moisture content, where applicable.
E The concentration indicated for this analyte is an estimated value above the calibration range of the
instrument. This value is considered an estimate.
MRL Method Reporting Limit. The MRL is roughly equivalent to the practical quantitation limit (PQL) and is
based on the low point of the calibration curve, when applicable, sample preparation factor, dilution
factor, and, in the case of soil samples, moisture content.
PQL PQL: Practical Quantitation Limit. The PQL presented is the laboratory MRL.
N The analysis indicates the presence of an analyte for which there is presumptive evidence (85% or greater
confidence) to make a "tentative identification".
P Greater than 25% concentration difference was observed between the primary and secondary GC column.
The lower concentration is reported.
[CALC] Calculated analyte - MDL/MRL reported to the highest reporting limit of the component analyses.
FINAL This report relates only to the sample as received by the laboratory, and may only be reproduced in full. I Page 7 of 8

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GOLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY CONTROL
LABORATORY DATA REVIEW
Page 1 of 3
Project Name: Moore County Landfill
Project Reference Number: 19127453.100
Sampling Event Date: January 08, 2020
Review Date: January 20, 2020
Report #: CDO0604
Signature:
QA/QC Sign Off:
Date:
Date:
GOLDER
Initials: NTT
Person(s) performing the review are to initial each item on this form as acknowledgement
of data acceptance, or as acknowledgement of a review issue. In the case of the latter, a
brief explanation should follow the applicable item.
Golder Associates Inc. has reviewed the laboratory certificates of analysis, chain -of -custody form,
and laboratory provided sample group quality assurance and quality control data for the above
referenced sample group to identify potential bias or inaccuracy, in general accordance with the
following United States Environmental Protection Agency documents:
• Region III Modifications to Functional Guidelines for Organic Data Review Multi -Media,
Multi -Concentration, September 1994;
• Region III Modifications to the Laboratory Data Validation Functional Guidelines for
Evaluating Inorganic Analyses, April 1993; and
• Laboratory Data Validation Functional Guidelines for Evaluating Inorganic Analyses, July
1998.
COMPLIANCE ANALYTE LIST(S) (check all that apply)
NC Closed Facility/C & D List
NC Appendix I VOAs and NC RCRA Metals
NC Appendix I + Detects
MNA Parameters
NC Appendix II + C&D + MNA
NC Subtitle D Leachate List
Other: Benzene
1.0 CHAIN OF CUSTODY (COC) REVIEW
NTT COC was properly signed by all parties.
NTT Correct project name and number are on the form.
NTT Sample receipt condition at laboratory was acceptable.
NTT Each sample and blank submitted for analysis appears in the report.

OLDER ASSOCIATES NC, INC.
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 2 of 3
2.0 SAMPLE HOLDING TIMES
NTT Holding times for extraction and/or analysis were met for each analytical
Method (see below for reference).
GOLDER
Review Criteria
Method
Anal tes
HoldingTime
SW-846 Method 8260 and 8011
VOCs
14 days
SW-846 Methods 8270, 8080,
8081, 8082, and 8151
SVOCs, PCBs,
pesticides and
herbicides
7 days for extraction, 40 days
from extraction for analysis
SW-846 Methods 6000 and 7000
Series
Metals except mercury
6 months (no temperature
requirements)
SW-846 Method 7470
Mercury
28 days
SM18 4500-S2 D
Sulfide
7 days
SW-846 Method 9010
Cyanide
14 days
EPA Method 300
Nitrate/Sulfate
48 hours/28 days
EPA Method 405.1
BOD
48 hours
EPA Method 410.4
COD
28 days
EPA Method 365.4
Phosphorous
28 days
3.0 LABORATORY QUALITY CONTROL REVIEW
NTT Laboratory analyzed at least one internal blank for each method, where applicable.
NTT Laboratory blank is interference -free.
NTT Surrogate recoveries are provided for each analytical method, where applicable.
NTT Surrogate recoveries for each method are within the acceptable limits (i.e., at least
50% of the surrogates were within range).
NTT MS/MSD/LCS data results are provided for each analytical method.
NTT MS/MSD/LCS recoveries for each method are within the acceptable limits (i.e., at least
1 of the 3 were within range).
4.0 ANALYTE LISTS/METHODS
NTT The proper number of constituents are present for each analyte list as identified above
(including detects where applicable).
NTT Proper EPA SW-846 analytical methods were used for analysis.
Notes:
5.0 DATA REPORTING
NTT All analytical reporting associated with the event was performed by the contracted lab.

OLDER ASSOCIATES NC, INC.
GOLDER
QUALITY ASSURANCE & QUALITY
CONTROLLABORATORY DATA REVIEW
Page 3 of 3
NTT Trip, field and/or equipment, and laboratory blank results have all been reported. All
detects for blanks are listed below by constituent. All laboratory method blanks, if any,
have been `flagged' with a `B' where detected in other samples as appropriate and a
laboratory narrative was provided. If the sample was flagged by the laboratory and is
not within 5X of the concentration in the blank (or 1 OX for commonly detected laboratory
contaminants -acetone, methylene chloride and phthalates), list below with explanation
if flags should be removed. If flags need to be added for samples, also list below.
NTT It is clear from the laboratory report that samples have or have not been diluted during
analysis, and if the samples have been diluted, the result is reported as a multiple of
the dilution (e.g., a sample diluted 10x resulting in an analytical detection of 1.0 should
be reported as 10). Those that have been diluted are listed below with the dilution
factor.
NTT The report provides the reporting limit for each constituent.
NTT The results were reported at or below their proper reporting limits. Those that are not
reported correctly are listed below (by constituent) with the proper reporting limit listed
beside them. State if the reporting limit error is due to dilutions.
NTT No inorganic or organic constituents were reported above their respective NC 2L
Drinking Water Standards or IMAC standards in wells, surface points, or
field/equipment/trip blanks.
➢ Benzene (NC2L = 1 un/L)
• MW-15R @1.5 ug/L
NTT No quantifiable inorganic or organic constituents were detected in a well or surface
water point at concentrations outside of their historical range (more than 5X previous
concentrations or first-time detections).
NTT Other report issues/Communications with laboratory/etc.:

WORK ORDER Printed: 1/17/2020 10:19:10AM
CDO0604
ENCO Cary
Sample Receipt Conditions
Client: Golder Associates, Inc. (G0007) Lab Project Mgr: Meghan K Shea
Project: Moore County LF Project Number: 19127453
PO #:
Report To:
Invoice To:
Golder Associates, Inc. (G0007)
Golder Associates, Inc. (G0007)
Ben Draper
Accounts Payable
5B Oak Branch Drive
5B Oak Branch Drive
Greensboro, NC 27407
Greensboro, NC 27407
Phone: [phone]
Phone :[phone]
Fax: [phone]
Fax:[phone]
Received By: Timothy J. Parker
Logged In By: Rachel Ann Yonish
Date Received: 09-Jan-20 12:20
Date Logged In: 09-Jan-20 13:26
Work Order Comments:
Default Cooler received at 1.6°C
Containers Intact Y Containers Properly Preserved Y Proper Containers Received Y All Samples in PreLog Received N COC/Labels Agree
Custody Seals Intact Y Volatile Containers Preserved Y Volatile Containers Headspace Free Y Aqueous Samples Checked for Residual Cl N Received On Ice
Temnerature Corrected Y
Y
Y
Reviewed By
Date
Page 1 of 1

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