MO-2805_3679_CA_MRP_20200207_sealed

SUBSEQUENT MONITORING REPORT
Burcham Property (Incident # 3679)
1630 Armstrong Ford Road
Belmont, Gaston County, North Carolina
February 7, 2020
Terracon Project No. 71149638A
Prepared for:
North Carolina Department of Environmental Quality
Division of Waste Management
Raleigh, North Carolina
Prepared by:
Terracon Consultants, Inc.
Charlotte, North Carolina
Terracon Consultants, Inc. 2701 Westport Road Charlotte, NC 28208
P 704-509-1777 F 704-509-1888 terracon.com
February 7, 2020
Mr. Scott Ryals
North Carolina Department of Environmental Quality
Division of Waste Management
1646 Mail Service Center
Raleigh, North Carolina 27699-1646
Email:[e-mail]
Re: Subsequent Monitoring Report
Burcham Property
1630 Armstrong Ford Road
Belmont, Gaston County, North Carolina
UST Incident Number: 3679
Terracon Project No. 71149638A
Dear Mr. Ryals:
Terracon Consultants, Inc. (Terracon) is pleased to submit this Subsequent Monitoring Report for the
above referenced property. This report has been prepared in general accordance with North
Carolina Department of Environmental Quality (NCDEQ), UST Section Guidelines for Assessment
and Corrective Action for UST Releases,dated July 15, 2008, revised December 2013, Task
Authorization No. 04, approved on October 3, 2019 and Task Authorization No. 05, approved on
November 27, 2019.
If you have any questions regarding this report or the assessment activities, please contact us at
704-509-1777.
Sincerely,
Terracon Consultants, Inc.
McKhenzy A. Welch, CPESC Christopher L. Corbitt, PG
Staff Scientist Senior Geologist
Enclosures
Table of Contents
A.SITE INFORMATION................................................................................................ 1
B.EXECUTIVE SUMMARY .......................................................................................... 2
C.SITE HISTORY AND CHARACTERIZATION .......................................................... 4
C.1 Site Setting ............................................................................................................................................. 4
C.2 Release Summary .................................................................................................................................. 4
C.3 Previous Investigations ........................................................................................................................ 4
C.4 Water Supply Wells ............................................................................................................................... 7
C.5 Surface Water......................................................................................................................................... 7
C.6 Land Use Information............................................................................................................................ 8
D.ASSESSMENT INFORMATION ............................................................................ 8
D.1 Site Geology and Hydrogeology ............................................................................................................... 8
D.2 Sampling Activities ................................................................................................................................ 9D.2.1 Free Product Evaluation ...................................................................................................................... 9
D.2.2 Groundwater Sampling Activities ........................................................................................................ 9
D.2.3 Analytical Results ................................................................................................................................ 9
E.CONCLUSIONS AND RECOMMENDATIONS ................................................... 10
FIGURES
Figure 1: Site Location Map
Figure 2: Site and Surrounding Properties Map
Figure 3: Receptor Survey Map
Figure 4: Groundwater Elevations Map
Figure 5: Groundwater Analytical Results
TABLES
Table 1: Water Supply Well Information
Table 2: Summary of Groundwater Analytical Results
Table 3: Monitoring Well Construction Information and Historical
Groundwater Elevations
APPENDIX
Appendix A: Laboratory Analytical Results and Chain of Custody Forms
Appendix B: Field Notes
Appendix C: Photographs
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 1
SUBSEQUENT MONITORING REPORT
A. SITE INFORMATION
Date of Report:February 7, 2020
NCDEQ Incident No:3679
Facility ID:0-006137
Site Name:Burcham Property
Site Location:1630 Armstrong Ford Road
Belmont, North Carolina 28012
Latitude:N 35o 12’ 31.45”
Longitude:W 81o 04’ 19.53”
UST Owner/Operator:Unknown
Current Property Owner: Ms. Beverly Pitman
1630 Armstrong Ford Road
Belmont, North Carolina, 28012
and
Robert and Wanda Brown
1640 Armstrong Ford Road
Belmont, North Carolina, 28012
Current Property
Occupant:Single Family Residence and Gravel Covered Driveway
Consultant:Terracon Consultants, Inc. (Contact: McKhenzy A. Welch)
2701 Westport Road
Charlotte, North Carolina 28208
[phone]
Laboratory:Pace Analytical (NCDEQ No. 5342)
9800 Kincey Avenue
Huntersville, North Carolina 28028
704-875-9092
Release Information:Release Date: December 1, 1995
Estimated Quantity: Unknown
Cause of Release: Unknown
Currently Active Tanks: None
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 2
I, Christopher L. Corbitt, a Licensed Geologist for Terracon Consultants, Inc., do certify that the
information contained in this report is correct and accurate to the best of my knowledge.
Christopher L. Corbitt, L.G.
NC License No. 1015
Terracon Consultants, Inc. is licensed to practice geology/engineering in North Carolina. The
certification number of the corporation is F-0869.
B. EXECUTIVE SUMMARY
The Burcham Property site is comprised of two adjoining parcels (1630 and 1640 Armstrong Ford
Road) totaling approximately 1.48 acres that are occupied by an approximate 784 square foot
residence and an associated gravel covered driveway.
Terracon mobilized to the site on December 30, 2019 to evaluate current site conditions by collecting
groundwater samples from monitoring wells MW-1, MW-4 and DW-1 and water supply wells WSW-1
and WSW-4. Initially, Terracon gauged the groundwater levels in the monitoring wells. Depth to
groundwater ranged from 27.24 feet below ground surface (bgs) in well MW-4 to 38.15 feet bgs in
well DW-1. Although Terracon could not determine groundwater flow direction during this sampling
event (sampled wells in general straight line), the historical flow direction at the site has been to the
east-southeast.
Prior to sampling, the monitoring wells were purged a minimum of three well volumes. The wells
were allowed to recharge a minimum of 90 percent of the original well volume before samples were
collected. Terracon also collected water samples from water supply wells WSW-1 and WSW-4
located near the source property. The supply wells were purged by allowing water to flow from a
spigot near the wellhead for a minimum of 15 minutes. Flow was reduced when the sample was
collected. Terracon was not granted access to water supply wells WSW-2, WSW-3, WSW-5, WSW-
6 and WSW-14.
The water samples were placed in laboratory-supplied glassware, labeled and stored in an ice-
packed cooler. The samples, along with chain-of-custody documentation, were delivered to Pace
Analytical Services, Inc. in Huntersville, North Carolina for analysis of volatile organic compounds
(VOCs) by EPA Method 6200B including MTBE, IPE and EDB on a standard laboratory schedule.
According to the laboratory analytical report, 1,2-dichloroethane (555 µg/L) was detected above its
Gross Contamination Level (GCL) in monitoring well MW-1. Benzene (3,860 µg/L), naphthalene (407
µg/L), ethylbenzene (660 µg/L), n-propylbenzene (115 µg/L), toluene (3,000 µg/L), 1,2,4-
trimethylbenzene (1,570 µg/L), 1,3,5-trimethylbenzene (659 µg/L), and total xylenes (5,520 µg/L)
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 3
were detected above their respective 2L groundwater standards in monitoring well MW-1. Benzene
(48 µg/L) and 1,2-dichlororethane (7.7 µg/L) were detected in monitoring well DW-1 above their
respective 2L standards. Various other petroleum constituents were detected in monitoring wells
MW-1 and DW-1 at concentrations below their respective 2L standards. Benzene (0.52 µg/L) was
also detected in water supply well WSW-1 at a concentration below its 2L standard. No constituents
of concern were detected in well MW-4 above the laboratory method detection limits (MDLs).
To attempt to reduce the constituent concentrations in wells MW-1 and DW-1, Terracon installed
RemRx™ CRP Persulfate sleeves into the two on-site monitoring wells on February 5, 2020. The
effectiveness of the sleeves will be evaluated during future sampling events.
Based on information obtained during the completion of these assessment activities, Terracon
provides the following conclusions and findings.
None of the monitoring wells contained measurable thicknesses of free product.
1,2-Dichloroethane (555 µg/L) was detected above its GCL in monitoring well MW-1.
Benzene (3,860 µg/L), naphthalene (407 µg/L), n-propylbenzene (115 µg/L), ethylbenzene (660
µg/L), toluene (3,000 µg/L), 1,2,4-trimethylbenzene (1,570 µg/L), 1,3,5-trimethylbenzene (659 µg/L),
and total xylenes (5,520 µg/L) were detected above their respective 2L groundwater standards in
monitoring well MW-1. Benzene (48 µg/L) and 1,2-dichlororethane (7.7 µg/L) were detected in
monitoring well DW-1 above their respective 2L standards.
Benzene (0.52 µg/L) was also detected in water supply well WSW-1 at a concentration below
its 2L standard.
Terracon was not granted access to water supply wells WSW-2, WSW-3, WSW-5, WSW-6 and
WSW-14.
RemRx™ CRP Persulfate sleeves were installed into on-site monitoring wells MW-1 and DW-1 on
February 5, 2020 to reduce constituent concentrations.
Historically, the groundwater flow direction at the site has been towards the east-southeast.
Constituent concentration trends in wells MW-1 and DW-1 have increased since the previous
sampling event (March 2019).
Based on the data presented in this assessment, Terracon recommends the following activities be
completed at the site.
Groundwater monitoring wells and selected off-site water supply wells should be sampled semi-
annually to evaluate the effectiveness of the RemRx remediation sleeves in the groundwater.
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 4
C. SITE HISTORY AND CHARACTERIZATION
The purpose of this report is to evaluate the current status of the groundwater quality at the Burcham
Property. Terracon completed this report to summarize the findings of assessment activities
performed on December 30, 2019 at the Burcham Property located at 1630 Armstrong Ford Road in
Belmont, Gaston County, North Carolina (Figure 1). This Subsequent Monitoring report was
prepared for the site in response to a request by NCDEQ Incident Manager, Mr. Scott Ryals with the
NCDEQ Division of Waste Management, State Lead Program.
The Subsequent Monitoring Report was prepared in general accordance with the 15A NCAC 2L.0115
regulations and the NCDEQ Underground Storage Tank (UST) Section Guidelines for Assessment
and Corrective Action for UST Releases, dated July 15, 2008, revised December 2013, under the
supervision of Mr. Christopher L. Corbitt, a North Carolina registered professional geologist (North
Carolina License No. 1015).
C.1 Site Setting
The Burcham Property site is comprised of two adjoining parcels (1630 and 1640 Armstrong Ford
Road) totaling approximately 1.48 acres occupied by an approximate 784 square foot residence and
an associated gravel covered driveway.
The adjacent properties to the north are occupied by single-family residences and wooded areas.
Adjacent properties to the east include single-family residences and a commercial business (Grady
McCuen Floors). Adjoining properties to the south and west are occupied by single-family
residences. The site and surrounding properties are depicted in Figures 1 and 2.
C.2 Release Summary
Reportedly, a 500-gallon kerosene UST was located southwest of the site at 1640 Armstrong Ford
Road. The Burcham property was likely a larger parcel in the past but has since been subdivided
into smaller parcels. There are reportedly several inactive USTs at the Grady McCuen property
located southeast of the site at 1619 Armstrong Ford Road. Additional information about the size
and contents of these USTs is unknown. A chronological summary of petroleum releases and
assessment activities at the site is included in the following section of the report.
C.3 Previous Investigations
In October 2009, Terraine Environmental (Terraine) conducted a groundwater sampling event at the
site. Based on the laboratory analytical results, benzene and 1,2-dichloroethane exceeded their
respective GCLs in wells MW-1 and MW-2. Other petroleum constituents were also detected above
the 2L groundwater standards in wells MW-1, MW-2 and DW-1. Terraine also detected benzene in a
water sample from supply well WSW-1 and 1,2-dichloroethane in well WSW-14 above their
respective 2L standards.
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 5
Based on review of a Receptor Survey and Groundwater Monitoring Report, completed by Terraine,
dated February 25, 2010, the following historical information is provided.
On December 21, 1994, S&ME Inc. (S&ME) attempted to locate an on-site kerosene UST
through excavation and soil boring activities; however, no evidence of the UST was identified
and analytical results from soil samples did not indicate the presence of petroleum
contaminants.
A Limited Site Assessment (LSA) was performed by S&ME in March 1995. Five Type II
monitoring wells (MW-1, MW-2, MW-3, MW-5 and MW-6) and one Type III monitoring well
(DW-1) were installed near the source area. Monitoring well MW-4 was reportedly installed
by the NCDEQ in August 1988. Soil samples collected during well installation activities
indicated the presence of petroleum contaminants. The highest concentrations were
detected near the suspected location of the former kerosene UST.
A Point-of-Entry (POE) filtration system was connected to water supply well WSW-1 situated
at the residence located at 1730 Armstrong Ford Road in August 1995.
Groundwater sampling has been conducted at the site, beginning with well MW-4, since
August 1988. The remaining wells have been sampled since 1995. Certain constituent
concentrations exceeded GCLs in monitoring wells MW-1 and MW-2 while other constituents
were detected above the 2L groundwater standards in monitoring wells MW-1, MW-2 and
DW-1. Petroleum constituents were also detected in monitoring well MW-4 but at
concentrations below 2L standards.
Water supply wells WSW-1, WSW-2, WSW-3, WSW-4, WSW-5 and WSW-6 have been
sampled since 1994. Water supply well WSW-14 was sampled in 2006. Constituent
concentrations have exceeded the 2L groundwater standards in samples collected from
water supply wells WSW-1 and WSW-6.
Free product was reportedly detected in monitoring wells MW-1 and MW-2 in 2001. An
aggressive fluid vapor recovery (AFVR) event was reportedly conducted on November 1,
2002. Following the event, free product was not detected in well MW-1 but free product was
measured in monitoring well MW-2 at a thickness of 0.02 feet.
On August 20, 2010, Terraine conducted soil sampling activities near the location of the former
kerosene UST to determine if soils were a secondary source of petroleum contamination. Soil
samples were collected from two soil borings (SB-1 to the west of the basin and SB-2 to the east).
Thirteen petroleum constituents were detected at levels exceeding their respective Maximum Soil
Contaminant Concentrations (MSCCs) in boring SB-1 at a depth of 20 feet bgs and four constituents
were detected in boring SB-2 (35 feet bgs). C9-C22 Aromatics exceeded Residential MSCCs in
boring SB-1.
Crawford Environmental Services (CES) conducted a semi-annual groundwater monitoring event at
the Burcham site on April 3, 2012. The groundwater sample collected from the influent stream of
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 6
water supply well WSW-1 exceeded the 2L standard for benzene (1.9 µg/L). Analytical results from
wells WSW-3 and WSW-14 detected concentrations of chloroform and 1,2-dichloroethane,
respectively. Analytical results of the groundwater sample from well MW-1 detected petroleum
constituents in excess of the 2L standards. The benzene concentration in well MW-1 was reported
at 2,800 µg/L.
On November 29, 2012, CES conducted a second semi-annual groundwater monitoring event at the
site. Well MW-1 contained 0.53 feet of free product and was not sampled. Analytical data for the
influent sample obtained from water supply well WSW-1 indicated benzene was detected above its
2L standard. 1,2-Dichloroethane was detected at a concentration exceeding its 2L standard in the
sample collected from water supply well WSW-14.
Terracon completed a Federal/State-Lead Monitoring Report in July 2014 after a groundwater
monitoring event was conducted at the site. Groundwater monitoring well MW-1 reportedly contained
0.02 feet of free product and was not sampled. Monitoring wells MW-2 and MW-3 were not located
during the sampling event. Dissolved-phase petroleum hydrocarbons exceeded their respective 2L
standards in wells DW-1, WSW-1 and WSW-14. No petroleum constituents were identified above
the GCLs. Terracon recommended removal of free product in monitoring wells MW-1, and MW-2, if
present.
On October 15, 2015, Terracon mobilized to the site to collect groundwater samples from monitoring
wells and water supply wells. Monitoring well MW-1 contained 0.01 feet of free product and was not
sampled. Monitoring wells MW-2 and MW-3 were not located during the sampling event. Dissolved-
phase petroleum hydrocarbons exceeded their respective 2L standards in wells DW-1 and WSW-1.
No petroleum constituents were identified above the GCLs. Terracon recommended annual sampling
to monitor residual petroleum constituents, placement of an absorbent sock in well MW-1 to remove
free product (replaced quarterly), and a bio-sock to be placed in well DW-1 to reduce dissolved
phase petroleum constituents (replaced semi-annually).
Terracon mobilized to the site on May 4, 2017 to collect groundwater samples from the monitoring
wells and water supply wells. Dissolved-phase petroleum hydrocarbons exceeded their respective 2L
standards in wells MW-1, DW-1, WSW-4 and WSW-14. 1,2-Dichloroethane was detected above its
GCL in monitoring well MW-1. Terracon installed an O-Sox insert within well DW-1. Terracon
recommended slug testing at the site to obtain aquifer characteristics as an evaluation of using
surfactants and/or injectants to enhance remedial efforts and semi-annual sampling of the on-site
monitoring wells.
Terracon mobilized to the site on February 26, 2018 to evaluate the site conditions by collecting
groundwater samples from monitoring wells MW-1, MW-4, MW-5, MW-6 and DW-1. Groundwater
samples were also collected from water supply wells WSW-1, WSW-4 and WSW-14. After
completion of sampling activities, Terracon personnel installed O-sox inserts in wells MW-1 and DW-
1. None of the on-site monitoring wells contained measurable thicknesses of free product, but 1,2-
dichloroethane was detected above its GCL in monitoring well MW-1.
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 7
Terracon mobilized to the site on September 5, 2018 to collect groundwater samples for laboratory
analysis from monitoring wells MW-1 and DW-1 and water supply wells WSW-4 and WSW-14. None
of the on-site monitoring wells contained measurable thicknesses of free product, but 1,2-
dichloroethane was detected above its GCL in monitoring well MW-1. Additionally, 1,2-
dichloroethane was detected in water supply well WSW-14 at a concentration slightly above its 2L
standard.
Terracon mobilized to the site on September 5, 2018 to collect groundwater samples for laboratory
analysis from monitoring wells MW-1 and DW-1 and water supply wells WSW-4 and WSW-14. None
of the on-site monitoring wells contained measurable thicknesses of free product, but 1,2-
dichloroethane was detected above its GCL in monitoring well MW-1. Additionally, 1,2-
dichloroethane was detected in water supply well WSW-14 at a concentration slightly above its 2L
standard.
Terracon mobilized to the site on March 5, 2019 to collect groundwater samples for laboratory
analysis from monitoring wells MW-1 and DW-1 and water supply wells WSW-4 and WSW-14. None
of the on-site monitoring wells contained measurable thicknesses of free product, but multiple
petroleum constituents were detected above their respective 2L standards in monitoring well MW-1.
Additionally, 1,2-dichloroethane was detected in water supply well WSW-14 at a concentration
slightly below its 2L standard.
C.4 Water Supply Wells
Fourteen water-supply wells were identified within 1,000 feet of the UST basin (source area) during
Terraine’s receptor survey. Municipal water is reportedly not available to the site or surrounding
properties. Water supply well WSW-1 is located on the site approximately 85 feet from the source
area and operates with a POS system. Water supply wells WSW-2, WSW-3, WSW-4, WSW-5,
WSW-6, WSW-7 and WSW-14 are located within 250 feet of the source area and are currently in
use. The remaining six water-supply wells (WSW-8, WSW-9, WSW-10, WSW-11, WSW-12 and
WSW-13) are located approximately 400 feet or greater from the source area. A summary of
Terraine’s receptor survey is presented in Table 1 and the locations of the wells are shown on
Figure 3.
C.5 Surface Water
The site is situated on the northeastern flank of a northwest-southeast trending ridge that parallels
nearby South New Hope Road. Most of the site is located in the drainage basin of the South Fork of
the Catawba River, which, at its closest point, is situated approximately 2,900 feet east of the site.
An unnamed tributary of the South Fork is located approximately 950 feet north of the site. Surface
waters are depicted on Figure 1.
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 8
C.6 Land Use Information
Adjacent properties to the north are occupied by single-family residences or are wooded. Adjacent
properties to the east include single-family residences and Grady McCuen Floors. Adjoining
properties to the south and west are occupied by single-family residences. There are no readily
identifiable sensitive land use features within 1,500 feet of the site.
D. ASSESSMENT INFORMATION
D.1 Site Geology and Hydrogeology
The following resources were reviewed to evaluate site-specific geological and hydrogeological
characteristics.
Belmont, North Carolina, USGS 7.5-minute series topographic map, dated 1997 (Figure 1).
Geologic Map of North Carolina, dated 1985.
The Geology of the Carolinas, Carolina Geological Society Fiftieth Anniversary Volume, edited by J.
Wright Horton, Jr., and Victor A. Zullo, The University of Tennessee Press, dated 1991.
Soil Survey of Gaston County, North Carolina, US Department of Agriculture, Natural Resources
Conservation Service, Web Soil Survey via the Internet,http://websoilsurvey.nrcs.usda.gov/app/.
The site is located within the Charlotte Belt of the Piedmont Physiographic Province. The Piedmont
Physiographic Province generally consists of low to medium elevation, rounded hills and long rolling
northeast to southwest trending ridges with incised creeks and river channels. Rocks in the site area
are described as metamorphosed felsic volcanic rocks.
In-place chemical and physical weathering of parent rocks typically form residual soils in the
Piedmont region. Weathering is facilitated by the presence of fractures, joints, and less resistant
minerals in the rock. In areas not altered by erosion, alluvial deposition or the activities of man, the
typical residual soil profile consists of clay-rich unconsolidated materials at the surface, transitioning
to sandy silts and silty sands at depth. Typically, the boundary between soil and rock is not sharply
defined. This transitional zone is termed “partially weathered rock” or saprolite. Information obtained
from the Web Soil Survey for Gaston County, depicts soils on the site as Cecil-Urban land complex
(CfB).
In the Piedmont, groundwater generally occurs in pore spaces within soils and in the structural
features present in the underlying rock (i.e. joints, fractures, and faults). Recharge to the water table
is primarily by precipitation infiltrating the surficial soils and percolating downward under the influence
of gravity to the water table (vadose zone). Typically, the water table is not a level surface, but a
subdued reflection of the land surface. The depth to the water table is not consistent and is
dependent upon several factors that include the amount of rainfall, permeability of the soil, the extent
of fracturing in the underlying rock and the influences of groundwater pumping. Groundwater
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 9
typically flows in directions parallel to the ground surface and under the influence of gravity, migrates
to discharge points such as surface water features, the toes of slopes or natural springs.
Fluctuations in the depth of the water table can be expected depending on variations in precipitation,
surface water run-off and other factors not evident at the time of our subsurface exploration.
Normally, the highest levels of the water table occur in late winter and spring and the lowest levels
occur in the late summer and fall. Based on an interpreted groundwater flow direction from historical
data, groundwater is expected to flow to the east-southeast from the site.
D.2 Sampling Activities
D.2.1 Free Product Evaluation
No free product was encountered at the site during this sampling event.
D.2.2 Groundwater Sampling Activities
Terracon mobilized to the site on December 30, 2019 to evaluate current site conditions by collecting
groundwater samples from monitoring wells MW-1, MW-4 and DW-1 and water supply wells WSW-1
and WSW-4. The approximate locations of the monitoring wells are shown on Figure 2. Initially,
Terracon gauged the groundwater levels in the monitoring wells. Depth to groundwater ranged from
27.24 feet bgs in well MW-4 to 38.15 feet bgs in well DW-1. Although Terracon could not determine
groundwater flow direction during this sampling event (sampled wells in general straight line), the
historical flow direction at the site has been to the east-southeast (Figure 4). Current and historical
groundwater depth measurements are provided in Table 3.
Prior to sampling, the monitoring wells were purged a minimum of three well volumes. The wells
were allowed to recharge a minimum of 90 percent of the original well volume before samples were
collected. Terracon also collected water samples from water supply wells WSW-1 and WSW-4
located near the source property. The supply wells were purged by allowing water to flow from a
spigot near the wellhead for a minimum of 15 minutes. Flow was reduced when the sample was
collected. Terracon was not granted access to water supply wells WSW-2, WSW-3, WSW-5, WSW-
6 and WSW-14.
The water samples were placed in laboratory-supplied glassware, labeled and stored in an ice-
packed cooler. The samples, along with chain-of-custody documentation, were delivered to Pace
Analytical Services, Inc. in Huntersville, North Carolina for analysis of VOCs by EPA Method 6200B,
including MTBE, IPE and EDB on a standard laboratory schedule.
D.2.3 Analytical Results
According to the laboratory analytical report, 1,2-dichloroethane (555 µg/L) was detected above its
Gross Contamination Level (GCL) in monitoring well MW-1. Benzene (3,860 µg/L), naphthalene (407
µg/L), ethylbenzene (660 µg/L), n-propylbenzene (115 µg/L), toluene (3,000 µg/L), 1,2,4-
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 10
trimethylbenzene (1,570 µg/L), 1,3,5-trimethylbenzene (659 µg/L), and total xylenes (5,520 µg/L)
were detected above their respective 2L groundwater standards in monitoring well MW-1. Benzene
(48 µg/L) and 1,2-dichlororethane (7.7 µg/L) were detected in monitoring well DW-1 above their
respective 2L standards. Various other petroleum constituents were detected in monitoring wells
MW-1 and DW-1 at concentrations below their respective 2L standards.
Benzene (0.52 µg/L) was also detected in water supply well WSW-1 at a concentration below its 2L
standard. No constituents of concern were detected in well MW-4 above the MDLs. The analytical
results from the monitoring wells and water supply wells are summarized in Table 2 and are shown
on Figure 5. A copy of the laboratory analytical report is provided in Appendix A.
To attempt to reduce the constituent concentrations in wells MW-1 and DW-1, Terracon installed
RemRx™ CRP Persulfate sleeves into the two on-site monitoring wells on February 5, 2020. The
effectiveness of the sleeves will be evaluated during future sampling events.
E. CONCLUSIONS AND RECOMMENDATIONS
Based on information obtained during the completion of these assessment activities, Terracon
provides the following conclusions and findings.
None of the monitoring wells contained measurable thicknesses of free product.
1,2-Dichloroethane (555 µg/L) was detected above its GCL in monitoring well MW-1.
Benzene (3,860 µg/L), naphthalene (407 µg/L), n-propylbenzene (115 µg/L), ethylbenzene (660
µg/L), toluene (3,000 µg/L), 1,2,4-trimethylbenzene (1,570 µg/L), 1,3,5-trimethylbenzene (659 µg/L),
and total xylenes (5,520 µg/L) were detected above their respective 2L groundwater standards in
monitoring well MW-1. Benzene (48 µg/L) and 1,2-dichlororethane (7.7 µg/L) were detected in
monitoring well DW-1 above their respective 2L standards.
Benzene (0.52 µg/L) was also detected in water supply well WSW-1 at a concentration below
its 2L standard.
Terracon was not granted access to water supply wells WSW-2, WSW-3, WSW-5, WSW-6 and
WSW-14.
RemRx™ CRP Persulfate sleeves were installed into on-site monitoring wells MW-1 and DW-1 on
February 5, 2020 to reduce constituent concentrations.
Historically, the groundwater flow direction at the site has been towards the east-southeast.
Constituent concentration trends in wells MW-1 and DW-1 have increased since the previous
sampling event (March 2019).
Burcham Property
Belmont, North Carolina
Project Number 71149638A
Incident No. 3679
February 7, 2020
Responsive ■Resourceful ■Reliable 11
Based on the data presented in this assessment, Terracon recommends the following activities be
completed at the site.
Groundwater monitoring wells and selected off-site water supply wells should be sampled semi-
annually to evaluate the effectiveness of the RemRx remediation sleeves in the groundwater.
FIGURES
SITE LOCATION MAP
Burcham Property
1630 Armstrong Ford Road
Belmont, NC
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGICAL SURVEY
QUADRANGLE: BELMONT, NC (1/1/1997).
2701 WestportRoad
Charlotte, NC
71149638AProject Manager:
Drawn by:
Checked by:
Approved by:
MAW
CLC
CLC
1:24,000
Burcham
February 2020
Project No.
Scale:
File Name:
Date:1
FigureMAW
SITE
2
Figure
DIAGRAM IS FOR GENERAL LOCATION ONLY,
AND IS NOT INTENDED FOR CONSTRUCTION
PURPOSES 2701 Westport Road
Charlotte, NC
Burcham Property
1630 Armstrong Ford Road
Belmont, Gaston County, NC
SITE AND SURROUNDING PROPERTIES MAPProject Manager:
Drawn by:
Checked by:
Approved by:
MAW
Project No.
File Name:
Date:
Scale:
71149638A
MAW
February 2020CLC
BurchamCLC
1” ~ 110’
MW-1
MW-2
WSW-14
DW-1
WSW-1
MW-4
MW-3
WSW-2
MW-6
MW-5
denotes approximate site
boundary
denotes water
supply well
denotes groundwater
monitoring well.
1
5
4
7
3
2
6
10
12 9
8
11
1,000 ft. Radius
(from release location)
RECEPTOR SURVEY MAP
BurchamProperty (Incident #3679)
1630 Armstrong Ford Road
Belmont, Gaston County, NC
2701 Westport Road
Charlotte, NC
DIAGRAM IS FOR GENERAL LOCATION ONLY, AND IS
NOT INTENDED FOR CONSTRUCTION PURPOSES
71149638A
SAC
CLC
CLC
AS SHOWN
February 2020
Scale:
3
FigureProject Manager:
Drawn by:
Checked by:
Approved by:
Project No.
File Name:
Date:
MAW
NUMBER CORRESPONDS WITH WATER SUPPLY WELL INFORMATIONLISTED IN TABLE 1
AERIAL PHOTOGRAPHY PROVIDED BYMICROSOFT BING MAPS
14
13
Burcham
4
Figure
DIAGRAM IS FOR GENERAL LOCATION ONLY,
AND IS NOT INTENDED FOR CONSTRUCTION
PURPOSES 2701 Westport Road
Charlotte, NC
GROUNDWATER ELEVATIONS MAPProject Manager:
Drawn by:
Checked by:
Approved by:
MAW Project No.
File Name:
Date:
Scale:
71149638A
MAW
February 2020CLC
BurchamCLC
1” ~ 110’
MW-1 MW-2
(Not Measured)
WSW-14
DW-1
(64.26)
WSW-1
MW-4
(65.17)
MW-3
(Not Measured)
WSW-2
(64.51)
MW-5
(Not Measured)
approximate site boundary
water supply well
groundwater monitoring
well
Burcham Property
1630 Armstrong Ford Road
Belmont, Gaston County, NC
MW-6
(Not Measured)
5
Figure
DIAGRAM IS FOR GENERAL LOCATION ONLY,
AND IS NOT INTENDED FOR CONSTRUCTION
PURPOSES 2701 Westport Road
Charlotte, NC
GROUNDWATER ANALYTICAL RESULTSProject Manager:
Drawn by:
Checked by:
Approved by:
MAW
Project No.
File Name:
Date:
Scale:
71149638A
MAW
February 2020CLC
BurchamCLC
1” ~ 110’
MW-1
MW-2
WSW-14
(not sampled)
DW-1
WSW-1
MW-4
MW-3
WSW-2
MW-6
MW-5
Sample ID: DW-1
Groundwater Sample6200 –Benzene: 8.9 µg/L1,2-Dichloroethane: 0.39J µg/L
Diisopropyl Ether (IPE): 0.31J µg/L
Ethylbenzene: 0.81 µg/L
Toluene: 0.47J µg/L1,2,4 Trimethylbenzene: 0.31J µg/LTotal Xylenes: 0.80J µg/L
*Values above 2L Standards are in bold.
**J indicates estimated value.
denotes approximate site
boundary
denotes water
supply well
denotes groundwater
monitoring well.
Burcham Property
1630 Armstrong Ford Road
Belmont, Gaston County, NC
Sample ID: MW-16200 –Benzene: 3,860 µg/L
1,2-Dichloroethane: 555 µg/L
Ethylbenzene: 660 µg/L
Isopropylbenzene: 64.0 µg/L
Naphthalene: 407 µg/Ln-Propylbenzene: 115 µg/L
Toluene: 3,000 µg/L
1,2,4-Trimethylbenzene: 1,570 µg/L
1,3,5-Trimethylbenzene: 659 µg/L
Total Xylenes: 5,520 µg/L*Values above 2L standards are inbold
**Values above GCL standards are bold,italicized, and red
***J indicates estimated value
(not sampled)
(not sampled)
Sample ID: WSW-1
Groundwater Sample
6200 – Benzene: 0.52 µg/L
(not sampled)
(not sampled)
Sample ID: DW-1
Groundwater Sample
6200 –Benzene: 48.0 µg/L
n-Butylbenzene: 0.47J µg/Lsec-Butylbenzene: 0.46J µg/L
1,2-Dichloroethane: 7.7 µg/L
Diisopropyl Ether (IPE): 4.7 µg/L
Ethylbenzene: 2.7 µg/L
Isopropylbenzene: 2.7 µg/Ln-Propylbenzene: 0.58 µg/L
Toluene: 1.0 µg/L
1,2,4 Trimethylbenzene: 0.37J µg/L
Total Xylenes: 1.71J µg/L
*Values above 2L Standards are in bold.**J indicates estimated value.
Sample ID: MW-4
Groundwater Sample
No Analytes Detected
TABLES
TABLE 1
Water Supply Well Information
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
Active 189407
WSW-2 John Brady Hightower Jr.210 Crest Street 1624 Armstrong Ford Road 150' northeast
Well Status/Use Tax PIN Notes
WSW-1 Beverly Pitman 1630 Armstrong Ford Road 1630 Armstrong Ford Road Onsite; 85' north-
northeast
Well No.Property Owner Mailing Address Property Address Distance/Directions
from site
Active 189453
WSW-4 Roger & Wanda Brown
704-813-1525 1640 Armstrong Ford Road 1640 Armstrong Ford Road 80' northwest
Active 189478
WSW-3 Joseph & Melinda Helms 1633 Armstrong Ford Road 1633 Armstrong Ford Road 130' southwest
Active 218581
WSW-8 Jeffery Scott Webb 215 Harrison Dr 215 Harrison Dr 620' east-southeast
Active 189402
WSW-5 Roger Hightower 1626 Armstrong Ford Road 1626 Armstrong Ford Road 210' northeast
189409
Active
Active 189474
WSW-7 Sandra Mason 104 Crest Street 104 Crest Street 240' southeast
Active
Active 189460
WSW-9 Charlie Jr. & Vickie Franklin 130 Harrison Dr 130 Harrison Dr 520' south-southeast
189454
WSW-6 Daniel & Lisa Moss 1620 Armstrong Ford Road 1620 Armstrong Ford Road 200' north-northeast
Active 189463
WSW-11 Tammy Dellinger & Timothy
Justice 1600 Armstrong Ford Road 1600 Armstrong Ford Road 680' northeast Active
WSW-10 Mark Morgan 222 Harrison Dr 222 Harrison Dr 890' ease-southeast
189531
WSW-14 Brian & Debby Henry
[phone]
5555 Bud Wilson Rd
Gastonia, NC 28052
1641 Armstrong Ford Road &
1625 Armstrong Ford Road 145' south-southeast
WSW-13 Richi Lee & Marla Stowe Price 236 Stowe Road
Gastonia, NC 28056 202 Harrison Dr 590' southeast Active 189470
WSW-12 Allen Owenby 133 Harrison Dr 133 Harrison Dr 390' south Active 189447
Active 189452 and
189451
TABLE 2
Summary of Groundwater Analytical Results
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
6010B
Well/Sample
I.D.
Date Collected
(mm/dd/yy)
3/1/1995 ND 15,000 350 ND ND 2,300 ND 20,000 ND 1,900 NA ND ND ND 600 NA ND 21,000 1,500 NA 11,800 ND ND ND 181/14/1998 ND 15,000 450 ND ND 420 ND 960 1,000 2,100 NA ND ND ND 880 NA ND 20,000 1,900 ND 1,200 ND ND ND 647/21/99 ND 12,000 1,000 ND ND 350 ND 810 1,000 2,200 NA ND NA ND NA NA ND 17,000 3,800 810 16,200 ND ND ND NA
1/6/2000 ND 12,600 100 ND ND 250 ND 1,300 NA 1,800 150 ND NA ND 850 150 ND 16,300 1,650 400 10,350 ND ND ND NA
3/24/2003 ND 9,800 NA ND ND NA ND 900 ND 1,500 NA ND ND ND NA NA ND 12,000 NA NA 11,700 ND ND ND NA
1/18/2006 ND 10,700 NA ND ND 534 ND NA 83 1,430 NA ND ND ND NA NA ND 16,300 NA NA 11,100 ND ND ND NA11/20/2008 ND 3,350 ND ND ND 12 ND 550 62 872 161 ND ND ND 836 161 ND 3,670 2,600 844 6,500 ND ND ND NA
10/21/2009 ND 6,870 ND ND ND ND ND 938 111 955 143 ND ND ND 656 143 ND 6,000 2,380 878 9,150 ND ND ND NA
4/30/2012 ND 2,800 52 5.6J ND 22 ND 720 76 260 39 19 ND 17 140 39 ND 2,000 680 470 3,800 ND ND ND NA
11/29/20127/14/2014
10/15/2015
5/4/2017 NA 2,890 <0.5 <0.5 14.6J <0.5 ND 586 70.7 792 108 NA <5.0 <20.0 538 <5.0 ND 2,800 2,270 957 7,330 NA NA NA NA
2/26/2018 NA 3,680 <12.5 <12.5 <25 <12.5 25 530 71.4 659 60.5 NA <12.5 <50 409 <12.5 10.4J 2,610 1,550 577 6,130 NA NA NA NA9/5/2018 NA 4,550 <6.2 <6.2 <12.5 <6.2 <6.2 542 76.8 1,150 112 NA <6.2 <25.0 544 215 19 3,940 1,990 797 7,500 NA NA NA NA
3/5/2019 NA 3,010 <6.2 <6.2 <12.5 <6.2 <6.2 369 <6.2 459 50.6 NA <6.2 <25.0 266 <6.2 8.1J 2,000 1,200 528 4,930 NA NA NA NA
12/30/2019 NA 3,860 <14.1 <9.8 <16.6 <9.2 <7.3 555 <13.4 660 64.0 NA <17.8 <60.0 407 115 <10.2 3,000 1,570 659 5,520 NA NA NA NA
3/1/1995 ND 14,000 350 ND ND 2,000 ND 15,000 ND 11,800 NA ND ND ND 600 NA ND 22,000 1,500 NA 11,800 ND ND ND 151/14/1998 ND 5,200 ND ND ND 21 ND 720 370 980 NA ND ND ND 220 NA ND 1,100 310 ND 980 ND ND ND 13.97/21/1999 ND 9,600 410 ND ND 330 ND 560 1,200 6,800 NA ND NA ND NA NA ND 8,400 1,200 ND 6,800 ND ND ND NA
7/24/2001 ND 6,410 90 ND ND 90 ND 1,070 NA 1,930 30 ND NA ND 250 50 ND 1,830 510 310 1,930 ND ND ND NA
3/24/2003 ND 1,300 NA ND ND NA ND 350 ND 1,490 NA ND ND ND NA NA ND 1,500 NA 190 1,490 ND ND ND NA1/18/2006 ND 1,830 NA ND ND 6.6 ND NA 43.5 1,160 NA ND ND ND NA NA ND 1,100 NA NA 1,160 ND ND ND NA10/21/2009 ND 6,260 ND ND ND ND ND 722 102 4,990 73.2 ND ND ND 519 141 ND 4,530 1,380 NA 4,990 ND ND ND NA
11/29/2012
7/14/201410/15/20155/4/2017
2/26/2018
9/5/2018
3/1/1995 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND NA NA ND ND ND ND ND1/14/1998 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND ND ND ND ND ND ND
7/24/2001 ND ND NA ND ND NA ND ND ND ND NA ND NA ND NA NA ND ND NA NA NA ND ND ND NA
3/24/2003 ND ND NA ND ND NA ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
1/18/2006 ND ND NA ND ND ND ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA10/29/2009
11/29/2012
7/14/2014
10/15/20155/4/2017
2/26/2018
9/5/2018
6,000 1 70 70 3 0.02 0.6 0.4 70 600 70 25 20 5 6 70 70 600 400 400 500 400 700 200 156,000,000 5,000 6,900 8,500 3000 50 600 400 70,000 84,500 25,000 11,700 20,000 5,000 6,000 30,000 70,000 260,000 28,500 25,000 85,500 NA NA NA 15,000
All results reported in micrograms per liter (µg/L).
<- denotes less than method detection limit or the EPA 6200B Minimum Reporting Limit
ND indicates not detected (detection limits are unknown for sampling conducted prior to Terracon's involvement with the site.)
NR indicates constitute not reported for this analytical method..
NA denotes not analyzed.
Bold and gray shading depict levels above the 2L standard.Yellow shading depicts levels above the GCL.
Not Sampled, Well not FoundNot Sampled, Well not Found
Not Sampled - Free Product
Not Sampled
Not Sampled
Not Sampled, Well not FoundNot Sampled, Well not Found
Not Sampled
Not Sampled
Not Sampled
Not Sampled
Not Sampled
Not Sampled - Free ProductNot Sampled - Free Product
Not Sampled
Not Sampled MethyleneChlorideTolueneNaphthaleneXylenes(Total)1,3,5-Trimethylbenzenen-Propylbenzene1,2-DichloropropaneStyreneMADEP VPH
C5-C8AliphaticsC9-C12AliphaticsC9-C10AromaticsLeadAnalytical Method
1,2,4-TrimethylbenzeneAcetoneEthylbenzeneIsopropylbenzenesec-Butylbenzenen-Butylbenzene1,2-DichloroethaneDiisopropylEther(IPE)Contaminant of Concern →p-IsopropyltolueneMethyltert-butylEther(MTBE)6200B
1,2-Dibromoethane(EDB)BenzeneChloromethaneMW-1
MW-3
MW-2
2L Standard (ug/L)
GCL (ug/L)
Page 2 of 6
TABLE 2
Summary of Groundwater Analytical Results
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
6010B
Well/Sample
I.D.
Date Collected
(mm/dd/yy)MethyleneChlorideTolueneNaphthaleneXylenes(Total)1,3,5-Trimethylbenzenen-Propylbenzene1,2-DichloropropaneStyreneMADEP VPH
C5-C8AliphaticsC9-C12AliphaticsC9-C10AromaticsLeadAnalytical Method
1,2,4-TrimethylbenzeneAcetoneEthylbenzeneIsopropylbenzenesec-Butylbenzenen-Butylbenzene1,2-DichloroethaneDiisopropylEther(IPE)Contaminant of Concern →p-IsopropyltolueneMethyltert-butylEther(MTBE)6200B
1,2-Dibromoethane(EDB)BenzeneChloromethane8/24/1988 ND ND NA ND ND NA ND ND ND 0.5 NA ND ND ND ND NA ND 0.48 ND ND ND ND ND ND ND
11/24/1994 ND ND NA ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND ND ND ND ND ND ND
3/1/1995 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND NA ND ND ND ND ND
1/14/1998 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND ND ND ND ND ND ND1/6/2000 ND ND ND ND ND ND ND ND NA ND ND ND NA ND ND ND ND ND ND ND NA ND ND ND NA7/24/2001 ND ND NA ND ND NA ND ND ND ND NA ND NA ND NA NA ND ND NA NA ND ND ND ND NA
3/24/2003 ND ND NA ND ND NA ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
1/18/2006 ND ND NA ND ND ND ND ND ND ND NA ND ND ND NA NA ND 0.66 NA NA ND ND ND ND NA11/20/2008 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND 5.4 ND ND ND NA10/21/2009 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA
11/29/2012 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
7/14/2014 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA
10/15/2015 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA5/4/2017 NA <0.25 <0.25 <0.25 <0.5 <0.25 ND <0.25 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA
2/26/2018 NA <0.5 <0.5 <0.5 <1.0 <0.5 ND <0.5 <0.5 <0.5 <0.5 NA <0.5 <2.0 <2.0 <0.5 ND <0.5 <0.5 <0.5 <1.5 NA NA NA NA
9/5/2018
12/30/2019 NA <0.24 <0.35 <0.25 <0.42 <0.23 <0.18 <0.26 <0.33 <0.24 <0.24 NA <0.44 <1.5 <0.66 <0.24 <0.26 <0.23 <0.19 <0.23 <0.24 NA NA NA NA3/1/1995 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND NA ND ND ND ND ND7/24/2001 ND ND NA ND ND NA ND ND ND ND NA ND NA ND NA NA ND ND NA NA NA ND ND ND NA
3/24/2003 ND ND NA ND ND NA ND ND ND ND NA ND ND ND NA NA ND ND NA NA NA ND ND ND NA
1/18/2006 ND ND NA ND ND ND ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA10/21/200911/29/2012 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
7/14/2014 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA
10/15/2015 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA
5/4/2017 NA <0.25 <0.25 <0.25 <0.5 <0.25 ND <0.25 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA2/26/2018 NA <0.5 <0.5 <0.5 <1.0 <0.5 ND <0.5 <0.5 <0.5 <0.5 NA <0.5 <2.0 <2.0 <0.5 ND <0.5 <0.5 <0.5 <1.5 NA NA NA NA
9/5/2018
3/1/1995 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND NA ND ND ND ND ND
1/14/1998 ND ND ND ND ND ND ND ND ND ND NA ND ND ND ND NA ND ND ND NA ND ND ND ND ND7/24/2001 ND ND NA ND ND NA ND ND ND ND NA ND NA ND NA NA ND ND NA NA NA ND ND ND NA
3/24/2003 ND ND NA ND ND NA ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
1/18/2006 ND ND NA ND ND ND ND ND ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
10/21/200911/29/2012 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
7/14/2014 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA
10/15/2015 NA <0.50 <0.50 <0.5 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA
5/4/2017 NA <0.25 <0.25 <0.25 <0.5 <0.25 ND <0.25 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA
2/26/2018 NA <0.5 <0.5 <0.5 <1.0 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 NA <0.5 <2.0 <2.0 <0.5 <0.5 <0.5 <0.5 <0.5 <1.5 NA NA NA NA
9/5/2018 6,000 1 70 70 3 0.02 0.6 0.40 70 600 70 25 20 5 6 70 70 600 400 400 500 400 700 200 156,000,000 5,000 6,900 8,500 3000 50 600 400 70,000 84,500 25,000 11,700 20,000 5,000 6,000 30,000 70,000 260,000 28,500 25,000 85,500 NA NA NA 15,000
All results reported in micrograms per liter (µg/L).
<- denotes less than method detection limit or the EPA 6200B Minimum Reporting Limit
ND indicates not detected (detection limits are unknown for sampling conducted prior to Terracon's involvement with the site.)
NR indicates constitute not reported for this analytical method.
NA denotes not analyzed.
Bold and gray shading depict levels above the 2L standard.
Yellow shading depicts levels above the GCL.
Not Sampled
Not Sampled
Not Sampled
2L Standard (ug/L)GCL (ug/L)
MW-6
Not Sampled
Not Sampled
MW-4
MW-5
Page 3 of 6
TABLE 2
Summary of Groundwater Analytical Results
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
6010B
Well/Sample
I.D.
Date Collected
(mm/dd/yy)MethyleneChlorideTolueneNaphthaleneXylenes(Total)1,3,5-Trimethylbenzenen-Propylbenzene1,2-DichloropropaneStyreneMADEP VPH
C5-C8AliphaticsC9-C12AliphaticsC9-C10AromaticsLeadAnalytical Method
1,2,4-TrimethylbenzeneAcetoneEthylbenzeneIsopropylbenzenesec-Butylbenzenen-Butylbenzene1,2-DichloroethaneDiisopropylEther(IPE)Contaminant of Concern →p-IsopropyltolueneMethyltert-butylEther(MTBE)6200B
1,2-Dibromoethane(EDB)BenzeneChloromethane3/1/1995 ND 5.6 ND ND ND ND ND 350 ND 1.1 NA ND ND ND ND NA ND 3.2 ND NA 10.9 ND ND ND ND
1/14/1998 ND 1 ND ND ND ND ND 2 ND ND NA ND ND ND ND NA ND ND ND ND ND ND ND ND ND
7/21/1999 ND 1 ND ND ND ND ND 4 0.6 ND NA ND NA ND NA NA ND 0.5 ND ND 1.3 ND ND ND NA
1/6/2000 ND 15.6 ND ND ND ND ND 3.6 NA 1.2 ND ND NA ND 1 ND ND 0.3 ND ND 0.3 ND ND ND NA7/24/2001 ND 16 NA ND ND NA ND 9.8 1.9 0.54 NA ND NA ND NA NA ND 0.52 NA NA NA ND ND ND NA3/24/2003 ND ND NA ND ND NA ND 2.3 ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
1/18/2006 ND 1.03 NA ND ND ND ND 1.36 ND ND NA ND ND ND NA NA ND ND NA NA ND ND ND ND NA
11/20/2008 ND 19 ND ND ND ND ND 4.2 0.6 3.6 ND ND ND ND ND 2.7 ND 2.9 ND ND 6 ND ND ND NA10/21/2009 ND 1.1 ND ND ND ND ND 0.5 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA11/29/2012 ND 0.72 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
7/14/2014 NA 104 <0.50 <0.50 ND <0.50 ND 3.2 <0.50 2.5 1.4 NR <0.50 <2.0 4.1 0.47J ND 7 2.1 0.29J 13.2 NA NA NA NA
10/15/2015 NA 2,100 <3.1 <3.1 ND <3.1 ND 21.8 25 175 20.8 NA <3.1 21.0J 97.4 20 ND 110 39.2 43 184.8 NA NA NA NA
5/4/2017 NA 34.8 <0.25 <0.25 <0.5 <0.25 ND 1.9 1.7 2.2 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND 2.3 <0.25 <0.25 1.65J NA NA NA NA2/26/2018 NA 19.2 <0.5 <0.5 <1.0 <0.5 ND 0.52 0.76 1.8 <0.5 NA <0.5 <2.0 <2.0 0.26J ND 1.1 1.3 <0.5 1.54J NA NA NA NA
9/5/2018 NA 51.3 <0.25 <0.25 <0.50 <0.25 <0.25 1.8 2.6 4.8 0.95 NA <0.25 <1.0 2.8 0.82 <0.25 5.1 2.0 <0.25 10.2 NA NA NA NA
3/5/2019 NA 8.9 <0.25 <0.25 <0.50 <0.25 <0.25 0.39J 0.31J 0.81 <0.25 NA <0.25 <1.0 <1.0 <0.25 <0.25 0.47J 0.31J <0.25 0.80J NA NA NA NA
12/30/2019 NA 48.0 0.47J 0.46J <0.42 <0.23 <0.18 7.7 4.7 2.7 2.7 NA <0.44 <1.5 <0.66 0.58 <0.26 1.0 0.37J <0.23 1.71J NA NA NA NA4/3/2012 ND 1.6 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND7/14/2014 NA 3.8 <0.50 <0.50 ND <0.50 ND 0.38J <0.50 0.36J <0.50 NA <0.50 <2.0 <2.0 <0.50 ND 0.53 <0.50 <0.50 0.63J NA NA NA NA
10/15/2015 NA 1 <0.50 <0.50 ND <0.50 ND 0.48J <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA
2/26/2018 NA 0.38J <0.5 <0.5 <1.0 <0.5 <0.5 0.29J <0.5 <0.5 <0.5 NA <0.5 <2.0 <2.0 <0.5 <0.5 <0.5 <0.5 <0.5 <1.5 NA NA NA NA9/5/201812/30/2019 NA 0.52 <0.35 <0.25 <0.42 <0.23 <0.18 <0.26 <0.33 <0.24 <0.24 NA <0.44 <1.5 <0.66 <0.24 <0.26 <0.23 <0.19 <0.23 <0.24 NA NA NA NA
WSW-1 - Spigot 4/3/2012 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND NA
WSW-1 Influent 11/29/2012 ND 5 ND ND ND ND ND ND ND 0.61 ND ND ND ND ND ND ND 0.82 ND ND ND ND ND ND ND
WSW- 1- Effluent 11/29/2012 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
Not Sampled
DMW-1
WSW-1- Well Head
Page 4 of 6
TABLE 2
Summary of Groundwater Analytical Results
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
6010B
Well/Sample
I.D.
Date Collected
(mm/dd/yy)MethyleneChlorideTolueneNaphthaleneXylenes(Total)1,3,5-Trimethylbenzenen-Propylbenzene1,2-DichloropropaneStyreneMADEP VPH
C5-C8AliphaticsC9-C12AliphaticsC9-C10AromaticsLeadAnalytical Method
1,2,4-TrimethylbenzeneAcetoneEthylbenzeneIsopropylbenzenesec-Butylbenzenen-Butylbenzene1,2-DichloroethaneDiisopropylEther(IPE)Contaminant of Concern →p-IsopropyltolueneMethyltert-butylEther(MTBE)6200B
1,2-Dibromoethane(EDB)BenzeneChloromethane7/14/2014 NR <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NR <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA10/15/2015
2/26/2018
9/5/2018
11/29/2012 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
7/14/2014 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA10/15/2015 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA2/26/20189/5/201810/15/2015 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA
5/4/2017 NA <0.25 <0.25 <0.25 <0.5 <0.25 ND <0.25 <0.25 <0.25 <0.25 NA 0.36J <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA
2/26/2018 NA <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 NA 0.37J <2.0 <2.0 <0.5 <0.5 <0.5 <0.5 <0.5 <1.5 NA NA NA NA
9/5/2018 NA <0.25 <0.25 <0.25 <0.5 <0.25 <0.25 <0.25 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 <0.25 <0.25 <0.25 <0.25 <0.25 NA NA NA NA
12/30/2019 NA <0.24 <0.35 <0.25 <0.42 <0.23 <0.18 <0.26 <0.33 <0.24 <0.24 NA <0.44 <1.5 <0.66 <0.24 <0.26 <0.23 <0.19 <0.23 <0.24 NA NA NA NA10/15/20152/26/20189/5/20187/14/2014 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA
10/15/2015 NA <0.50 <0.50 <0.50 ND <0.50 ND <0.50 <0.50 <0.50 <0.50 NA <0.50 <1.0 <1.0 <0.50 ND <0.50 <0.50 <0.50 <1.5 NA NA NA NA
5/4/2017 NA <0.25 <0.25 <0.25 ND <0.25 ND <0.25 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA2/26/20189/5/2018
11/29/2012 ND ND ND ND ND ND ND 1.7 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
7/14/2014 NR <0.50 <0.50 <0.50 ND <0.50 ND 0.55 <0.50 <0.50 <0.50 NR <0.50 <2.0 <2.0 <0.50 ND <0.50 <0.50 <0.50 <1.0 NA NA NA NA
10/15/20155/4/2017 NA <0.25 <0.25 <0.25 <0.5 <0.25 ND 0.73 <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 ND <0.25 <0.25 <0.25 <0.75 NA NA NA NA
2/26/2018 NA <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 0.84 <0.5 <0.5 <0.5 NA <0.5 <2.0 <2.0 <0.5 <0.5 <0.5 <0.5 <0.5 <1.5 NA NA NA NA
9/5/2018 NA <0.25 <0.25 <0.25 <0.5 <0.25 <0.25 0.42J <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 <0.25 <0.25 <0.25 <0.25 <0.25 NA NA NA NA
3/5/2019 NA <0.25 <0.25 <0.25 <0.5 <0.25 <0.25 0.39J <0.25 <0.25 <0.25 NA <0.25 <1.0 <1.0 <0.25 <0.25 <0.25 <0.25 <0.25 <0.25 NA NA NA NA6,000 1 70 70 3 0.02 0.6 0.4 70 600 70 25 20 5 6 70 70 600 400 400 500 400 700 200 15
6,000,000 5,000 6,900 8,500 3000 50 600 400 70,000 84,500 25,000 11,700 20,000 5,000 6,000 30,000 70,000 260,000 28,500 25,000 85,500 NA NA NA 15,000
All results reported in micrograms per liter (µg/L).
<- denotes less than method detection limit or the EPA 6200B Minimum Reporting Limit
ND indicates not detected (detection limits are unknown for sampling conducted prior to Terracon's involvement with the site.)
NR indicates constitute not reported for this analytical method.
NA denotes not analyzed.
Bold and gray shading depict levels above the 2L standard.
Yellow shading depicts levels above the GCL.
GCL (ug/L)2L Standard (ug/L)
Not Sampled
Not Sampled
Not Sampled
Not Sampled
Not Sampled
Not Sampled
Not Sampled
WSW-3
Not Sampled
Not Sampled
Not Sampled
WSW-14
WSW-4
WSW-5
Not Sampled
WSW-6
WSW-2
Page 5 of 6
TABLE 3
Monitoring Well Construction Information
and Historical Groundwater Elevations
Former Burcham Property
Belmont, North Carolina
Terracon Project No. 71149638A
NCDEQ Incident No. 3679
Well Id Date Intalled Date Water Level
Measured
Well Casing Depth
(ft. BGS)
Screened Interval
(x to y ft. BGS)
Bottom of Well
(ft. BGS)
Top of Casing
Elevation (ft.)
Depth to Water
from Top of
Casing (ft.)
Free Product
Thickness (ft.)
Groundwater
Elevation (ft.)Comments
3/1/1995 34.28 -68.161/14/1998 35.15 -67.29
8/21/1999 37.77 -64.677/24/2001 41.39 0.58 61.05
9/14/2001 NA 0.58 NA
12/20/2001 NA 0.1 NA11/1/2002 NA 0.98 NA
3/24/2003 36.61 -65.83
1/18/2006 37.00 -65.4411/20/2008 41.88 -60.56
10/21/2009 41.14 -61.304/30/2012 38.75 -63.6911/29/2012 45.02 -57.42
7/14/2014 NA 0.25 NA10/15/2015 41.67 0.01 60.78
5/4/2017 38.23 0.01 64.21
2/26/2018 39.42 -63.029/5/2018 40.44 -62.00
3/5/2019 33.49 -68.95
12/30/2019 37.93 -64.513/1/1995 35.16 -70.391/14/1998 34.23 -71.32
8/21/1999 36.79 -68.767/24/2001 40.44 0.46 65.11
9/14/2001 NA 0.46 NA
12/20/2001 NA 0.19 NA11/1/2002 NA 0.72 NA
3/24/2003 35.70 -69.85
1/18/2006 33.42 -72.1311/20/2008 NM -NA
10/21/2009 40.24 -65.317/14/2014 NM -NM10/15/2015 NM -NM
5/4/2017 NM -NM2/26/2018 NM -NM9/5/2018
3/1/1995 32.76 -64.79
1/14/1998 32.80 -64.758/21/1999 35.19 -62.36
7/24/2001 38.16 -59.393/24/2003 34.26 -63.291/18/2006 NM -NA
11/20/2008 NM -NA10/21/2009 NM -NA
11/29/2012 NM -NM
7/14/2014 NM -NM10/15/2015 NM -NM
5/4/2017 NM -NM
2/26/2018 NM -NM9/5/2018
3/1/1995 24.51 -67.90
1/14/1998 24.57 -67.848/21/1999 27.37 -65.04
7/24/2001 30.61 -61.80
3/24/2003 25.93 -66.481/18/2006 26.30 -66.11
11/20/2008 31.29 -61.12
10/21/2009 30.81 -61.6011/29/2012 34.51 -57.90
7/14/2014 25.73 -66.6810/15/2015 31.30 -61.115/4/2017 27.64 -64.77
2/26/2018 26.96 -65.459/5/201812/30/2019 27.24 -65.17
3/1/1995 36.59 -64.15
1/14/1998 NM -NA8/21/1999 38.70 -62.04
7/24/2001 41.51 -59.233/24/2003 37.81 -62.931/18/2006 38.26 -62.48
11/20/2008 42.37 -58.3710/21/2009 NM -NM11/29/2012 44.93 -55.81
7/14/2014 37.65 -63.0910/15/2015 41.71 -59.03
5/4/2017 39.07 -61.67
2/26/2018 40.40 -60.349/5/2018
3/1/1995 35.11 -67.30
1/14/1998 35.11 -67.308/21/1999 37.66 -64.75
7/24/2001 40.90 -61.51
3/24/2003 36.55 -65.861/18/2006 36.92 -65.49
11/20/2008 41.73 -60.68
10/21/2009 41.14 -61.2711/29/2012 44.78 -57.63
7/14/2014 37.71 -63.2210/15/2015 41.83 -59.105/4/2017 39.01 -61.92
2/26/2018 40.38 -60.55
9/5/20183/1/1995 35.11 -67.30
1/14/1998 35.11 -67.30
8/21/1999 37.66 -64.757/24/2001 40.90 -61.51
3/24/2003 36.55 -65.861/18/2006 36.92 -65.4911/20/2008 41.73 -60.68
10/21/2009 41.14 -61.2711/29/2012 44.78 -57.637/14/2014 37.32 -65.09
10/15/2015 41.64 -60.775/4/2017 38.48 -60.77
2/26/2018 39.48 -62.93
9/5/2018 40.41 -62.003/5/2019 33.41 -69.00
12/30/2019 38.15 64.26
MW-3 2/22/1995 25 25-45 45
101.55MW-2 2/21/1995 25 25-50 50
MW-5 2/20/1995 25 25-48 48
25 25-48 48 100.93
DW-1 2/23/1995 62 62-64.5 64.5
MW-6 2/20/1995
MW-1 2/21/1995 24 22-46 46
MW-4 8/1/1988 Unknown Unknown 45
Not Sampled
102.41
102.44
92.41
Not Sampled
Not Sampled
100.74
Not Sampled
Not Sampled
97.55
APPENDIX A
LABORATORY ANALYTICAL RESULTS AND
CHAIN-OF-CUSTODY FORMS
#=CL#
January 06, 2020
LIMS USE: FR - MCKHENZY WELCH
LIMS OBJECT ID: 92458986
92458986
Project:
Pace Project No.:
RE:
McKhenzy Welch
Terracon
2701 Westport Rd
Charlotte, NC 28208
Burcham Property
Dear McKhenzy Welch:
Enclosed are the analytical results for sample(s) received by the laboratory on December 31, 2019.
The results relate only to the samples included in this report. Results reported herein conform to the
most current, applicable TNI/NELAC standards and the laboratory's Quality Assurance Manual,
where applicable, unless otherwise noted in the body of the report.
If you have any questions concerning this report, please feel free to contact me.
Sincerely,
Taylor Ezell
[e-mail]
Project Manager
[phone]
Enclosures
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 1 of 34
#=CP#
CERTIFICATIONS
Pace Project No.:
Project:
92458986
Burcham Property
Pace Analytical Services Charlotte
9800 Kincey Ave. Ste 100, Huntersville, NC 28078
Louisiana/NELAP Certification # LA170028
North Carolina Drinking Water Certification #: 37706
North Carolina Field Services Certification #: 5342
North Carolina Wastewater Certification #: 12
South Carolina Certification #: 99006001
Florida/NELAP Certification #: E87627
Kentucky UST Certification #: 84
Virginia/VELAP Certification #: 460221
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 2 of 34
#=SS#
SAMPLE SUMMARY
Pace Project No.:
Project:
92458986
Burcham Property
Lab ID Sample ID Matrix Date Collected Date Received
92458986001 FB Water 12/30/19 10:30 12/31/19 09:51
92458986002 MW-1 Water 12/30/19 12:35 12/31/19 09:51
92458986003 DW-1 Water 12/30/19 12:05 12/31/19 09:51
92458986004 MW-4 Water 12/30/19 11:10 12/31/19 09:51
92458986005 WSW-1 Water 12/30/19 13:00 12/31/19 09:51
92458986006 WSW-4 Water 12/30/19 13:05 12/31/19 09:51
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 3 of 34
#=SA#
SAMPLE ANALYTE COUNT
Pace Project No.:
Project:
92458986
Burcham Property
Lab ID Sample ID Method
Analytes
Reported LaboratoryAnalysts
92458986001 FB SM 6200B 63 PASI-CCL
92458986002 MW-1 SM 6200B 63 PASI-CCL
92458986003 DW-1 SM 6200B 63 PASI-CCL
92458986004 MW-4 SM 6200B 63 PASI-CCL
92458986005 WSW-1 SM 6200B 63 PASI-CCL
92458986006 WSW-4 SM 6200B 63 PASI-CCL
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 4 of 34
#=HO#
SUMMARY OF DETECTION
Pace Project No.:
Project:
92458986
Burcham Property
Parameters AnalyzedResult
Lab Sample ID
Report Limit QualifiersUnitsMethod
Client Sample ID
92458986002 MW-1
Benzene 3860 ug/L 01/04/20 06:1220.0SM 6200B
1,2-Dichloroethane 555 ug/L 01/04/20 06:1220.0SM 6200B
Ethylbenzene 660 ug/L 01/04/20 06:1220.0SM 6200B
Isopropylbenzene (Cumene)64.0 ug/L 01/04/20 06:1220.0SM 6200B
Naphthalene 407 ug/L 01/04/20 06:1280.0SM 6200B
n-Propylbenzene 115 ug/L 01/04/20 06:1220.0SM 6200B
Toluene 3000 ug/L 01/04/20 06:1220.0SM 6200B
1,2,4-Trimethylbenzene 1570 ug/L 01/04/20 06:1220.0SM 6200B
1,3,5-Trimethylbenzene 659 ug/L 01/04/20 06:1220.0SM 6200B
m&p-Xylene 3290 ug/L 01/04/20 06:1240.0SM 6200B
o-Xylene 2230 ug/L 01/04/20 06:1220.0SM 6200B
92458986003 DW-1
Benzene 48.0 ug/L 01/02/20 20:390.50SM 6200B
n-Butylbenzene 0.47J ug/L 01/02/20 20:390.50SM 6200B
sec-Butylbenzene 0.46J ug/L 01/02/20 20:390.50SM 6200B
1,2-Dichloroethane 7.7 ug/L 01/02/20 20:390.50SM 6200B
Diisopropyl ether 4.7 ug/L 01/02/20 20:390.50SM 6200B
Ethylbenzene 2.7 ug/L 01/02/20 20:390.50SM 6200B
Isopropylbenzene (Cumene)2.7 ug/L 01/02/20 20:390.50SM 6200B
n-Propylbenzene 0.58 ug/L 01/02/20 20:390.50SM 6200B
Toluene 1.0 ug/L 01/02/20 20:390.50SM 6200B
1,2,4-Trimethylbenzene 0.37J ug/L 01/02/20 20:390.50SM 6200B
m&p-Xylene 0.98J ug/L 01/02/20 20:391.0SM 6200B
o-Xylene 0.73 ug/L 01/02/20 20:390.50SM 6200B
92458986005 WSW-1
Benzene 0.52 ug/L 01/04/20 02:280.50SM 6200B
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 5 of 34
#=NA#
PROJECT NARRATIVE
Pace Project No.:
Project:
92458986
Burcham Property
Method:
Client:Terracon - Charlotte, NC
SM 6200B
Date:January 06, 2020
Description:6200B MSV
General Information:
6 samples were analyzed for SM 6200B. All samples were received in acceptable condition with any exceptions noted below or on the
chain-of custody and/or the sample condition upon receipt form (SCUR) attached at the end of this report.
Hold Time:
The samples were analyzed within the method required hold times with any exceptions noted below.
Initial Calibrations (including MS Tune as applicable):
All criteria were within method requirements with any exceptions noted below.
Continuing Calibration:
All criteria were within method requirements with any exceptions noted below.
Internal Standards:
All internal standards were within QC limits with any exceptions noted below.
Surrogates:
All surrogates were within QC limits with any exceptions noted below.
Method Blank:
All analytes were below the report limit in the method blank, where applicable, with any exceptions noted below.
Laboratory Control Spike:
All laboratory control spike compounds were within QC limits with any exceptions noted below.
Matrix Spikes:
All percent recoveries and relative percent differences (RPDs) were within acceptance criteria with any exceptions noted below.
QC Batch: 517653
A matrix spike and/or matrix spike duplicate (MS/MSD) were performed on the following sample(s): 92458856005
M1: Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery.
• MSD (Lab ID: 2771445)
• Methyl-tert-butyl ether
R1: RPD value was outside control limits.
• MSD (Lab ID: 2771445)
• Bromomethane
QC Batch: 517750
A matrix spike and/or matrix spike duplicate (MS/MSD) were performed on the following sample(s): 92458919003
M1: Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery.
• MS (Lab ID: 2771746)
• Bromomethane
• MSD (Lab ID: 2771747)
• Bromomethane
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 6 of 34
#=NA#
PROJECT NARRATIVE
Pace Project No.:
Project:
92458986
Burcham Property
Method:
Client:Terracon - Charlotte, NC
SM 6200B
Date:January 06, 2020
Description:6200B MSV
Additional Comments:
This data package has been reviewed for quality and completeness and is approved for release.
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 7 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:FB Lab ID:92458986001 Collected:12/30/19 10:30 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene ND ug/L 01/02/20 19:09 71-43-20.50 0.24 1
Bromobenzene ND ug/L 01/02/20 19:09 108-86-10.50 0.22 1
Bromochloromethane ND ug/L 01/02/20 19:09 74-97-50.50 0.26 1
Bromodichloromethane ND ug/L 01/02/20 19:09 75-27-40.50 0.18 1
Bromoform ND ug/L 01/02/20 19:09 75-25-20.50 0.40 1
Bromomethane ND ug/L 01/02/20 19:09 74-83-95.0 1.7 1
n-Butylbenzene ND ug/L 01/02/20 19:09 104-51-80.50 0.35 1
sec-Butylbenzene ND ug/L 01/02/20 19:09 135-98-80.50 0.25 1
tert-Butylbenzene ND ug/L 01/02/20 19:09 98-06-60.50 0.25 1
Carbon tetrachloride ND ug/L 01/02/20 19:09 56-23-50.50 0.23 1
Chlorobenzene ND ug/L 01/02/20 19:09 108-90-70.50 0.22 1
Chloroethane ND ug/L 01/02/20 19:09 75-00-31.0 0.58 1
Chloroform ND ug/L 01/02/20 19:09 67-66-30.50 0.35 1
Chloromethane ND ug/L 01/02/20 19:09 74-87-31.0 0.42 1
2-Chlorotoluene ND ug/L 01/02/20 19:09 95-49-80.50 0.21 1
4-Chlorotoluene ND ug/L 01/02/20 19:09 106-43-40.50 0.21 1
1,2-Dibromo-3-chloropropane ND ug/L 01/02/20 19:09 96-12-81.0 0.38 1
Dibromochloromethane ND ug/L 01/02/20 19:09 124-48-10.50 0.40 1
1,2-Dibromoethane (EDB)ND ug/L 01/02/20 19:09 106-93-40.50 0.23 1
Dibromomethane ND ug/L 01/02/20 19:09 74-95-30.50 0.31 1
1,2-Dichlorobenzene ND ug/L 01/02/20 19:09 95-50-10.50 0.24 1
1,3-Dichlorobenzene ND ug/L 01/02/20 19:09 541-73-10.50 0.25 1
1,4-Dichlorobenzene ND ug/L 01/02/20 19:09 106-46-70.50 0.25 1
Dichlorodifluoromethane ND ug/L 01/02/20 19:09 75-71-80.50 0.28 1
1,1-Dichloroethane ND ug/L 01/02/20 19:09 75-34-30.50 0.24 1
1,2-Dichloroethane ND ug/L 01/02/20 19:09 107-06-20.50 0.26 1
1,1-Dichloroethene ND ug/L 01/02/20 19:09 75-35-40.50 0.22 1
cis-1,2-Dichloroethene ND ug/L 01/02/20 19:09 156-59-20.50 0.21 1
trans-1,2-Dichloroethene ND ug/L 01/02/20 19:09 156-60-50.50 0.26 1
1,2-Dichloropropane ND ug/L 01/02/20 19:09 78-87-50.50 0.18 1
1,3-Dichloropropane ND ug/L 01/02/20 19:09 142-28-90.50 0.34 1
2,2-Dichloropropane ND ug/L 01/02/20 19:09 594-20-70.50 0.28 1
1,1-Dichloropropene ND ug/L 01/02/20 19:09 563-58-60.50 0.35 1
cis-1,3-Dichloropropene ND ug/L 01/02/20 19:09 10061-01-50.50 0.36 1
trans-1,3-Dichloropropene ND ug/L 01/02/20 19:09 10061-02-60.50 0.39 1
Diisopropyl ether ND ug/L 01/02/20 19:09 108-20-30.50 0.33 1
Ethylbenzene ND ug/L 01/02/20 19:09 100-41-40.50 0.24 1
Hexachloro-1,3-butadiene ND ug/L 01/02/20 19:09 87-68-32.0 1.2 1
Isopropylbenzene (Cumene)ND ug/L 01/02/20 19:09 98-82-80.50 0.24 1
Methylene Chloride ND ug/L 01/02/20 19:09 75-09-22.0 1.5 1
Methyl-tert-butyl ether ND ug/L 01/02/20 19:09 1634-04-40.50 0.44 1
Naphthalene ND ug/L 01/02/20 19:09 91-20-32.0 0.66 1
n-Propylbenzene ND ug/L 01/02/20 19:09 103-65-10.50 0.24 1
Styrene ND ug/L 01/02/20 19:09 100-42-50.50 0.26 1
1,1,1,2-Tetrachloroethane ND ug/L 01/02/20 19:09 630-20-60.50 0.42 1
1,1,2,2-Tetrachloroethane ND ug/L 01/02/20 19:09 79-34-50.50 0.19 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 8 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:FB Lab ID:92458986001 Collected:12/30/19 10:30 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/02/20 19:09 127-18-40.50 0.23 1
Toluene ND ug/L 01/02/20 19:09 108-88-30.50 0.23 1
1,2,3-Trichlorobenzene ND ug/L 01/02/20 19:09 87-61-62.0 0.78 1
1,2,4-Trichlorobenzene ND ug/L 01/02/20 19:09 120-82-12.0 0.44 1
1,1,1-Trichloroethane ND ug/L 01/02/20 19:09 71-55-60.50 0.28 1
1,1,2-Trichloroethane ND ug/L 01/02/20 19:09 79-00-50.50 0.23 1
Trichloroethene ND ug/L 01/02/20 19:09 79-01-60.50 0.23 1
Trichlorofluoromethane ND ug/L 01/02/20 19:09 75-69-41.0 0.34 1
1,2,3-Trichloropropane ND ug/L 01/02/20 19:09 96-18-40.50 0.27 1
1,2,4-Trimethylbenzene ND ug/L 01/02/20 19:09 95-63-60.50 0.19 1
1,3,5-Trimethylbenzene ND ug/L 01/02/20 19:09 108-67-80.50 0.23 1
Vinyl chloride ND ug/L 01/02/20 19:09 75-01-41.0 0.41 1
m&p-Xylene ND ug/L 01/02/20 19:09 179601-23-11.0 0.44 1
o-Xylene ND ug/L 01/02/20 19:09 95-47-60.50 0.24 1
Surrogates
1,2-Dichloroethane-d4 (S)104 %01/02/20 19:09 17060-07-070-130 1
4-Bromofluorobenzene (S)98 %01/02/20 19:09 460-00-470-130 1
Toluene-d8 (S)101 %01/02/20 19:09 2037-26-570-130 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 9 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:MW-1 Lab ID:92458986002 Collected:12/30/19 12:35 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene 3860 ug/L 01/04/20 06:12 71-43-220.0 9.6 40
Bromobenzene ND ug/L 01/04/20 06:12 108-86-120.0 8.6 40
Bromochloromethane ND ug/L 01/04/20 06:12 74-97-520.0 10.3 40
Bromodichloromethane ND ug/L 01/04/20 06:12 75-27-420.0 7.4 40
Bromoform ND ug/L 01/04/20 06:12 75-25-220.0 16.2 40
Bromomethane ND ug/L 01/04/20 06:12 74-83-920068.8 40
n-Butylbenzene ND ug/L 01/04/20 06:12 104-51-820.0 14.1 40
sec-Butylbenzene ND ug/L 01/04/20 06:12 135-98-820.0 9.8 40
tert-Butylbenzene ND ug/L 01/04/20 06:12 98-06-620.0 10.0 40
Carbon tetrachloride ND ug/L 01/04/20 06:12 56-23-520.0 9.3 40
Chlorobenzene ND ug/L 01/04/20 06:12 108-90-720.0 9.0 40
Chloroethane ND ug/L 01/04/20 06:12 75-00-340.0 23.4 40
Chloroform ND ug/L 01/04/20 06:12 67-66-320.0 14.1 40
Chloromethane ND ug/L 01/04/20 06:12 74-87-340.0 16.6 40
2-Chlorotoluene ND ug/L 01/04/20 06:12 95-49-820.0 8.3 40
4-Chlorotoluene ND ug/L 01/04/20 06:12 106-43-420.0 8.2 40
1,2-Dibromo-3-chloropropane ND ug/L 01/04/20 06:12 96-12-840.0 15.4 40
Dibromochloromethane ND ug/L 01/04/20 06:12 124-48-120.0 16.1 40
1,2-Dibromoethane (EDB)ND ug/L 01/04/20 06:12 106-93-420.0 9.2 40
Dibromomethane ND ug/L 01/04/20 06:12 74-95-320.0 12.4 40
1,2-Dichlorobenzene ND ug/L 01/04/20 06:12 95-50-120.0 9.6 40
1,3-Dichlorobenzene ND ug/L 01/04/20 06:12 541-73-120.0 10.0 40
1,4-Dichlorobenzene ND ug/L 01/04/20 06:12 106-46-720.0 10 40
Dichlorodifluoromethane ND ug/L 01/04/20 06:12 75-71-820.0 11.4 40
1,1-Dichloroethane ND ug/L 01/04/20 06:12 75-34-320.0 9.8 40
1,2-Dichloroethane 555 ug/L 01/04/20 06:12 107-06-220.0 10.5 40
1,1-Dichloroethene ND ug/L 01/04/20 06:12 75-35-420.0 8.7 40
cis-1,2-Dichloroethene ND ug/L 01/04/20 06:12 156-59-220.0 8.3 40
trans-1,2-Dichloroethene ND ug/L 01/04/20 06:12 156-60-520.0 10.3 40
1,2-Dichloropropane ND ug/L 01/04/20 06:12 78-87-520.0 7.3 40
1,3-Dichloropropane ND ug/L 01/04/20 06:12 142-28-920.0 13.6 40
2,2-Dichloropropane ND ug/L 01/04/20 06:12 594-20-720.0 11.2 40
1,1-Dichloropropene ND ug/L 01/04/20 06:12 563-58-620.0 13.9 40
cis-1,3-Dichloropropene ND ug/L 01/04/20 06:12 10061-01-520.0 14.3 40
trans-1,3-Dichloropropene ND ug/L 01/04/20 06:12 10061-02-620.0 15.8 40
Diisopropyl ether ND ug/L 01/04/20 06:12 108-20-320.0 13.4 40
Ethylbenzene 660 ug/L 01/04/20 06:12 100-41-420.0 9.6 40
Hexachloro-1,3-butadiene ND ug/L 01/04/20 06:12 87-68-380.0 48.0 40
Isopropylbenzene (Cumene)64.0 ug/L 01/04/20 06:12 98-82-820.0 9.5 40
Methylene Chloride ND ug/L 01/04/20 06:12 75-09-280.0 60.0 40
Methyl-tert-butyl ether ND ug/L 01/04/20 06:12 1634-04-420.0 17.8 40
Naphthalene 407 ug/L 01/04/20 06:12 91-20-380.0 26.4 40
n-Propylbenzene 115 ug/L 01/04/20 06:12 103-65-120.0 9.6 40
Styrene ND ug/L 01/04/20 06:12 100-42-520.0 10.2 40
1,1,1,2-Tetrachloroethane ND ug/L 01/04/20 06:12 630-20-620.0 16.9 40
1,1,2,2-Tetrachloroethane ND ug/L 01/04/20 06:12 79-34-520.0 7.7 40
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 10 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:MW-1 Lab ID:92458986002 Collected:12/30/19 12:35 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/04/20 06:12 127-18-420.0 9.3 40
Toluene 3000 ug/L 01/04/20 06:12 108-88-320.0 9.1 40
1,2,3-Trichlorobenzene ND ug/L 01/04/20 06:12 87-61-680.0 31.2 40
1,2,4-Trichlorobenzene ND ug/L 01/04/20 06:12 120-82-180.0 17.4 40
1,1,1-Trichloroethane ND ug/L 01/04/20 06:12 71-55-620.0 11.1 40
1,1,2-Trichloroethane ND ug/L 01/04/20 06:12 79-00-520.0 9.3 40
Trichloroethene ND ug/L 01/04/20 06:12 79-01-620.0 9.3 40
Trichlorofluoromethane ND ug/L 01/04/20 06:12 75-69-440.0 13.4 40
1,2,3-Trichloropropane ND ug/L 01/04/20 06:12 96-18-420.0 10.8 40
1,2,4-Trimethylbenzene 1570 ug/L 01/04/20 06:12 95-63-620.0 7.7 40
1,3,5-Trimethylbenzene 659 ug/L 01/04/20 06:12 108-67-820.0 9.1 40
Vinyl chloride ND ug/L 01/04/20 06:12 75-01-440.0 16.3 40
m&p-Xylene 3290 ug/L 01/04/20 06:12 179601-23-140.0 17.6 40
o-Xylene 2230 ug/L 01/04/20 06:12 95-47-620.0 9.5 40
Surrogates
1,2-Dichloroethane-d4 (S)99 %01/04/20 06:12 17060-07-070-130 40
4-Bromofluorobenzene (S)97 %01/04/20 06:12 460-00-470-130 40
Toluene-d8 (S)101 %01/04/20 06:12 2037-26-570-130 40
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 11 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:DW-1 Lab ID:92458986003 Collected:12/30/19 12:05 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene 48.0 ug/L 01/02/20 20:39 71-43-20.50 0.24 1
Bromobenzene ND ug/L 01/02/20 20:39 108-86-10.50 0.22 1
Bromochloromethane ND ug/L 01/02/20 20:39 74-97-50.50 0.26 1
Bromodichloromethane ND ug/L 01/02/20 20:39 75-27-40.50 0.18 1
Bromoform ND ug/L 01/02/20 20:39 75-25-20.50 0.40 1
Bromomethane ND ug/L 01/02/20 20:39 74-83-95.0 1.7 1
n-Butylbenzene 0.47J ug/L 01/02/20 20:39 104-51-80.50 0.35 1
sec-Butylbenzene 0.46J ug/L 01/02/20 20:39 135-98-80.50 0.25 1
tert-Butylbenzene ND ug/L 01/02/20 20:39 98-06-60.50 0.25 1
Carbon tetrachloride ND ug/L 01/02/20 20:39 56-23-50.50 0.23 1
Chlorobenzene ND ug/L 01/02/20 20:39 108-90-70.50 0.22 1
Chloroethane ND ug/L 01/02/20 20:39 75-00-31.0 0.58 1
Chloroform ND ug/L 01/02/20 20:39 67-66-30.50 0.35 1
Chloromethane ND ug/L 01/02/20 20:39 74-87-31.0 0.42 1
2-Chlorotoluene ND ug/L 01/02/20 20:39 95-49-80.50 0.21 1
4-Chlorotoluene ND ug/L 01/02/20 20:39 106-43-40.50 0.21 1
1,2-Dibromo-3-chloropropane ND ug/L 01/02/20 20:39 96-12-81.0 0.38 1
Dibromochloromethane ND ug/L 01/02/20 20:39 124-48-10.50 0.40 1
1,2-Dibromoethane (EDB)ND ug/L 01/02/20 20:39 106-93-40.50 0.23 1
Dibromomethane ND ug/L 01/02/20 20:39 74-95-30.50 0.31 1
1,2-Dichlorobenzene ND ug/L 01/02/20 20:39 95-50-10.50 0.24 1
1,3-Dichlorobenzene ND ug/L 01/02/20 20:39 541-73-10.50 0.25 1
1,4-Dichlorobenzene ND ug/L 01/02/20 20:39 106-46-70.50 0.25 1
Dichlorodifluoromethane ND ug/L 01/02/20 20:39 75-71-80.50 0.28 1
1,1-Dichloroethane ND ug/L 01/02/20 20:39 75-34-30.50 0.24 1
1,2-Dichloroethane 7.7 ug/L 01/02/20 20:39 107-06-20.50 0.26 1
1,1-Dichloroethene ND ug/L 01/02/20 20:39 75-35-40.50 0.22 1
cis-1,2-Dichloroethene ND ug/L 01/02/20 20:39 156-59-20.50 0.21 1
trans-1,2-Dichloroethene ND ug/L 01/02/20 20:39 156-60-50.50 0.26 1
1,2-Dichloropropane ND ug/L 01/02/20 20:39 78-87-50.50 0.18 1
1,3-Dichloropropane ND ug/L 01/02/20 20:39 142-28-90.50 0.34 1
2,2-Dichloropropane ND ug/L 01/02/20 20:39 594-20-70.50 0.28 1
1,1-Dichloropropene ND ug/L 01/02/20 20:39 563-58-60.50 0.35 1
cis-1,3-Dichloropropene ND ug/L 01/02/20 20:39 10061-01-50.50 0.36 1
trans-1,3-Dichloropropene ND ug/L 01/02/20 20:39 10061-02-60.50 0.39 1
Diisopropyl ether 4.7 ug/L 01/02/20 20:39 108-20-30.50 0.33 1
Ethylbenzene 2.7 ug/L 01/02/20 20:39 100-41-40.50 0.24 1
Hexachloro-1,3-butadiene ND ug/L 01/02/20 20:39 87-68-32.0 1.2 1
Isopropylbenzene (Cumene)2.7 ug/L 01/02/20 20:39 98-82-80.50 0.24 1
Methylene Chloride ND ug/L 01/02/20 20:39 75-09-22.0 1.5 1
Methyl-tert-butyl ether ND ug/L 01/02/20 20:39 1634-04-40.50 0.44 1
Naphthalene ND ug/L 01/02/20 20:39 91-20-32.0 0.66 1
n-Propylbenzene 0.58 ug/L 01/02/20 20:39 103-65-10.50 0.24 1
Styrene ND ug/L 01/02/20 20:39 100-42-50.50 0.26 1
1,1,1,2-Tetrachloroethane ND ug/L 01/02/20 20:39 630-20-60.50 0.42 1
1,1,2,2-Tetrachloroethane ND ug/L 01/02/20 20:39 79-34-50.50 0.19 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 12 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:DW-1 Lab ID:92458986003 Collected:12/30/19 12:05 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/02/20 20:39 127-18-40.50 0.23 1
Toluene 1.0 ug/L 01/02/20 20:39 108-88-30.50 0.23 1
1,2,3-Trichlorobenzene ND ug/L 01/02/20 20:39 87-61-62.0 0.78 1
1,2,4-Trichlorobenzene ND ug/L 01/02/20 20:39 120-82-12.0 0.44 1
1,1,1-Trichloroethane ND ug/L 01/02/20 20:39 71-55-60.50 0.28 1
1,1,2-Trichloroethane ND ug/L 01/02/20 20:39 79-00-50.50 0.23 1
Trichloroethene ND ug/L 01/02/20 20:39 79-01-60.50 0.23 1
Trichlorofluoromethane ND ug/L 01/02/20 20:39 75-69-41.0 0.34 1
1,2,3-Trichloropropane ND ug/L 01/02/20 20:39 96-18-40.50 0.27 1
1,2,4-Trimethylbenzene 0.37J ug/L 01/02/20 20:39 95-63-60.50 0.19 1
1,3,5-Trimethylbenzene ND ug/L 01/02/20 20:39 108-67-80.50 0.23 1
Vinyl chloride ND ug/L 01/02/20 20:39 75-01-41.0 0.41 1
m&p-Xylene 0.98J ug/L 01/02/20 20:39 179601-23-11.0 0.44 1
o-Xylene 0.73 ug/L 01/02/20 20:39 95-47-60.50 0.24 1
Surrogates
1,2-Dichloroethane-d4 (S)111 %01/02/20 20:39 17060-07-070-130 1
4-Bromofluorobenzene (S)99 %01/02/20 20:39 460-00-470-130 1
Toluene-d8 (S)102 %01/02/20 20:39 2037-26-570-130 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 13 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:MW-4 Lab ID:92458986004 Collected:12/30/19 11:10 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene ND ug/L 01/02/20 20:57 71-43-20.50 0.24 1
Bromobenzene ND ug/L 01/02/20 20:57 108-86-10.50 0.22 1
Bromochloromethane ND ug/L 01/02/20 20:57 74-97-50.50 0.26 1
Bromodichloromethane ND ug/L 01/02/20 20:57 75-27-40.50 0.18 1
Bromoform ND ug/L 01/02/20 20:57 75-25-20.50 0.40 1
Bromomethane ND ug/L 01/02/20 20:57 74-83-95.0 1.7 1
n-Butylbenzene ND ug/L 01/02/20 20:57 104-51-80.50 0.35 1
sec-Butylbenzene ND ug/L 01/02/20 20:57 135-98-80.50 0.25 1
tert-Butylbenzene ND ug/L 01/02/20 20:57 98-06-60.50 0.25 1
Carbon tetrachloride ND ug/L 01/02/20 20:57 56-23-50.50 0.23 1
Chlorobenzene ND ug/L 01/02/20 20:57 108-90-70.50 0.22 1
Chloroethane ND ug/L 01/02/20 20:57 75-00-31.0 0.58 1
Chloroform ND ug/L 01/02/20 20:57 67-66-30.50 0.35 1
Chloromethane ND ug/L 01/02/20 20:57 74-87-31.0 0.42 1
2-Chlorotoluene ND ug/L 01/02/20 20:57 95-49-80.50 0.21 1
4-Chlorotoluene ND ug/L 01/02/20 20:57 106-43-40.50 0.21 1
1,2-Dibromo-3-chloropropane ND ug/L 01/02/20 20:57 96-12-81.0 0.38 1
Dibromochloromethane ND ug/L 01/02/20 20:57 124-48-10.50 0.40 1
1,2-Dibromoethane (EDB)ND ug/L 01/02/20 20:57 106-93-40.50 0.23 1
Dibromomethane ND ug/L 01/02/20 20:57 74-95-30.50 0.31 1
1,2-Dichlorobenzene ND ug/L 01/02/20 20:57 95-50-10.50 0.24 1
1,3-Dichlorobenzene ND ug/L 01/02/20 20:57 541-73-10.50 0.25 1
1,4-Dichlorobenzene ND ug/L 01/02/20 20:57 106-46-70.50 0.25 1
Dichlorodifluoromethane ND ug/L 01/02/20 20:57 75-71-80.50 0.28 1
1,1-Dichloroethane ND ug/L 01/02/20 20:57 75-34-30.50 0.24 1
1,2-Dichloroethane ND ug/L 01/02/20 20:57 107-06-20.50 0.26 1
1,1-Dichloroethene ND ug/L 01/02/20 20:57 75-35-40.50 0.22 1
cis-1,2-Dichloroethene ND ug/L 01/02/20 20:57 156-59-20.50 0.21 1
trans-1,2-Dichloroethene ND ug/L 01/02/20 20:57 156-60-50.50 0.26 1
1,2-Dichloropropane ND ug/L 01/02/20 20:57 78-87-50.50 0.18 1
1,3-Dichloropropane ND ug/L 01/02/20 20:57 142-28-90.50 0.34 1
2,2-Dichloropropane ND ug/L 01/02/20 20:57 594-20-70.50 0.28 1
1,1-Dichloropropene ND ug/L 01/02/20 20:57 563-58-60.50 0.35 1
cis-1,3-Dichloropropene ND ug/L 01/02/20 20:57 10061-01-50.50 0.36 1
trans-1,3-Dichloropropene ND ug/L 01/02/20 20:57 10061-02-60.50 0.39 1
Diisopropyl ether ND ug/L 01/02/20 20:57 108-20-30.50 0.33 1
Ethylbenzene ND ug/L 01/02/20 20:57 100-41-40.50 0.24 1
Hexachloro-1,3-butadiene ND ug/L 01/02/20 20:57 87-68-32.0 1.2 1
Isopropylbenzene (Cumene)ND ug/L 01/02/20 20:57 98-82-80.50 0.24 1
Methylene Chloride ND ug/L 01/02/20 20:57 75-09-22.0 1.5 1
Methyl-tert-butyl ether ND ug/L 01/02/20 20:57 1634-04-40.50 0.44 1
Naphthalene ND ug/L 01/02/20 20:57 91-20-32.0 0.66 1
n-Propylbenzene ND ug/L 01/02/20 20:57 103-65-10.50 0.24 1
Styrene ND ug/L 01/02/20 20:57 100-42-50.50 0.26 1
1,1,1,2-Tetrachloroethane ND ug/L 01/02/20 20:57 630-20-60.50 0.42 1
1,1,2,2-Tetrachloroethane ND ug/L 01/02/20 20:57 79-34-50.50 0.19 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 14 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:MW-4 Lab ID:92458986004 Collected:12/30/19 11:10 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/02/20 20:57 127-18-40.50 0.23 1
Toluene ND ug/L 01/02/20 20:57 108-88-30.50 0.23 1
1,2,3-Trichlorobenzene ND ug/L 01/02/20 20:57 87-61-62.0 0.78 1
1,2,4-Trichlorobenzene ND ug/L 01/02/20 20:57 120-82-12.0 0.44 1
1,1,1-Trichloroethane ND ug/L 01/02/20 20:57 71-55-60.50 0.28 1
1,1,2-Trichloroethane ND ug/L 01/02/20 20:57 79-00-50.50 0.23 1
Trichloroethene ND ug/L 01/02/20 20:57 79-01-60.50 0.23 1
Trichlorofluoromethane ND ug/L 01/02/20 20:57 75-69-41.0 0.34 1
1,2,3-Trichloropropane ND ug/L 01/02/20 20:57 96-18-40.50 0.27 1
1,2,4-Trimethylbenzene ND ug/L 01/02/20 20:57 95-63-60.50 0.19 1
1,3,5-Trimethylbenzene ND ug/L 01/02/20 20:57 108-67-80.50 0.23 1
Vinyl chloride ND ug/L 01/02/20 20:57 75-01-41.0 0.41 1
m&p-Xylene ND ug/L 01/02/20 20:57 179601-23-11.0 0.44 1
o-Xylene ND ug/L 01/02/20 20:57 95-47-60.50 0.24 1
Surrogates
1,2-Dichloroethane-d4 (S)102 %01/02/20 20:57 17060-07-070-130 1
4-Bromofluorobenzene (S)97 %01/02/20 20:57 460-00-470-130 1
Toluene-d8 (S)103 %01/02/20 20:57 2037-26-570-130 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 15 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:WSW-1 Lab ID:92458986005 Collected:12/30/19 13:00 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene 0.52 ug/L 01/04/20 02:28 71-43-20.50 0.24 1
Bromobenzene ND ug/L 01/04/20 02:28 108-86-10.50 0.22 1
Bromochloromethane ND ug/L 01/04/20 02:28 74-97-50.50 0.26 1
Bromodichloromethane ND ug/L 01/04/20 02:28 75-27-40.50 0.18 1
Bromoform ND ug/L 01/04/20 02:28 75-25-20.50 0.40 1
Bromomethane ND ug/L 01/04/20 02:28 74-83-95.0 1.7 1
n-Butylbenzene ND ug/L 01/04/20 02:28 104-51-80.50 0.35 1
sec-Butylbenzene ND ug/L 01/04/20 02:28 135-98-80.50 0.25 1
tert-Butylbenzene ND ug/L 01/04/20 02:28 98-06-60.50 0.25 1
Carbon tetrachloride ND ug/L 01/04/20 02:28 56-23-50.50 0.23 1
Chlorobenzene ND ug/L 01/04/20 02:28 108-90-70.50 0.22 1
Chloroethane ND ug/L 01/04/20 02:28 75-00-31.0 0.58 1
Chloroform ND ug/L 01/04/20 02:28 67-66-30.50 0.35 1
Chloromethane ND ug/L 01/04/20 02:28 74-87-31.0 0.42 1
2-Chlorotoluene ND ug/L 01/04/20 02:28 95-49-80.50 0.21 1
4-Chlorotoluene ND ug/L 01/04/20 02:28 106-43-40.50 0.21 1
1,2-Dibromo-3-chloropropane ND ug/L 01/04/20 02:28 96-12-81.0 0.38 1
Dibromochloromethane ND ug/L 01/04/20 02:28 124-48-10.50 0.40 1
1,2-Dibromoethane (EDB)ND ug/L 01/04/20 02:28 106-93-40.50 0.23 1
Dibromomethane ND ug/L 01/04/20 02:28 74-95-30.50 0.31 1
1,2-Dichlorobenzene ND ug/L 01/04/20 02:28 95-50-10.50 0.24 1
1,3-Dichlorobenzene ND ug/L 01/04/20 02:28 541-73-10.50 0.25 1
1,4-Dichlorobenzene ND ug/L 01/04/20 02:28 106-46-70.50 0.25 1
Dichlorodifluoromethane ND ug/L 01/04/20 02:28 75-71-80.50 0.28 1
1,1-Dichloroethane ND ug/L 01/04/20 02:28 75-34-30.50 0.24 1
1,2-Dichloroethane ND ug/L 01/04/20 02:28 107-06-20.50 0.26 1
1,1-Dichloroethene ND ug/L 01/04/20 02:28 75-35-40.50 0.22 1
cis-1,2-Dichloroethene ND ug/L 01/04/20 02:28 156-59-20.50 0.21 1
trans-1,2-Dichloroethene ND ug/L 01/04/20 02:28 156-60-50.50 0.26 1
1,2-Dichloropropane ND ug/L 01/04/20 02:28 78-87-50.50 0.18 1
1,3-Dichloropropane ND ug/L 01/04/20 02:28 142-28-90.50 0.34 1
2,2-Dichloropropane ND ug/L 01/04/20 02:28 594-20-70.50 0.28 1
1,1-Dichloropropene ND ug/L 01/04/20 02:28 563-58-60.50 0.35 1
cis-1,3-Dichloropropene ND ug/L 01/04/20 02:28 10061-01-50.50 0.36 1
trans-1,3-Dichloropropene ND ug/L 01/04/20 02:28 10061-02-60.50 0.39 1
Diisopropyl ether ND ug/L 01/04/20 02:28 108-20-30.50 0.33 1
Ethylbenzene ND ug/L 01/04/20 02:28 100-41-40.50 0.24 1
Hexachloro-1,3-butadiene ND ug/L 01/04/20 02:28 87-68-32.0 1.2 1
Isopropylbenzene (Cumene)ND ug/L 01/04/20 02:28 98-82-80.50 0.24 1
Methylene Chloride ND ug/L 01/04/20 02:28 75-09-22.0 1.5 1
Methyl-tert-butyl ether ND ug/L 01/04/20 02:28 1634-04-40.50 0.44 1
Naphthalene ND ug/L 01/04/20 02:28 91-20-32.0 0.66 1
n-Propylbenzene ND ug/L 01/04/20 02:28 103-65-10.50 0.24 1
Styrene ND ug/L 01/04/20 02:28 100-42-50.50 0.26 1
1,1,1,2-Tetrachloroethane ND ug/L 01/04/20 02:28 630-20-60.50 0.42 1
1,1,2,2-Tetrachloroethane ND ug/L 01/04/20 02:28 79-34-50.50 0.19 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 16 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:WSW-1 Lab ID:92458986005 Collected:12/30/19 13:00 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/04/20 02:28 127-18-40.50 0.23 1
Toluene ND ug/L 01/04/20 02:28 108-88-30.50 0.23 1
1,2,3-Trichlorobenzene ND ug/L 01/04/20 02:28 87-61-62.0 0.78 1
1,2,4-Trichlorobenzene ND ug/L 01/04/20 02:28 120-82-12.0 0.44 1
1,1,1-Trichloroethane ND ug/L 01/04/20 02:28 71-55-60.50 0.28 1
1,1,2-Trichloroethane ND ug/L 01/04/20 02:28 79-00-50.50 0.23 1
Trichloroethene ND ug/L 01/04/20 02:28 79-01-60.50 0.23 1
Trichlorofluoromethane ND ug/L 01/04/20 02:28 75-69-41.0 0.34 1
1,2,3-Trichloropropane ND ug/L 01/04/20 02:28 96-18-40.50 0.27 1
1,2,4-Trimethylbenzene ND ug/L 01/04/20 02:28 95-63-60.50 0.19 1
1,3,5-Trimethylbenzene ND ug/L 01/04/20 02:28 108-67-80.50 0.23 1
Vinyl chloride ND ug/L 01/04/20 02:28 75-01-41.0 0.41 1
m&p-Xylene ND ug/L 01/04/20 02:28 179601-23-11.0 0.44 1
o-Xylene ND ug/L 01/04/20 02:28 95-47-60.50 0.24 1
Surrogates
1,2-Dichloroethane-d4 (S)100 %01/04/20 02:28 17060-07-070-130 1
4-Bromofluorobenzene (S)101 %01/04/20 02:28 460-00-470-130 1
Toluene-d8 (S)104 %01/04/20 02:28 2037-26-570-130 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 17 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:WSW-4 Lab ID:92458986006 Collected:12/30/19 13:05 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Benzene ND ug/L 01/04/20 02:11 71-43-20.50 0.24 1
Bromobenzene ND ug/L 01/04/20 02:11 108-86-10.50 0.22 1
Bromochloromethane ND ug/L 01/04/20 02:11 74-97-50.50 0.26 1
Bromodichloromethane ND ug/L 01/04/20 02:11 75-27-40.50 0.18 1
Bromoform ND ug/L 01/04/20 02:11 75-25-20.50 0.40 1
Bromomethane ND ug/L 01/04/20 02:11 74-83-95.0 1.7 1
n-Butylbenzene ND ug/L 01/04/20 02:11 104-51-80.50 0.35 1
sec-Butylbenzene ND ug/L 01/04/20 02:11 135-98-80.50 0.25 1
tert-Butylbenzene ND ug/L 01/04/20 02:11 98-06-60.50 0.25 1
Carbon tetrachloride ND ug/L 01/04/20 02:11 56-23-50.50 0.23 1
Chlorobenzene ND ug/L 01/04/20 02:11 108-90-70.50 0.22 1
Chloroethane ND ug/L 01/04/20 02:11 75-00-31.0 0.58 1
Chloroform ND ug/L 01/04/20 02:11 67-66-30.50 0.35 1
Chloromethane ND ug/L 01/04/20 02:11 74-87-31.0 0.42 1
2-Chlorotoluene ND ug/L 01/04/20 02:11 95-49-80.50 0.21 1
4-Chlorotoluene ND ug/L 01/04/20 02:11 106-43-40.50 0.21 1
1,2-Dibromo-3-chloropropane ND ug/L 01/04/20 02:11 96-12-81.0 0.38 1
Dibromochloromethane ND ug/L 01/04/20 02:11 124-48-10.50 0.40 1
1,2-Dibromoethane (EDB)ND ug/L 01/04/20 02:11 106-93-40.50 0.23 1
Dibromomethane ND ug/L 01/04/20 02:11 74-95-30.50 0.31 1
1,2-Dichlorobenzene ND ug/L 01/04/20 02:11 95-50-10.50 0.24 1
1,3-Dichlorobenzene ND ug/L 01/04/20 02:11 541-73-10.50 0.25 1
1,4-Dichlorobenzene ND ug/L 01/04/20 02:11 106-46-70.50 0.25 1
Dichlorodifluoromethane ND ug/L 01/04/20 02:11 75-71-80.50 0.28 1
1,1-Dichloroethane ND ug/L 01/04/20 02:11 75-34-30.50 0.24 1
1,2-Dichloroethane ND ug/L 01/04/20 02:11 107-06-20.50 0.26 1
1,1-Dichloroethene ND ug/L 01/04/20 02:11 75-35-40.50 0.22 1
cis-1,2-Dichloroethene ND ug/L 01/04/20 02:11 156-59-20.50 0.21 1
trans-1,2-Dichloroethene ND ug/L 01/04/20 02:11 156-60-50.50 0.26 1
1,2-Dichloropropane ND ug/L 01/04/20 02:11 78-87-50.50 0.18 1
1,3-Dichloropropane ND ug/L 01/04/20 02:11 142-28-90.50 0.34 1
2,2-Dichloropropane ND ug/L 01/04/20 02:11 594-20-70.50 0.28 1
1,1-Dichloropropene ND ug/L 01/04/20 02:11 563-58-60.50 0.35 1
cis-1,3-Dichloropropene ND ug/L 01/04/20 02:11 10061-01-50.50 0.36 1
trans-1,3-Dichloropropene ND ug/L 01/04/20 02:11 10061-02-60.50 0.39 1
Diisopropyl ether ND ug/L 01/04/20 02:11 108-20-30.50 0.33 1
Ethylbenzene ND ug/L 01/04/20 02:11 100-41-40.50 0.24 1
Hexachloro-1,3-butadiene ND ug/L 01/04/20 02:11 87-68-32.0 1.2 1
Isopropylbenzene (Cumene)ND ug/L 01/04/20 02:11 98-82-80.50 0.24 1
Methylene Chloride ND ug/L 01/04/20 02:11 75-09-22.0 1.5 1
Methyl-tert-butyl ether ND ug/L 01/04/20 02:11 1634-04-40.50 0.44 1
Naphthalene ND ug/L 01/04/20 02:11 91-20-32.0 0.66 1
n-Propylbenzene ND ug/L 01/04/20 02:11 103-65-10.50 0.24 1
Styrene ND ug/L 01/04/20 02:11 100-42-50.50 0.26 1
1,1,1,2-Tetrachloroethane ND ug/L 01/04/20 02:11 630-20-60.50 0.42 1
1,1,2,2-Tetrachloroethane ND ug/L 01/04/20 02:11 79-34-50.50 0.19 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 18 of 34
#=AR#
ANALYTICAL RESULTS
Pace Project No.:
Project:
92458986
Burcham Property
Sample:WSW-4 Lab ID:92458986006 Collected:12/30/19 13:05 Received:12/31/19 09:51 Matrix:Water
Parameters Results Units DF Prepared Analyzed CAS No.QualMDLLimit
Report
Analytical Method: SM 6200B6200B MSV
Tetrachloroethene ND ug/L 01/04/20 02:11 127-18-40.50 0.23 1
Toluene ND ug/L 01/04/20 02:11 108-88-30.50 0.23 1
1,2,3-Trichlorobenzene ND ug/L 01/04/20 02:11 87-61-62.0 0.78 1
1,2,4-Trichlorobenzene ND ug/L 01/04/20 02:11 120-82-12.0 0.44 1
1,1,1-Trichloroethane ND ug/L 01/04/20 02:11 71-55-60.50 0.28 1
1,1,2-Trichloroethane ND ug/L 01/04/20 02:11 79-00-50.50 0.23 1
Trichloroethene ND ug/L 01/04/20 02:11 79-01-60.50 0.23 1
Trichlorofluoromethane ND ug/L 01/04/20 02:11 75-69-41.0 0.34 1
1,2,3-Trichloropropane ND ug/L 01/04/20 02:11 96-18-40.50 0.27 1
1,2,4-Trimethylbenzene ND ug/L 01/04/20 02:11 95-63-60.50 0.19 1
1,3,5-Trimethylbenzene ND ug/L 01/04/20 02:11 108-67-80.50 0.23 1
Vinyl chloride ND ug/L 01/04/20 02:11 75-01-41.0 0.41 1
m&p-Xylene ND ug/L 01/04/20 02:11 179601-23-11.0 0.44 1
o-Xylene ND ug/L 01/04/20 02:11 95-47-60.50 0.24 1
Surrogates
1,2-Dichloroethane-d4 (S)100 %01/04/20 02:11 17060-07-070-130 1
4-Bromofluorobenzene (S)102 %01/04/20 02:11 460-00-470-130 1
Toluene-d8 (S)104 %01/04/20 02:11 2037-26-570-130 1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 19 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
QC Batch:
QC Batch Method:
Analysis Method:
Analysis Description:
517653
SM 6200B
SM 6200B
6200B MSV
Associated Lab Samples:92458986001, 92458986003, 92458986004
Parameter Units
Blank
Result
Reporting
Limit Qualifiers
METHOD BLANK:2771442
Associated Lab Samples:92458986001, 92458986003, 92458986004
Matrix:Water
AnalyzedMDL
1,1,1,2-Tetrachloroethane ug/L ND 0.50 01/02/20 18:510.42
1,1,1-Trichloroethane ug/L ND 0.50 01/02/20 18:510.28
1,1,2,2-Tetrachloroethane ug/L ND 0.50 01/02/20 18:510.19
1,1,2-Trichloroethane ug/L ND 0.50 01/02/20 18:510.23
1,1-Dichloroethane ug/L ND 0.50 01/02/20 18:510.24
1,1-Dichloroethene ug/L ND 0.50 01/02/20 18:510.22
1,1-Dichloropropene ug/L ND 0.50 01/02/20 18:510.35
1,2,3-Trichlorobenzene ug/L ND 2.0 01/02/20 18:510.78
1,2,3-Trichloropropane ug/L ND 0.50 01/02/20 18:510.27
1,2,4-Trichlorobenzene ug/L ND 2.0 01/02/20 18:510.44
1,2,4-Trimethylbenzene ug/L ND 0.50 01/02/20 18:510.19
1,2-Dibromo-3-chloropropane ug/L ND 1.0 01/02/20 18:510.38
1,2-Dibromoethane (EDB)ug/L ND 0.50 01/02/20 18:510.23
1,2-Dichlorobenzene ug/L ND 0.50 01/02/20 18:510.24
1,2-Dichloroethane ug/L ND 0.50 01/02/20 18:510.26
1,2-Dichloropropane ug/L ND 0.50 01/02/20 18:510.18
1,3,5-Trimethylbenzene ug/L ND 0.50 01/02/20 18:510.23
1,3-Dichlorobenzene ug/L ND 0.50 01/02/20 18:510.25
1,3-Dichloropropane ug/L ND 0.50 01/02/20 18:510.34
1,4-Dichlorobenzene ug/L ND 0.50 01/02/20 18:510.25
2,2-Dichloropropane ug/L ND 0.50 01/02/20 18:510.28
2-Chlorotoluene ug/L ND 0.50 01/02/20 18:510.21
4-Chlorotoluene ug/L ND 0.50 01/02/20 18:510.21
Benzene ug/L ND 0.50 01/02/20 18:510.24
Bromobenzene ug/L ND 0.50 01/02/20 18:510.22
Bromochloromethane ug/L ND 0.50 01/02/20 18:510.26
Bromodichloromethane ug/L ND 0.50 01/02/20 18:510.18
Bromoform ug/L ND 0.50 01/02/20 18:510.40
Bromomethane ug/L ND 5.0 01/02/20 18:511.7
Carbon tetrachloride ug/L ND 0.50 01/02/20 18:510.23
Chlorobenzene ug/L ND 0.50 01/02/20 18:510.22
Chloroethane ug/L ND 1.0 01/02/20 18:510.58
Chloroform ug/L ND 0.50 01/02/20 18:510.35
Chloromethane ug/L ND 1.0 01/02/20 18:510.42
cis-1,2-Dichloroethene ug/L ND 0.50 01/02/20 18:510.21
cis-1,3-Dichloropropene ug/L ND 0.50 01/02/20 18:510.36
Dibromochloromethane ug/L ND 0.50 01/02/20 18:510.40
Dibromomethane ug/L ND 0.50 01/02/20 18:510.31
Dichlorodifluoromethane ug/L ND 0.50 01/02/20 18:510.28
Diisopropyl ether ug/L ND 0.50 01/02/20 18:510.33
Ethylbenzene ug/L ND 0.50 01/02/20 18:510.24
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 20 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
Blank
Result
Reporting
Limit Qualifiers
METHOD BLANK:2771442
Associated Lab Samples:92458986001, 92458986003, 92458986004
Matrix:Water
AnalyzedMDL
Hexachloro-1,3-butadiene ug/L ND 2.0 01/02/20 18:511.2
Isopropylbenzene (Cumene)ug/L ND 0.50 01/02/20 18:510.24
m&p-Xylene ug/L ND 1.0 01/02/20 18:510.44
Methyl-tert-butyl ether ug/L ND 0.50 01/02/20 18:510.44
Methylene Chloride ug/L ND 2.0 01/02/20 18:511.5
n-Butylbenzene ug/L ND 0.50 01/02/20 18:510.35
n-Propylbenzene ug/L ND 0.50 01/02/20 18:510.24
Naphthalene ug/L ND 2.0 01/02/20 18:510.66
o-Xylene ug/L ND 0.50 01/02/20 18:510.24
sec-Butylbenzene ug/L ND 0.50 01/02/20 18:510.25
Styrene ug/L ND 0.50 01/02/20 18:510.26
tert-Butylbenzene ug/L ND 0.50 01/02/20 18:510.25
Tetrachloroethene ug/L ND 0.50 01/02/20 18:510.23
Toluene ug/L ND 0.50 01/02/20 18:510.23
trans-1,2-Dichloroethene ug/L ND 0.50 01/02/20 18:510.26
trans-1,3-Dichloropropene ug/L ND 0.50 01/02/20 18:510.39
Trichloroethene ug/L ND 0.50 01/02/20 18:510.23
Trichlorofluoromethane ug/L ND 1.0 01/02/20 18:510.34
Vinyl chloride ug/L ND 1.0 01/02/20 18:510.41
1,2-Dichloroethane-d4 (S)%103 70-130 01/02/20 18:51
4-Bromofluorobenzene (S)%99 70-130 01/02/20 18:51
Toluene-d8 (S)%102 70-130 01/02/20 18:51
Parameter Units
LCS
Result
% Rec
Limits Qualifiers% RecConc.
2771443LABORATORY CONTROL SAMPLE:
LCSSpike
1,1,1,2-Tetrachloroethane ug/L 51.850 104 60-140
1,1,1-Trichloroethane ug/L 54.250 108 60-140
1,1,2,2-Tetrachloroethane ug/L 52.050 104 60-140
1,1,2-Trichloroethane ug/L 50.550 101 60-140
1,1-Dichloroethane ug/L 53.050 106 60-140
1,1-Dichloroethene ug/L 54.450 109 60-140
1,1-Dichloropropene ug/L 58.750 117 60-140
1,2,3-Trichlorobenzene ug/L 55.750 111 60-140
1,2,3-Trichloropropane ug/L 52.250 104 60-140
1,2,4-Trichlorobenzene ug/L 53.750 107 60-140
1,2,4-Trimethylbenzene ug/L 52.950 106 60-140
1,2-Dibromo-3-chloropropane ug/L 53.150 106 60-140
1,2-Dibromoethane (EDB)ug/L 51.950 104 60-140
1,2-Dichlorobenzene ug/L 52.250 104 60-140
1,2-Dichloroethane ug/L 49.750 99 60-140
1,2-Dichloropropane ug/L 52.250 104 60-140
1,3,5-Trimethylbenzene ug/L 52.550 105 60-140
1,3-Dichlorobenzene ug/L 51.350 103 60-140
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 21 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
LCS
Result
% Rec
Limits Qualifiers% RecConc.
2771443LABORATORY CONTROL SAMPLE:
LCSSpike
1,3-Dichloropropane ug/L 54.250 108 60-140
1,4-Dichlorobenzene ug/L 52.050 104 60-140
2,2-Dichloropropane ug/L 60.250 120 60-140
2-Chlorotoluene ug/L 52.050 104 60-140
4-Chlorotoluene ug/L 52.250 104 60-140
Benzene ug/L 52.850 106 60-140
Bromobenzene ug/L 51.650 103 60-140
Bromochloromethane ug/L 48.850 98 60-140
Bromodichloromethane ug/L 53.850 108 60-140
Bromoform ug/L 52.450 105 60-140
Bromomethane ug/L 61.550 123 60-140
Carbon tetrachloride ug/L 54.250 108 60-140
Chlorobenzene ug/L 50.650 101 60-140
Chloroethane ug/L 37.250 74 60-140
Chloroform ug/L 50.650 101 60-140
Chloromethane ug/L 37.050 74 60-140
cis-1,2-Dichloroethene ug/L 51.750 103 60-140
cis-1,3-Dichloropropene ug/L 56.250 112 60-140
Dibromochloromethane ug/L 53.250 106 60-140
Dibromomethane ug/L 47.050 94 60-140
Dichlorodifluoromethane ug/L 48.350 97 60-140
Diisopropyl ether ug/L 51.750 103 60-140
Ethylbenzene ug/L 50.850 102 60-140
Hexachloro-1,3-butadiene ug/L 52.350 105 60-140
Isopropylbenzene (Cumene)ug/L 51.750 103 60-140
m&p-Xylene ug/L 103100 103 60-140
Methyl-tert-butyl ether ug/L 54.450 109 60-140
Methylene Chloride ug/L 48.650 97 60-140
n-Butylbenzene ug/L 55.850 112 60-140
n-Propylbenzene ug/L 51.350 103 60-140
Naphthalene ug/L 55.450 111 60-140
o-Xylene ug/L 50.650 101 60-140
sec-Butylbenzene ug/L 52.850 106 60-140
Styrene ug/L 52.450 105 60-140
tert-Butylbenzene ug/L 44.650 89 60-140
Tetrachloroethene ug/L 49.850 100 60-140
Toluene ug/L 49.350 99 60-140
trans-1,2-Dichloroethene ug/L 52.850 106 60-140
trans-1,3-Dichloropropene ug/L 55.850 112 60-140
Trichloroethene ug/L 50.550 101 60-140
Trichlorofluoromethane ug/L 46.950 94 60-140
Vinyl chloride ug/L 48.250 96 60-140
1,2-Dichloroethane-d4 (S)%103 70-130
4-Bromofluorobenzene (S)%101 70-130
Toluene-d8 (S)%100 70-130
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 22 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
MS
Result
% Rec
Limits Qual% RecConc.
2771444MATRIX SPIKE & MATRIX SPIKE DUPLICATE:
MSSpike
Result
92458856005
2771445
MSD
Result
MSD
% Rec RPD RPD
Max
MSDMS
Spike
Conc.
1,1,1,2-Tetrachloroethane ug/L 400 106 60-140112 5 30400<8.4 425 447
1,1,1-Trichloroethane ug/L 400 115 60-140118 3 30400<5.6 460 473
1,1,2,2-Tetrachloroethane ug/L 400 104 60-140109 5 30400<3.9 415 438
1,1,2-Trichloroethane ug/L 400 106 60-140111 5 30400<4.6 424 443
1,1-Dichloroethane ug/L 400 117 60-140118 1 30400<4.9 467 471
1,1-Dichloroethene ug/L 400 122 60-140123 0 30400<4.4 488 490
1,1-Dichloropropene ug/L 400 128 60-140129 1 30400<7.0 511 514
1,2,3-Trichlorobenzene ug/L 400 89 60-140104 15 30400<15.6 357 414
1,2,3-Trichloropropane ug/L 400 105 60-140112 7 30400<5.4 419 449
1,2,4-Trichlorobenzene ug/L 400 92 60-140104 12 30400<8.7 368 417
1,2,4-Trimethylbenzene ug/L 400 104 60-140110 4 3040033.2 451 471
1,2-Dibromo-3-
chloropropane ug/L 400 97 60-140107 9 30400<7.7 390 427
1,2-Dibromoethane (EDB)ug/L 400 101 60-140111 9 30400<4.6 406 444
1,2-Dichlorobenzene ug/L 400 101 60-140107 6 30400<4.8 405 429
1,2-Dichloroethane ug/L 400 101 60-140106 5 304008.8J 412 432
1,2-Dichloropropane ug/L 400 114 60-140115 1 30400<3.7 456 460
1,3,5-Trimethylbenzene ug/L 400 111 60-140115 4 30400<4.5 444 461
1,3-Dichlorobenzene ug/L 400 101 60-140107 6 30400<5.0 405 430
1,3-Dichloropropane ug/L 400 109 60-140114 5 30400<6.8 434 454
1,4-Dichlorobenzene ug/L 400 103 60-140108 5 30400<5.0 411 432
2,2-Dichloropropane ug/L 400 109 60-140114 5 30400<5.6 436 458
2-Chlorotoluene ug/L 400 107 60-140112 5 30400<4.1 427 447
4-Chlorotoluene ug/L 400 106 60-140111 4 30400<4.1 424 443
Benzene ug/L 400 116 60-140116 0 30400115578580
Bromobenzene ug/L 400 105 60-140111 5 30400<4.3 422 443
Bromochloromethane ug/L 400 108 60-140107 1 30400<5.2 433 429
Bromodichloromethane ug/L 400 112 60-140115 3 30400<3.7 448 460
Bromoform ug/L 400 99 60-140105 6 30400<8.1 394 419
Bromomethane ug/L R14008860-140127 36 30400<34.4 351 506
Carbon tetrachloride ug/L 400 119 60-140124 4 30400<4.6 478 496
Chlorobenzene ug/L 400 106 60-140111 5 30400<4.5 422 442
Chloroethane ug/L 400 103 60-140103 1 30400<11.7 410 413
Chloroform ug/L 400 113 60-140113 0 30400<7.1 453 452
Chloromethane ug/L 400 76 60-14078 2 30400<8.3 305 312
cis-1,2-Dichloroethene ug/L 400 112 60-140115 2 30400<4.1 450 459
cis-1,3-Dichloropropene ug/L 400 112 60-140118 5 30400<7.1 450 472
Dibromochloromethane ug/L 400 101 60-140108 7 30400<8.0 405 433
Dibromomethane ug/L 400 104 60-140103 1 30400<6.2 416 412
Dichlorodifluoromethane ug/L 400 110 60-140111 1 30400<5.7 440 442
Diisopropyl ether ug/L 400 107 60-140108 1 3040096.0 524 530
Ethylbenzene ug/L 400 106 60-140112 5 304008.6J 431 455
Hexachloro-1,3-butadiene ug/L 400 101 60-140108 6 30400<24.0 405 431
Isopropylbenzene(Cumene)ug/L 400 109 60-140114 4 30400<4.8 436 455
m&p-Xylene ug/L 800 106 60-140111 5 3080034.3 879 925
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 23 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
MS
Result
% Rec
Limits Qual% RecConc.
2771444MATRIX SPIKE & MATRIX SPIKE DUPLICATE:
MSSpike
Result
92458856005
2771445
MSD
Result
MSD
% Rec RPD RPD
Max
MSDMS
Spike
Conc.
Methyl-tert-butyl ether ug/L M140013760-140143 1 30400283033803410
Methylene Chloride ug/L 400 99 60-140102 3 30400<30.0 396 408
n-Butylbenzene ug/L 400 108 60-140117 8 30400<7.1 430 467
n-Propylbenzene ug/L 400 107 60-140113 5 30400<4.8 429 451
Naphthalene ug/L 400 76 60-14089 14 3040075.5 378 433
o-Xylene ug/L 400 106 60-140112 5 3040042.8 466 489
sec-Butylbenzene ug/L 400 112 60-140116 4 30400<4.9 446 463
Styrene ug/L 400 103 60-140109 6 30400<5.1 412 435
tert-Butylbenzene ug/L 400 95 60-14099 4 30400<5.0 381 396
Tetrachloroethene ug/L 400 103 60-140110 7 30400<4.6 412 441
Toluene ug/L 400 109 60-140111 1 304006.1J 444 449
trans-1,2-Dichloroethene ug/L 400 116 60-140121 4 30400<5.1 464 482
trans-1,3-Dichloropropene ug/L 400 111 60-140113 2 30400<7.9 446 454
Trichloroethene ug/L 400 113 60-140115 2 30400<4.6 451 458
Trichlorofluoromethane ug/L 400 106 60-140107 1 30400<6.7 425 428
Vinyl chloride ug/L 400 107 60-140109 2 30400<8.1 427 436
1,2-Dichloroethane-d4 (S)%105 70-130102
4-Bromofluorobenzene (S)%99 70-130101
Toluene-d8 (S)%101 70-130101
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 24 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
QC Batch:
QC Batch Method:
Analysis Method:
Analysis Description:
517750
SM 6200B
SM 6200B
6200B MSV
Associated Lab Samples:92458986002, 92458986005, 92458986006
Parameter Units
Blank
Result
Reporting
Limit Qualifiers
METHOD BLANK:2771744
Associated Lab Samples:92458986002, 92458986005, 92458986006
Matrix:Water
AnalyzedMDL
1,1,1,2-Tetrachloroethane ug/L ND 0.50 01/03/20 23:350.42
1,1,1-Trichloroethane ug/L ND 0.50 01/03/20 23:350.28
1,1,2,2-Tetrachloroethane ug/L ND 0.50 01/03/20 23:350.19
1,1,2-Trichloroethane ug/L ND 0.50 01/03/20 23:350.23
1,1-Dichloroethane ug/L ND 0.50 01/03/20 23:350.24
1,1-Dichloroethene ug/L ND 0.50 01/03/20 23:350.22
1,1-Dichloropropene ug/L ND 0.50 01/03/20 23:350.35
1,2,3-Trichlorobenzene ug/L ND 2.0 01/03/20 23:350.78
1,2,3-Trichloropropane ug/L ND 0.50 01/03/20 23:350.27
1,2,4-Trichlorobenzene ug/L ND 2.0 01/03/20 23:350.44
1,2,4-Trimethylbenzene ug/L ND 0.50 01/03/20 23:350.19
1,2-Dibromo-3-chloropropane ug/L ND 1.0 01/03/20 23:350.38
1,2-Dibromoethane (EDB)ug/L ND 0.50 01/03/20 23:350.23
1,2-Dichlorobenzene ug/L ND 0.50 01/03/20 23:350.24
1,2-Dichloroethane ug/L ND 0.50 01/03/20 23:350.26
1,2-Dichloropropane ug/L ND 0.50 01/03/20 23:350.18
1,3,5-Trimethylbenzene ug/L ND 0.50 01/03/20 23:350.23
1,3-Dichlorobenzene ug/L ND 0.50 01/03/20 23:350.25
1,3-Dichloropropane ug/L ND 0.50 01/03/20 23:350.34
1,4-Dichlorobenzene ug/L ND 0.50 01/03/20 23:350.25
2,2-Dichloropropane ug/L ND 0.50 01/03/20 23:350.28
2-Chlorotoluene ug/L ND 0.50 01/03/20 23:350.21
4-Chlorotoluene ug/L ND 0.50 01/03/20 23:350.21
Benzene ug/L ND 0.50 01/03/20 23:350.24
Bromobenzene ug/L ND 0.50 01/03/20 23:350.22
Bromochloromethane ug/L ND 0.50 01/03/20 23:350.26
Bromodichloromethane ug/L ND 0.50 01/03/20 23:350.18
Bromoform ug/L ND 0.50 01/03/20 23:350.40
Bromomethane ug/L ND 5.0 01/03/20 23:351.7
Carbon tetrachloride ug/L ND 0.50 01/03/20 23:350.23
Chlorobenzene ug/L ND 0.50 01/03/20 23:350.22
Chloroethane ug/L ND 1.0 01/03/20 23:350.58
Chloroform ug/L ND 0.50 01/03/20 23:350.35
Chloromethane ug/L ND 1.0 01/03/20 23:350.42
cis-1,2-Dichloroethene ug/L ND 0.50 01/03/20 23:350.21
cis-1,3-Dichloropropene ug/L ND 0.50 01/03/20 23:350.36
Dibromochloromethane ug/L ND 0.50 01/03/20 23:350.40
Dibromomethane ug/L ND 0.50 01/03/20 23:350.31
Dichlorodifluoromethane ug/L ND 0.50 01/03/20 23:350.28
Diisopropyl ether ug/L ND 0.50 01/03/20 23:350.33
Ethylbenzene ug/L ND 0.50 01/03/20 23:350.24
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 25 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
Blank
Result
Reporting
Limit Qualifiers
METHOD BLANK:2771744
Associated Lab Samples:92458986002, 92458986005, 92458986006
Matrix:Water
AnalyzedMDL
Hexachloro-1,3-butadiene ug/L ND 2.0 01/03/20 23:351.2
Isopropylbenzene (Cumene)ug/L ND 0.50 01/03/20 23:350.24
m&p-Xylene ug/L ND 1.0 01/03/20 23:350.44
Methyl-tert-butyl ether ug/L ND 0.50 01/03/20 23:350.44
Methylene Chloride ug/L ND 2.0 01/03/20 23:351.5
n-Butylbenzene ug/L ND 0.50 01/03/20 23:350.35
n-Propylbenzene ug/L ND 0.50 01/03/20 23:350.24
Naphthalene ug/L ND 2.0 01/03/20 23:350.66
o-Xylene ug/L ND 0.50 01/03/20 23:350.24
sec-Butylbenzene ug/L ND 0.50 01/03/20 23:350.25
Styrene ug/L ND 0.50 01/03/20 23:350.26
tert-Butylbenzene ug/L ND 0.50 01/03/20 23:350.25
Tetrachloroethene ug/L ND 0.50 01/03/20 23:350.23
Toluene ug/L ND 0.50 01/03/20 23:350.23
trans-1,2-Dichloroethene ug/L ND 0.50 01/03/20 23:350.26
trans-1,3-Dichloropropene ug/L ND 0.50 01/03/20 23:350.39
Trichloroethene ug/L ND 0.50 01/03/20 23:350.23
Trichlorofluoromethane ug/L ND 1.0 01/03/20 23:350.34
Vinyl chloride ug/L ND 1.0 01/03/20 23:350.41
1,2-Dichloroethane-d4 (S)%100 70-130 01/03/20 23:35
4-Bromofluorobenzene (S)%104 70-130 01/03/20 23:35
Toluene-d8 (S)%102 70-130 01/03/20 23:35
Parameter Units
LCS
Result
% Rec
Limits Qualifiers% RecConc.
2771745LABORATORY CONTROL SAMPLE:
LCSSpike
1,1,1,2-Tetrachloroethane ug/L 56.450 113 60-140
1,1,1-Trichloroethane ug/L 53.950 108 60-140
1,1,2,2-Tetrachloroethane ug/L 55.050 110 60-140
1,1,2-Trichloroethane ug/L 54.750 109 60-140
1,1-Dichloroethane ug/L 52.450 105 60-140
1,1-Dichloroethene ug/L 52.250 104 60-140
1,1-Dichloropropene ug/L 57.650 115 60-140
1,2,3-Trichlorobenzene ug/L 58.650 117 60-140
1,2,3-Trichloropropane ug/L 51.450 103 60-140
1,2,4-Trichlorobenzene ug/L 56.050 112 60-140
1,2,4-Trimethylbenzene ug/L 52.550 105 60-140
1,2-Dibromo-3-chloropropane ug/L 52.950 106 60-140
1,2-Dibromoethane (EDB)ug/L 54.150 108 60-140
1,2-Dichlorobenzene ug/L 53.350 107 60-140
1,2-Dichloroethane ug/L 48.750 97 60-140
1,2-Dichloropropane ug/L 53.250 106 60-140
1,3,5-Trimethylbenzene ug/L 52.650 105 60-140
1,3-Dichlorobenzene ug/L 52.350 105 60-140
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 26 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
LCS
Result
% Rec
Limits Qualifiers% RecConc.
2771745LABORATORY CONTROL SAMPLE:
LCSSpike
1,3-Dichloropropane ug/L 54.350 109 60-140
1,4-Dichlorobenzene ug/L 51.850 104 60-140
2,2-Dichloropropane ug/L 54.650 109 60-140
2-Chlorotoluene ug/L 50.450 101 60-140
4-Chlorotoluene ug/L 50.550 101 60-140
Benzene ug/L 52.450 105 60-140
Bromobenzene ug/L 53.750 107 60-140
Bromochloromethane ug/L 55.350 111 60-140
Bromodichloromethane ug/L 53.350 107 60-140
Bromoform ug/L 58.950 118 60-140
Bromomethane ug/L 61.750 123 60-140
Carbon tetrachloride ug/L 51.750 103 60-140
Chlorobenzene ug/L 52.050 104 60-140
Chloroethane ug/L 42.450 85 60-140
Chloroform ug/L 46.550 93 60-140
Chloromethane ug/L 43.950 88 60-140
cis-1,2-Dichloroethene ug/L 50.750 101 60-140
cis-1,3-Dichloropropene ug/L 57.550 115 60-140
Dibromochloromethane ug/L 57.850 116 60-140
Dibromomethane ug/L 53.250 106 60-140
Dichlorodifluoromethane ug/L 51.450 103 60-140
Diisopropyl ether ug/L 54.950 110 60-140
Ethylbenzene ug/L 51.150 102 60-140
Hexachloro-1,3-butadiene ug/L 54.350 109 60-140
Isopropylbenzene (Cumene)ug/L 51.650 103 60-140
m&p-Xylene ug/L 99.7100 100 60-140
Methyl-tert-butyl ether ug/L 53.550 107 60-140
Methylene Chloride ug/L 48.150 96 60-140
n-Butylbenzene ug/L 53.850 108 60-140
n-Propylbenzene ug/L 50.250 100 60-140
Naphthalene ug/L 56.250 112 60-140
o-Xylene ug/L 50.550 101 60-140
sec-Butylbenzene ug/L 52.950 106 60-140
Styrene ug/L 53.650 107 60-140
tert-Butylbenzene ug/L 45.350 91 60-140
Tetrachloroethene ug/L 53.450 107 60-140
Toluene ug/L 50.850 102 60-140
trans-1,2-Dichloroethene ug/L 53.150 106 60-140
trans-1,3-Dichloropropene ug/L 55.550 111 60-140
Trichloroethene ug/L 54.850 110 60-140
Trichlorofluoromethane ug/L 49.750 99 60-140
Vinyl chloride ug/L 51.350 103 60-140
1,2-Dichloroethane-d4 (S)%94 70-130
4-Bromofluorobenzene (S)%97 70-130
Toluene-d8 (S)%98 70-130
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 27 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
MS
Result
% Rec
Limits Qual% RecConc.
2771746MATRIX SPIKE & MATRIX SPIKE DUPLICATE:
MSSpike
Result
92458919003
2771747
MSD
Result
MSD
% Rec RPD RPD
Max
MSDMS
Spike
Conc.
1,1,1,2-Tetrachloroethane ug/L 20 108 60-140108 0 3020ND21.6 21.6
1,1,1-Trichloroethane ug/L 20 112 60-140118 6 3020ND22.4 23.6
1,1,2,2-Tetrachloroethane ug/L 20 105 60-140104 1 3020ND21.0 20.7
1,1,2-Trichloroethane ug/L 20 111 60-140111 1 3020ND22.2 22.3
1,1-Dichloroethane ug/L 20 110 60-140114 4 3020ND21.9 22.9
1,1-Dichloroethene ug/L 20 117 60-140117 0 3020ND23.4 23.3
1,1-Dichloropropene ug/L 20 122 60-140128 5 3020ND24.4 25.6
1,2,3-Trichlorobenzene ug/L 20 126 60-140115 9 3020ND25.2 23.0
1,2,3-Trichloropropane ug/L 20 103 60-140100 2 3020ND20.6 20.1
1,2,4-Trichlorobenzene ug/L 20 118 60-140108 9 3020ND23.6 21.6
1,2,4-Trimethylbenzene ug/L 20 102 60-140100 1 3020ND20.3 20.0
1,2-Dibromo-3-
chloropropane ug/L 20 107 60-140102 5 3020ND21.4 20.4
1,2-Dibromoethane (EDB)ug/L 20 107 60-140105 2 3020ND21.4 20.9
1,2-Dichlorobenzene ug/L 20 100 60-140100 1 3020ND20.0 19.9
1,2-Dichloroethane ug/L 20 97 60-140100 3 3020ND19.4 19.9
1,2-Dichloropropane ug/L 20 110 60-140112 1 3020ND22.0 22.3
1,3,5-Trimethylbenzene ug/L 20 101 60-140102 1 3020ND20.2 20.3
1,3-Dichlorobenzene ug/L 20 100 60-14098 2 3020ND20.1 19.7
1,3-Dichloropropane ug/L 20 107 60-140105 2 3020ND21.3 21.0
1,4-Dichlorobenzene ug/L 20 98 60-14099 1 3020ND19.6 19.8
2,2-Dichloropropane ug/L 20 117 60-140123 5 3020ND23.5 24.6
2-Chlorotoluene ug/L 20 96 60-14097 2 3020ND19.1 19.5
4-Chlorotoluene ug/L 20 97 60-14097 1 3020ND19.5 19.3
Benzene ug/L 20 109 60-140110 1 3020ND21.8 22.0
Bromobenzene ug/L 20 104 60-140103 1 3020ND20.9 20.6
Bromochloromethane ug/L 20 118 60-140119 1 3020ND23.5 23.7
Bromodichloromethane ug/L 20 112 60-140110 1 3020ND22.4 22.0
Bromoform ug/L 20 115 60-140114 1 3020ND23.0 22.8
Bromomethane ug/L M12016660-140159 4 3020ND33.2 31.8
Carbon tetrachloride ug/L 20 114 60-140115 1 3020ND22.8 23.0
Chlorobenzene ug/L 20 102 60-140102 0 3020ND20.5 20.5
Chloroethane ug/L 20 112 60-140111 1 3020ND22.4 22.1
Chloroform ug/L 20 101 60-140102 1 3020ND20.1 20.4
Chloromethane ug/L 20 96 60-14095 0 3020ND19.1 19.0
cis-1,2-Dichloroethene ug/L 20 108 60-140111 2 3020ND21.7 22.1
cis-1,3-Dichloropropene ug/L 20 113 60-140116 3 3020ND22.7 23.2
Dibromochloromethane ug/L 20 114 60-140112 2 3020ND22.7 22.3
Dibromomethane ug/L 20 115 60-140113 1 3020ND22.9 22.6
Dichlorodifluoromethane ug/L 20 107 60-140107 0 3020ND21.4 21.4
Diisopropyl ether ug/L 20 109 60-140111 1 3020ND21.9 22.2
Ethylbenzene ug/L 20 102 60-140102 1 3020ND20.5 20.4
Hexachloro-1,3-butadiene ug/L 20 134 60-140125 6 3020ND26.8 25.1
Isopropylbenzene(Cumene)ug/L 20 104 60-140103 1 3020ND20.8 20.6
m&p-Xylene ug/L 40 101 60-140101 0 3040ND40.3 40.4
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 28 of 34
#=QC#
QUALITY CONTROL DATA
Pace Project No.:
Project:
92458986
Burcham Property
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
Parameter Units
MS
Result
% Rec
Limits Qual% RecConc.
2771746MATRIX SPIKE & MATRIX SPIKE DUPLICATE:
MSSpike
Result
92458919003
2771747
MSD
Result
MSD
% Rec RPD RPD
Max
MSDMS
Spike
Conc.
Methyl-tert-butyl ether ug/L 20 115 60-140114 0 30203.2 26.2 26.1
Methylene Chloride ug/L 20 104 60-140106 2 3020ND20.8 21.2
n-Butylbenzene ug/L 20 111 60-140106 5 3020ND22.3 21.2
n-Propylbenzene ug/L 20 97 60-14098 0 3020ND19.5 19.6
Naphthalene ug/L 20 120 60-140108 10 3020ND23.9 21.5
o-Xylene ug/L 20 101 60-140101 0 3020ND20.2 20.3
sec-Butylbenzene ug/L 20 106 60-140103 3 3020ND21.2 20.6
Styrene ug/L 20 106 60-140104 1 3020ND21.1 20.8
tert-Butylbenzene ug/L 20 88 60-14087 1 3020ND17.6 17.5
Tetrachloroethene ug/L 20 110 60-140108 2 3020ND22.0 21.5
Toluene ug/L 20 106 60-140106 0 3020ND21.1 21.2
trans-1,2-Dichloroethene ug/L 20 116 60-140116 0 3020ND23.2 23.3
trans-1,3-Dichloropropene ug/L 20 112 60-140111 1 3020ND22.4 22.1
Trichloroethene ug/L 20 120 60-140116 3 3020ND23.9 23.1
Trichlorofluoromethane ug/L 20 114 60-140115 1 3020ND22.8 23.0
Vinyl chloride ug/L 20 110 60-140110 0 3020ND22.1 22.1
1,2-Dichloroethane-d4 (S)%93 70-13096
4-Bromofluorobenzene (S)%101 70-130100
Toluene-d8 (S)%99 70-130100
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 29 of 34
#=QL#
QUALIFIERS
Pace Project No.:
Project:
92458986
Burcham Property
DEFINITIONS
DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot.
ND - Not Detected at or above adjusted reporting limit.
TNTC - Too Numerous To Count
J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit.
MDL - Adjusted Method Detection Limit.
PQL - Practical Quantitation Limit.
RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and
bias for a specific analyte in a specific matrix.
S - Surrogate
1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is
a combined concentration.
Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values.
LCS(D) - Laboratory Control Sample (Duplicate)
MS(D) - Matrix Spike (Duplicate)
DUP - Sample Duplicate
RPD - Relative Percent Difference
NC - Not Calculable.
SG - Silica Gel - Clean-Up
U - Indicates the compound was analyzed for, but not detected.
Acid preservation may not be appropriate for 2 Chloroethylvinyl ether.
A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA
Method 8260.
N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for
each analyte is a combined concentration.
Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes.
TNI - The NELAC Institute.
LABORATORIES
Pace Analytical Services - CharlottePASI-C
ANALYTE QUALIFIERS
Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery.M1
RPD value was outside control limits.R1
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 30 of 34
#=CR#
QUALITY CONTROL DATA CROSS REFERENCE TABLE
Pace Project No.:
Project:
92458986
Burcham Property
Lab ID Sample ID QC Batch Method QC Batch Analytical Method
Analytical
Batch
92458986001 517653FBSM 6200B
92458986002 517750MW-1 SM 6200B
92458986003 517653DW-1 SM 6200B
92458986004 517653MW-4 SM 6200B
92458986005 517750WSW-1 SM 6200B
92458986006 517750WSW-4 SM 6200B
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.Date: 01/06/2020 02:48 PM
Pace Analytical Services, LLC
9800 Kincey Ave. Suite 100
Huntersville, NC 28078
[phone]
Page 31 of 34
Page 32 of 34
Page 33 of 34
Page 34 of 34
APPENDIX B
FIELD NOTES
Groundwater Sampling Log
Project No.71149638A Date 12/30/2019
Site Location Burcham Property Well ID DW-1
Weather Sunny, 60s Sample Collection Time 12:05
Casing
Diameter Gal/ft L/ft Evacuation Data
6 1.47 5.56 Screen Length (ft bls)
4 .653 2.47 Well Length (ft bTOC)64.5
3 .367 1.39 Depth to water (ft bTOC)38.15
2 .163 .618 Water column length (ft)26.35
1 .041 .154 Well Volume 4.30
¾ .023 .087 Evacuation Volume (x 3 )12.90
Sample Method Purge Device QA/QC Samples Sample ID for QA/QC
Peristaltic Grundfos Dedicated Duplicate
Bladder Proactive Disposable MS/MSD
Bailer PDB Decontaminated Equipment Blank
Monsoon Field Blank
Field Parameters
Time Purge
(gal)
Temp
(OC)
pH
(SU)
DO
(mg/L)
Cond.
(mmhos/cm)
Turb.
(NTU)
Redox
(mV)
Flow
(mL/min)
Drawdown
(ft)
11:58 3.5 18.1 6.79 7.97 2,120 -305.0 --
12:01 3.5 18.1 6.79 6.12 2,096 -189.5 --
Laboratory Analyses
Analytical Parameter Method No.
Bottles
Bottle Size/Type Preservative
VOCs 6200B 4 40 mL/ Amber HCl
PAHs
SVOCs
TPH
Metals
Notes:
Sampling Personnel: Victoria Larson
Groundwater Sampling Log
Project No.71149638A Date 12/30/2019
Site Location Burcham Property Well ID MW-1
Weather Sunny, 60s Sample Collection Time 12:35
Casing
Diameter Gal/ft L/ft Evacuation Data
6 1.47 5.56 Screen Length (ft bls)
4 .653 2.47 Well Length (ft bTOC)46
3 .367 1.39 Depth to water (ft bTOC)37.93
2 .163 .618 Water column length (ft)8.07
1 .041 .154 Well Volume 1.32
¾ .023 .087 Evacuation Volume (x 3 )3.95
Sample Method Purge Device QA/QC Samples Sample ID for QA/QC
Peristaltic Grundfos Dedicated Duplicate
Bladder Proactive Disposable MS/MSD
Bailer PDB Decontaminated Equipment Blank
Monsoon Field Blank FB – 10:30
Field Parameters
Time Purge
(gal)
Temp
(OC)
pH
(SU)
DO
(mg/L)
Cond.
(mmhos/cm)
Turb.
(NTU)
Redox
(mV)
Flow
(mL/min)
Drawdown
(ft)
12:25 1.3 18.0 4.94 2.54 1034 -388.9 --
12:28 1.3 17.9 4.93 2.20 1027 -354.5 --
12:31 1.3 17.9 4.97 2.00 1027 -325.8
Laboratory Analyses
Analytical Parameter Method No.
Bottles
Bottle Size/Type Preservative
VOCs 6200B 4 40 mL/ Amber HCl
PAHs
SVOCs
TPH
Metals
Notes:Strong Odor
Sampling Personnel: Victoria Larson
Groundwater Sampling Log
Project No.71149638A Date 12/302019
Site Location Burcham Property Well ID MW-4
Weather Sunny, 60s Sample Collection Time 11:10
Casing
Diameter Gal/ft L/ft Evacuation Data
6 1.47 5.56 Screen Length (ft bls)
4 .653 2.47 Well Length (ft bTOC)45
3 .367 1.39 Depth to water (ft bTOC)27.24
2 .163 .618 Water column length (ft)17.76
1 .041 .154 Well Volume 2.89
¾ .023 .087 Evacuation Volume (x 3 )8.64
Sample Method Purge Device QA/QC Samples Sample ID for QA/QC
Peristaltic Grundfos Dedicated Duplicate
Bladder Proactive Disposable MS/MSD
Bailer PDB Decontaminated Equipment Blank
Monsoon Field Blank
Field Parameters
Time Purge
(gal)
Temp
(OC)
pH
(SU)
DO
(mg/L)
Cond.
(mmhos/cm)
Turb.
(NTU)
Redox
(mV)
Flow
(mL/min)
Drawdown
(ft)
10:58 3.0 17.6 3.35 3.87 281.5 -452.3 --
11:01 3.0 17.5 3.09 3.34 457.7 -456.7 --
11:04 3.0 17.3 3.19 3.41 517.0 -446.2 --
Laboratory Analyses
Analytical Parameter Method No.
Bottles
Bottle Size/Type Preservative
VOCs 6200B 4 40 mL/ Amber HCl
PAHs
SVOCs
TPH
Metals
Notes:
Sampling Personnel: Victoria Larson
APPENDIX C
PHOTOGRAPHS
Project No. 71149638A
Date Photos Taken: March 5 and December 30, 2019
Burcham Property– Belmont, North Carolina – Incident #3679
View of the Burcham property with on-site residence, looking north.
View of monitoring well DW-1.
Project No. 71149638A
Date Photos Taken: March 5 and December 30, 2019
Burcham Property– Belmont, North Carolina – Incident #3679
View of monitoring well MW-1.
View of adjacent residence maintaining well WSW-4, looking west.
Project No. 71149638A
Date Photos Taken: March 5 and December 30, 2019
Burcham Property– Belmont, North Carolina – Incident #3679
View of monitoring well MW-4.