HomeMy WebLinkAboutWS-2689_6187_CA_MRP_20230414GROUNDWATER MONITORING REPORT
ARCHIE ELLEDGE WASTEWATER TREATMENT PLANT
2801 GRIFFITH ROAD
WINSTON-SALEM, FORSYTH CO., NORTH CAROLINA 27103
GROUNDWATER INCIDENT #6187
Prepared For
Ms. Gwen Royé
City of Winston-Salem
P.O. Box 2511
Winston-Salem, North Carolina 27102
For Submittal To
Ms. Christina Schroeter
North Carolina Department of Environmental Quality
Division of Waste Management, UST Section
Winston-Salem Regional Office
Prepared By
Griffith Enterprises, Inc.
353 Jonestown Rd., #312
Winston-Salem, North Carolina 27104
April 14, 2023
Report Certification
The geological and hydrogeological evaluations contained within this
Groundwater Monitoring Report are prepared in accordance with generally
accepted scientific practices, and are based on our understanding of the site and
data provided to us by others.
M. Alan Griffith 4/14/23
__________________________________________
M. Alan Griffith, L.G.
N.C. Licensed Geologist No. 2052
Griffith Enterprises, Inc. Corporate License No. C-398
Contents
Text
General Site Information Page 1 ....................................................................
Introduction Page 1 .........................................................................................
Discussion of March 2023 Monitoring Well Sampling Results Page 2 ...........
Water Supply Wells Located Within 250 Feet of the Release Page 3 ............
Results of Updated Receptor Survey Page 3 .................................................
Report Conclusions Page 4 ............................................................................
Tables
1. Summary of Former UST Inventory
2. List of Contiguous Properties
3. Summary of Known Water Supply Wells
4. Ground Water Sample Analytical Results
5. Summary of Water Level Elevations
Figures
1. Site Location Map on (U.S.G.S. Topographic Map)
2. Site Area Map
3. Site Configuration Map
4. Ground Water Elevation Map (3/15/23)
5. Ground Water Analytical Results Map (3/15/23)
Appendix
1. Laboratory Reports
2. Receptor Parcel Location List and Returned Water Supply Well Responses
3. North Carolina NCAC 2B Surface Water Standards Table
General Site Information
•Site Name: Archie Elledge Wastewater Treatment Plant
•Date of Report: 4/14/2023
•Site Priority Ranking: I0145D (from NCDEQ Database)
•Responsible Party: City of Winston-Salem, P.O. Box 2511, Winston-Salem,
North Carolina, 27102. Phone: (336) 748-3891 Attn: Ms. Gwen Royé
•Property Owner: City of Winston Salem, North Carolina
•Consultant / Contractor Information: Griffith Enterprises, Inc.
•Release Information: Date Discovered: 9/10/90
Estimated Quantity: unknown
Cause of Release: unknown
Source of Release: 2,000-gallon gasoline UST
•Latitude and Longitude of Release: 36o 03’ 30” / 80o 16’ 40” (from NCDENR
Database)
Introduction
The Elledge Wastewater Treatment Plant is located 2801 Griffith Road in
Winston-Salem, North Carolina, and is owned an operated by the City of
Winston-Salem. The site location is illustrated on Figure 1, a reproduction of a
part of the U.S.G.S. topographic map, Winston-Salem West Quadrangle.
Two under-ground storage tanks (USTs) were operated at the site:
•1 – 2,500 gallon gasoline
•1 – 2,000 gallon gasoline
During closure and removal of the two USTs in September of 1990, soil
hydrocarbon impact was documented. Based on the UST closure report,
NCDENR issued a NORR dated December 6, 2001 requesting completion of a
Limited Site Assessment (LSA) for this incident. In response to the NORR, a LSA
Phase II was completed and submitted to the NCDENR Winston-Salem Regional
Office on April 17, 2002 by the City of Winston-Salem.
A summary of the results for the 2002 LSA Phase II investigation were as follows:
•Residual soil hydrocarbon impact beneath the former tank basin was
detected at concentrations above NCDENR “Soil to Ground Water” and
“Residential” MSCCs.
•Ten (10) hydrocarbon compounds were detected in the groundwater that
exceeded NCAC 2L Ground Water Standards.
•The 2002 LSA Phase II investigation identified five (5) water supply wells that
are located between 1,000 feet and 1,700 feet away from the original UST
location (See Table 3 and Figure 2).
•Salem Creek (Class C Stream) is located approximately 150 feet southeast
from the original UST release area.
The following is a summary of dissolved phase constituent concentrations that
were reported to be above their respective NCAC 2L ground water standards
from an interim groundwater sampling event that was completed for monitoring
wells MW-4, MW-5, MW-6 and DW-1 on September 18, 2014:
MW-4:
•C5-C8 aliphatic fraction: (8,270 ug/l); (2L level: 400 ug/l).
•C9-C12 aliphatic fraction: (6,210 ug/l); (2L level: 700 ug/l).
•Benzene: (662 ug/l); (2L level: 1 ug/l).
•Ethylbenzene: (899 ug/l); (2L level: 600 ug/l).
•Naphthalene: (598 ug/l); (2L level: 6 ug/l).
•n-propylbenzene: (135 ug/l); (2L level: 70 ug/l).
•Xylenes (total): (575 ug/l); (2L level: 500 ug/l).
•1,2,4-trimethylbenzene: (486 ug/l); (2L level: 400 ug/l).
MW-5:
•Lead: (19 ug/l); (2L level: 15 ug/l).
A Notice of Regulatory Requirements (NORR) was issued to the City of Winston-
Salem on February 17, 2023. The NORR requested the following updated
information for this incident:
•Collect groundwater samples from the existing monitoring wells on the site.
•Collect groundwater samples from the closest water supply well located within
250 feet of the release.
•Update the receptor survey the surrounding area for water resources that could
be at risk, such as water supply wells, lakes, streams etc.
Results of March 2023 Monitoring Well Sampling Results
Two (2) on-site monitoring wells (MW-4 & DW-1) were gauged and sampled on
March 15, 2023. The groundwater gauging data is presented in Table 5 and
illustrated in Figure 4. Monitoring wells MW-5 and MW-6 could not be located and
are suspected of being destroyed during the site grading associated with the
demolition of the former Sludge Conditioning Building as displayed in Figure 3.
The laboratory analyses that were performed on the collected groundwater
samples from monitoring wells MW-4 and DW-1 consisted of EPA Method 6200B
(VOCs), EPA Method 6010 (Lead), and MADEP VPH. The groundwater analytical
laboratory data is summarized in Table 4. Illustrations of the data are presented
in Figure 5. NAPL was not detected in either of the two monitoring wells during
this recent sampling event.
The following as a summary of the dissolved phase constituent concentrations
that were reported to be above their respective NCAC 2L ground water standards
from the groundwater sampling event completed for monitoring wells MW-4 and
DW-1 on March 15, 2023:
MW-4:
•C5-C8 aliphatic fraction: (1,290 ug/l); (2L level: 400 ug/l).
•C9-C10 aromatic fraction: (427 ug/l); (2L level: 200 ug/l).
•Benzene: (83.9 ug/l); (2L level: 1 ug/l).
•Naphthalene: (16.3 ug/l); (2L level: 6 ug/l).
DW-1: No dissolved phase VOC concentrations were detected in DW-1.
As summarized in Table 4, the total VOC concentrations being reported in
monitoring well MW-4 continues to greatly decrease over time. The current total
dissolved phase hydrocarbon concentration of 2,227 ug/l is significantly less than
the 84,300 ug/l that was initially reported on January 21, 2002. This is a
contaminant concentration reduction of over 97% from 2002 to 2023.
Also, according to the North Carolina 15A NCAC 02B Water Quality Standards
for Surface Waters Table that is included in the Appendix of this report, the latest
dissolved phase VOC concentrations that are listed in Table 4 do not exceed the
NCAC 2B Surface Water Standards for a Class C Stream by a factor of 10x.
Water Supply Wells Located Within 250 Feet Of The Release
There were no water supply wells identified within 250 feet of the former UST
release (See Table 3).
Results of Updated Receptor Survey
As listed in the Appendix of this report, there are twenty-five (25) property parcels
that are located within 1500 feet of the former UST release. NCDEQ Water
Supply Well Questionnaire Forms were mailed to each of the property owners to
ascertain if any water supply wells were located on their respective properties. A
total of eighteen (18) of the property owners responded by either returning the
form, emailing the information, or leaving a voicemail with the requested
information.
Griffith Enterprises also performed field reconnaissance activities in an attempt to
locate additional potential receptors.
As listed in Table 3, results from the updated receptor survey show that the same
five (5) properties that were identified in the 2002 LSA Phase II are the parcels
currently utilizing water supply wells. The water supply wells range in distance
from approximately 1,000 feet, out to a distance of approximately 1,700 feet from
the original UST release area.
Also, as stated earlier in this report, Salem Creek (Class C Stream) is located
approximately 150 feet southeast from the original UST release area.
Report Conclusions
The following as a summary of the dissolved phase constituent concentrations
that were reported to be above their respective NCAC 2L ground water standards
from the groundwater sampling event completed for monitoring wells MW-4 and
DW-1 on March 15, 2023:
MW-4:
•C5-C8 aliphatic fraction: (1,290 ug/l); (2L level: 400 ug/l).
•C9-C10 aromatic fraction: (427 ug/l); (2L level: 200 ug/l).
•Benzene: (83.9 ug/l); (2L level: 1 ug/l).
•Naphthalene: (16.3 ug/l); (2L level: 6 ug/l).
DW-1: No dissolved phase VOC concentrations were detected in DW-1.
As summarized in Table 4, the total VOC concentrations being reported in
monitoring well MW-4 continues to greatly decrease over time. The current total
dissolved phase hydrocarbon concentration of 2,227 ug/l is significantly less than
the 84,300 ug/l that was initially reported on January 21, 2002. This is a
contaminant concentration reduction of over 97% from 2002 to 2023.
Also, according to the North Carolina 15A NCAC 02B Water Quality Standards
for Surface Waters Table that is included in the Appendix of this report, the latest
dissolved phase VOC concentrations that are listed in Table 4 do not exceed the
NCAC 2B Surface Water Standards for a Class C Stream by a factor of 10x.
It is also important to note that each of the four (4) dissolved phase hydrocarbon
compounds detected above NCAC 2L Standards were reported at concentrations
below NCDENR Gross Contaminant Levels (GCLs).
There were no water supply wells identified within 250 feet of the former UST
release.
The results from the updated receptor survey show that the same five (5)
properties that were identified in the 2002 LSA Phase II are the parcels currently
utilizing water supply wells. The water supply wells range in distance from
approximately 1,000 feet, out to a distance of approximately 1,700 feet from the
original UST release area.
Salem Creek (Class C Stream) is located approximately 150 feet southeast from
the original UST release area.
Based on the information that is contained in this report, we are requesting that
the NCDEQ consider lowering the Risk Classification of this site from
Intermediate to Low, and issue a No Further Action for this incident.
TABLES
TABLE 3
WATER SUPPLY WELLS
ARCHIE ELLEDGE TREATMENT PLANT, WINSTON-SALEM, NC
Map Well Address Well Property Property Owner Distance (ft) Well Const.City
ID Owner Owner Address From Site Status Connect
1 2389 Clemmonsville Rd. W. Patsy T Haga Same 177 Wintergreen Drive 1,700 ft. south in use NA No
Winston-Salem Irrev. Trust Garner, NC. 27529
2 2385 Clemmonsville Rd. W. Patsy T Haga Same 177 Wintergreen Drive 1,700 ft. south in use NA No
Winston-Salem Irrev. Trust Garner, NC. 27529
3 2367 Clemmonsville Rd. W. David H. Brown Same 2367 Clemmonsville Rd. W.1,000 ft. south in use NA No
Winston-Salem Winston-Salem 27127
4 2365 Clemmonsville Rd. W.Laura H. Brown Same 2365 Clemmonsville Rd. W.1,300 ft. south in use NA No
Winston-Salem Winston-Salem 27127
5 2774 Neiman Industrial Dr.Ransom C.Same P.O. Box 283 1,500 ft.in use NA No
Winston-Salem Weatherman, Jr.Winston-Salem 27012 northwest
Note: Properties at ID #1 and ID #2 share the same well.
Table 4GROUND WATER SAMPLE ANALYTICAL RESULTSARCHIE ELLEDGE TREATMENT PLANT UST2801 GRIFFITH ROADWINSTON-SALEM, NORTH CAROLINASAMPLE IDDATE COLLECTEDVPHAliphaticsC5 - C8EPHAliphaticsC9 - C12
VPH/EPH
Aromatics
C9 - C10
benzene
n-butylbenzene
IPE
ethyl-benzene
isopropylbenzene
p-isopropyltoluene
naphthalene
MTBE
n-propylbenzene
toluene
total xylenes
1,2,4 -trimethylbenzene
1,3,5-trimethylbenzene
total hydro-carbons
Lead Method 3030C(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)(µg/L)MW-403/15/231,29026742783.9BDL9.7621.81.161.1316.31.112.2815.130.546.713.22,227BDL09/18/148,2706,210BDL662BDLBDL89950.9BDL5985.113532057548615218,3635.309/17/1214,00017,0009,30068053BDL1,20090BDL670BDL2607501,8901,30045047,643BDL09/29/1010,00018,0008,9001,200NABDL1,300NANANABDLNA2,6003,4501,80055047,800BDL03/04/0232,00016,0005,1001,800NABDL590NANANABDLNA2,6002,450BDLBDL60,540BDL01/21/0246,00017,000BDL4,000NABDL2,300NANANABDLNA8,5006,500BDLBDL84,300BDLMW-503/15/23NOT SAMPLED WELL DESTROYED DURING SITE DEMOLITION PROJECT09/18/14BDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDL1909/17/12BDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDL8.609/29/10BDLBDLBDLBDLNABDLBDLNANANABDLNA24BDLBDLBDL24603/04/02BDLBDLBDLBDLNABDLBDLNANANABDLNABDLBDLBDLBDLBDLBDL01/21/02BDLBDLBDLBDLNABDLBDLNANANABDLNABDLBDLBDLBDLBDLBDLMW-603/15/23NOT SAMPLED WELL DESTROYED DURING SITE DEMOLITION PROJECT09/18/14BDLBDLBDLBDLBDL2BDLBDLBDLBDL2.9BDLBDLBDLBDLBDL4.9BDL09/17/12BDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDL1309/29/10190BDLBDLBDLNA170BDLNANANA16NABDLBDLBDLBDL376BDL03/04/02BDLBDLBDLBDLNA630BDLNANANA900NABDLBDLBDLBDL1,530BDLMW-703/15/23NOT SAMPLED WELL DESTROYED DURING CONSTRUCTION PROJECT03/04/02330BDLBDLBDLNABDLBDLNANANABDLNABDLBDLBDLBDL330BDLDW-103/15/23BDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDLBDL09/18/14 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL09/17/12 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL09/29/10 BDL BDL BDL BDLNABDL BDLNA NA NABDLNABDL BDL BDL BDL BDL BDL03/04/02 BDL100BDL13NABDL 5.6NA NA NABDLNA24 28BDL BDL171BDL2L Ground-Water Stds400 700 200170 70 600 70 25620 70 600 500 400 400NS15GCLsNS NS NS5,000 5,900 70,000 80,000 30,500 11,700 6,000 20,000 26,100 260,000 50,000 28,500 24,100NS15,000BDL: Not Detected above Reporting LimitNA: Not analyzedBold & shaded values exceed NCAC 2L standards
MONITORING DATE DATE CASING DEPTH TO GROUNDWATER SCREENED
WELL GAUGED DRILLED ELEV. (ft.)WATER (ft.)ELEV. (ft.) INTERVAL (ft.)
MW-4 3/15/2023 1/9/2002 94.62 12.43 82.19 5-25
MW-4 9/18/2014 1/9/2002 94.62 13.93 80.69 5-25
MW-4 9/17/2012 1/9/2002 94.62 13.71 80.91 5-25
MW-4 9/29/2010 1/9/2002 94.62 13.61 81.01 5-25
MW-4 3/4/2002 1/9/2002 94.62 14.42 80.20 5-25
MW-4 1/21/2002 1/9/2002 94.62 13.87 80.75 5-25
MW-5 9/18/2014 1/9/2002 92.42 12.57 79.85 5-25
MW-5 9/17/2012 1/9/2002 92.42 12.41 80.01 5-25
MW-5 9/29/2010 1/9/2002 92.42 12.34 80.08 5-25
MW-5 3/4/2002 1/9/2002 92.42 13.27 79.15 5-25
MW-5 1/21/2002 1/9/2002 92.42 12.45 79.97 5-25
MW-6 9/18/2014 2/4/2002 92.26 13.22 79.04 5-25
MW-6 9/17/2012 2/4/2002 92.26 12.99 79.27 5-25
MW-6 9/29/2010 2/4/2002 92.26 12.54 79.72 5-25
MW-6 3/4/2002 2/4/2002 92.26 13.63 78.63 5-25
DW-1 3/15/2023 2/25/2002 95.03 12.20 82.83 50-55
DW-1 9/18/2014 2/25/2002 95.03 13.63 81.40 50-55
DW-1 9/17/2012 2/25/2002 95.03 13.66 81.37 50-55
DW-1 9/29/2010 2/25/2002 95.03 13.65 81.38 50-55
DW-1 3/4/2002 2/25/2002 95.03 14.34 80.69 50-55
wells surveyed to temporary benchmark of 100 ft.
TABLE 5
WATER LEVEL ELEVATIONS
ARCHIE ELLEDGE TREATMENT PLANT, WINSTON-SALEM, NC
Page 1 of 1
FIGURES
Monitoring Well Destroyed
Monitoring Well Destroyed
4
Groundwater Elevation Map 3/15/2023
82.19’
82.83’’
(Demolished)
Monitoring Well Destroyed
Monitoring Well Destroyed
5
Groundwater Analytical Results 3/15/2023
Concentrations are in ug/l.
Only concentrations exceeding
NCAC 2L Standards are shown.
(Demolished)MW-4
C5-C8 Aliphatics: 1,290 ug/l
C9-C10 Aromatics: 427 ug/l
Benzene: 83.9 ug/l
Naphthalene: 16.3 ug/lBDL
APPENDIX 1
ANALYTICAL REPORT
March 24, 2023
Griffith Enterprise
Sample Delivery Group:L1595581
Samples Received:03/16/2023
Project Number:
Description:Archie Elledge Wastewater Treatment Plant
Report To:Mr. Alan Griffith
353 Jonestown Road, PMB 312
Winston-Salem, NC 27104
Entire Report Reviewed By:
March 24, 2023
[Preliminary Report]
Heather J Wagner
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided, and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 www.pacenational.com
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 1 of 17
March 24, 2023
Heather J Wagner
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 1 of 17
TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 4
Sr: Sample Results 5
MW-4 L1595581-01 5
DW-1 L1595581-02 7
Qc: Quality Control Summary 9
Metals (ICP) by Method 6010D 9
Volatile Petroleum Hydrocarbons by Method MADEPV 10
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 11
Gl: Glossary of Terms 15
Al: Accreditations & Locations 16
Sc: Sample Chain of Custody 17
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
MW-4 L1595581-01 GW M. Alan Griffith 03/15/23 11:45 03/16/23 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Metals (ICP) by Method 6010D WG2025058 1 03/18/23 21:51 03/20/23 15:03 ZSA Mt. Juliet, TN
Volatile Petroleum Hydrocarbons by Method MADEPV WG2025365 1 03/17/23 16:08 03/17/23 16:08 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 WG2028890 1 03/23/23 15:56 03/23/23 15:56 ADM Mt. Juliet, TN
Collected by Collected date/time Received date/time
DW-1 L1595581-02 GW M. Alan Griffith 03/15/23 12:20 03/16/23 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Metals (ICP) by Method 6010D WG2025058 1 03/18/23 21:51 03/20/23 15:06 ZSA Mt. Juliet, TN
Volatile Petroleum Hydrocarbons by Method MADEPV WG2025365 1 03/17/23 16:41 03/17/23 16:41 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 WG2028890 1 03/23/23 16:20 03/23/23 16:20 ADM Mt. Juliet, TN
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
Heather J Wagner
Project Manager
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 4 of 17
Heather J Wagner
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 4 of 17
SAMPLE RESULTS - 01
L1595581
MW-4
Collected date/time: 03/15/23 11:45
Metals (ICP) by Method 6010D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Lead ND 0.00600 1 03/20/2023 15:03 WG2025058
Volatile Petroleum Hydrocarbons by Method MADEPV
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Unadjusted C5-C8 Aliphatics 1.29 0.100 1 03/17/2023 16:08 WG2025365
Unadjusted C9-C12 Aliphatics 0.267 0.100 1 03/17/2023 16:08 WG2025365
Unadjusted C9-C10 Aromatics 0.427 0.100 1 03/17/2023 16:08 WG2025365
Total VPH 1.98 0.100 1 03/17/2023 16:08 WG2025365
(S) 2,5-Dibromotoluene(FID) 109 70.0-130 03/17/2023 16:08 WG2025365
(S) 2,5-Dibromotoluene(PID) 104 70.0-130 03/17/2023 16:08 WG2025365
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Acetone ND 0.0500 1 03/23/2023 15:56 WG2028890
Acrolein ND 0.0500 1 03/23/2023 15:56 WG2028890
Acrylonitrile ND 0.0100 1 03/23/2023 15:56 WG2028890
Benzene 0.0839 0.00100 1 03/23/2023 15:56 WG2028890
Bromobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
Bromodichloromethane ND 0.00100 1 03/23/2023 15:56 WG2028890
Bromoform ND 0.00100 1 03/23/2023 15:56 WG2028890
Bromomethane ND 0.00500 1 03/23/2023 15:56 WG2028890
n-Butylbenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
sec-Butylbenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
tert-Butylbenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
Carbon tetrachloride ND 0.00100 1 03/23/2023 15:56 WG2028890
Chlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
Chlorodibromomethane ND 0.00100 1 03/23/2023 15:56 WG2028890
Chloroethane ND 0.00500 1 03/23/2023 15:56 WG2028890
Chloroform ND 0.00500 1 03/23/2023 15:56 WG2028890
Chloromethane ND 0.00250 1 03/23/2023 15:56 WG2028890
2-Chlorotoluene ND 0.00100 1 03/23/2023 15:56 WG2028890
4-Chlorotoluene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,2-Dibromo-3-Chloropropane ND 0.00500 1 03/23/2023 15:56 WG2028890
1,2-Dibromoethane ND 0.00100 1 03/23/2023 15:56 WG2028890
Dibromomethane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,2-Dichlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,3-Dichlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,4-Dichlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
Dichlorodifluoromethane ND 0.00500 1 03/23/2023 15:56 WG2028890
1,1-Dichloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,2-Dichloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1-Dichloroethene ND 0.00100 1 03/23/2023 15:56 WG2028890
cis-1,2-Dichloroethene ND 0.00100 1 03/23/2023 15:56 WG2028890
trans-1,2-Dichloroethene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,2-Dichloropropane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1-Dichloropropene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,3-Dichloropropane ND 0.00100 1 03/23/2023 15:56 WG2028890
2,2-Dichloropropane ND 0.00100 1 03/23/2023 15:56 WG2028890
Di-isopropyl ether 0.00976 0.00100 1 03/23/2023 15:56 WG2028890
Ethylbenzene 0.0218 0.00100 1 03/23/2023 15:56 WG2028890
Hexachloro-1,3-butadiene ND 0.00100 1 03/23/2023 15:56 WG2028890
Isopropylbenzene 0.00116 0.00100 1 03/23/2023 15:56 WG2028890
p-Isopropyltoluene 0.00113 0.00100 1 03/23/2023 15:56 WG2028890
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 5 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 5 of 17
SAMPLE RESULTS - 01
L1595581
MW-4
Collected date/time: 03/15/23 11:45
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
2-Butanone (MEK)ND 0.0100 1 03/23/2023 15:56 WG2028890
Methylene Chloride ND 0.00500 1 03/23/2023 15:56 WG2028890
4-Methyl-2-pentanone (MIBK) ND 0.0100 1 03/23/2023 15:56 WG2028890
Methyl tert-butyl ether 0.00111 0.00100 1 03/23/2023 15:56 WG2028890
Naphthalene 0.0163 0.00500 1 03/23/2023 15:56 WG2028890
n-Propylbenzene 0.00228 0.00100 1 03/23/2023 15:56 WG2028890
Styrene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1,1,2-Tetrachloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1,2,2-Tetrachloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
Tetrachloroethene ND 0.00100 1 03/23/2023 15:56 WG2028890
Toluene 0.0151 0.00100 1 03/23/2023 15:56 WG2028890
1,2,3-Trichlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,2,4-Trichlorobenzene ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1,1-Trichloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
1,1,2-Trichloroethane ND 0.00100 1 03/23/2023 15:56 WG2028890
Trichloroethene ND 0.00100 1 03/23/2023 15:56 WG2028890
Trichlorofluoromethane ND 0.00500 1 03/23/2023 15:56 WG2028890
1,2,3-Trichloropropane ND 0.00250 1 03/23/2023 15:56 WG2028890
1,2,4-Trimethylbenzene 0.0467 0.00100 1 03/23/2023 15:56 WG2028890
1,3,5-Trimethylbenzene 0.0132 0.00100 1 03/23/2023 15:56 WG2028890
Vinyl chloride ND 0.00100 1 03/23/2023 15:56 WG2028890
o-Xylene 0.00543 0.00100 1 03/23/2023 15:56 WG2028890
m&p-Xylenes 0.0251 0.00200 1 03/23/2023 15:56 WG2028890
Ethanol ND J3 0.100 1 03/23/2023 15:56 WG2028890
(S) Toluene-d8 112 80.0-120 03/23/2023 15:56 WG2028890
(S) 4-Bromofluorobenzene 103 77.0-126 03/23/2023 15:56 WG2028890
(S) 1,2-Dichloroethane-d4 91.3 70.0-130 03/23/2023 15:56 WG2028890
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 6 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 6 of 17
SAMPLE RESULTS - 02
L1595581
DW-1
Collected date/time: 03/15/23 12:20
Metals (ICP) by Method 6010D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Lead ND 0.00600 1 03/20/2023 15:06 WG2025058
Volatile Petroleum Hydrocarbons by Method MADEPV
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Unadjusted C5-C8 Aliphatics ND 0.100 1 03/17/2023 16:41 WG2025365
Unadjusted C9-C12 Aliphatics ND 0.100 1 03/17/2023 16:41 WG2025365
Unadjusted C9-C10 Aromatics ND 0.100 1 03/17/2023 16:41 WG2025365
Total VPH ND 0.100 1 03/17/2023 16:41 WG2025365
(S) 2,5-Dibromotoluene(FID) 91.3 70.0-130 03/17/2023 16:41 WG2025365
(S) 2,5-Dibromotoluene(PID) 90.0 70.0-130 03/17/2023 16:41 WG2025365
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Acetone ND 0.0500 1 03/23/2023 16:20 WG2028890
Acrolein ND 0.0500 1 03/23/2023 16:20 WG2028890
Acrylonitrile ND 0.0100 1 03/23/2023 16:20 WG2028890
Benzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Bromobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Bromodichloromethane ND 0.00100 1 03/23/2023 16:20 WG2028890
Bromoform ND 0.00100 1 03/23/2023 16:20 WG2028890
Bromomethane ND 0.00500 1 03/23/2023 16:20 WG2028890
n-Butylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
sec-Butylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
tert-Butylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Carbon tetrachloride ND 0.00100 1 03/23/2023 16:20 WG2028890
Chlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Chlorodibromomethane ND 0.00100 1 03/23/2023 16:20 WG2028890
Chloroethane ND 0.00500 1 03/23/2023 16:20 WG2028890
Chloroform ND 0.00500 1 03/23/2023 16:20 WG2028890
Chloromethane ND 0.00250 1 03/23/2023 16:20 WG2028890
2-Chlorotoluene ND 0.00100 1 03/23/2023 16:20 WG2028890
4-Chlorotoluene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2-Dibromo-3-Chloropropane ND 0.00500 1 03/23/2023 16:20 WG2028890
1,2-Dibromoethane ND 0.00100 1 03/23/2023 16:20 WG2028890
Dibromomethane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2-Dichlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,3-Dichlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,4-Dichlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Dichlorodifluoromethane ND 0.00500 1 03/23/2023 16:20 WG2028890
1,1-Dichloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2-Dichloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1-Dichloroethene ND 0.00100 1 03/23/2023 16:20 WG2028890
cis-1,2-Dichloroethene ND 0.00100 1 03/23/2023 16:20 WG2028890
trans-1,2-Dichloroethene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2-Dichloropropane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1-Dichloropropene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,3-Dichloropropane ND 0.00100 1 03/23/2023 16:20 WG2028890
2,2-Dichloropropane ND 0.00100 1 03/23/2023 16:20 WG2028890
Di-isopropyl ether ND 0.00100 1 03/23/2023 16:20 WG2028890
Ethylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Hexachloro-1,3-butadiene ND 0.00100 1 03/23/2023 16:20 WG2028890
Isopropylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
p-Isopropyltoluene ND 0.00100 1 03/23/2023 16:20 WG2028890
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 7 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 7 of 17
SAMPLE RESULTS - 02
L1595581
DW-1
Collected date/time: 03/15/23 12:20
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
2-Butanone (MEK)ND 0.0100 1 03/23/2023 16:20 WG2028890
Methylene Chloride ND 0.00500 1 03/23/2023 16:20 WG2028890
4-Methyl-2-pentanone (MIBK) ND 0.0100 1 03/23/2023 16:20 WG2028890
Methyl tert-butyl ether ND 0.00100 1 03/23/2023 16:20 WG2028890
Naphthalene ND 0.00500 1 03/23/2023 16:20 WG2028890
n-Propylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Styrene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1,1,2-Tetrachloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1,2,2-Tetrachloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
Tetrachloroethene ND 0.00100 1 03/23/2023 16:20 WG2028890
Toluene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2,3-Trichlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,2,4-Trichlorobenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1,1-Trichloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
1,1,2-Trichloroethane ND 0.00100 1 03/23/2023 16:20 WG2028890
Trichloroethene ND 0.00100 1 03/23/2023 16:20 WG2028890
Trichlorofluoromethane ND 0.00500 1 03/23/2023 16:20 WG2028890
1,2,3-Trichloropropane ND 0.00250 1 03/23/2023 16:20 WG2028890
1,2,4-Trimethylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
1,3,5-Trimethylbenzene ND 0.00100 1 03/23/2023 16:20 WG2028890
Vinyl chloride ND 0.00100 1 03/23/2023 16:20 WG2028890
o-Xylene ND 0.00100 1 03/23/2023 16:20 WG2028890
m&p-Xylenes ND 0.00200 1 03/23/2023 16:20 WG2028890
Ethanol ND J3 0.100 1 03/23/2023 16:20 WG2028890
(S) Toluene-d8 113 80.0-120 03/23/2023 16:20 WG2028890
(S) 4-Bromofluorobenzene 103 77.0-126 03/23/2023 16:20 WG2028890
(S) 1,2-Dichloroethane-d4 88.0 70.0-130 03/23/2023 16:20 WG2028890
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 8 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 8 of 17
QUALITY CONTROL SUMMARYWG2025058
Metals (ICP) by Method 6010D L1595581-01,02
Method Blank (MB)
(MB) R3903239-1 03/20/23 14:31
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Lead U 0.00299 0.00600
Laboratory Control Sample (LCS)
(LCS) R3903239-2 03/20/23 14:33
Spike Amount LCS Result LCS Rec. Rec. Limits LCS Qualifier
Analyte mg/l mg/l %%
Lead 1.00 0.968 96.8 80.0-120
L1595492-01 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1595492-01 03/20/23 14:36 • (MS) R3903239-4 03/20/23 14:41 • (MSD) R3903239-5 03/20/23 14:44
Spike Amount Original Result MS Result MSD Result MS Rec. MSD Rec. Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l mg/l %%%%%
Lead 1.00 ND 0.988 0.986 98.8 98.6 1 75.0-125 0.141 20
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 9 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 9 of 17
QUALITY CONTROL SUMMARYWG2025365
Volatile Petroleum Hydrocarbons by Method MADEPV L1595581-01,02
Method Blank (MB)
(MB) R3903567-2 03/17/23 10:38
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Unadjusted C5-C8 Aliphatics U 0.0333 0.100
Unadjusted C9-C12 Aliphatics U 0.0333 0.100
Unadjusted C9-C10 Aromatics U 0.0333 0.100
Total VPH U 0.0333 0.100
(S) 2,5-Dibromotoluene(FID) 93.9 70.0-130
(S) 2,5-Dibromotoluene(PID) 92.4 70.0-130
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3903567-1 03/17/23 09:33 • (LCSD) R3903567-3 03/17/23 13:57
Spike Amount LCS Result LCSD Result LCS Rec. LCSD Rec. Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
Unadjusted C5-C8 Aliphatics 1.20 1.08 1.08 90.0 90.0 70.0-130 0.000 25
Unadjusted C9-C12 Aliphatics 1.40 1.36 1.34 97.1 95.7 70.0-130 1.48 25
Unadjusted C9-C10 Aromatics 0.200 0.214 0.216 107 108 70.0-130 0.930 25
Total VPH 2.80 2.65 2.64 94.6 94.3 70.0-130 0.378 25
(S) 2,5-Dibromotoluene(FID) 98.9 91.5 70.0-130
(S) 2,5-Dibromotoluene(PID) 97.0 91.7 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 10 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 10 of 17
QUALITY CONTROL SUMMARYWG2028890
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 L1595581-01,02
Method Blank (MB)
(MB) R3904852-3 03/23/23 12:51
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Acetone U 0.0113 0.0500
Acrolein U 0.00254 0.0500
Acrylonitrile U 0.000671 0.0100
Benzene U 0.0000941 0.00100
Bromobenzene U 0.000118 0.00100
Bromodichloromethane U 0.000136 0.00100
Bromoform U 0.000129 0.00100
Bromomethane U 0.000605 0.00500
n-Butylbenzene U 0.000157 0.00100
sec-Butylbenzene U 0.000125 0.00100
tert-Butylbenzene U 0.000127 0.00100
Carbon tetrachloride U 0.000128 0.00100
Chlorobenzene U 0.000116 0.00100
Chlorodibromomethane U 0.000140 0.00100
Chloroethane U 0.000192 0.00500
Chloroform U 0.000111 0.00500
Chloromethane U 0.000960 0.00250
2-Chlorotoluene U 0.000106 0.00100
4-Chlorotoluene U 0.000114 0.00100
1,2-Dibromo-3-Chloropropane U 0.000276 0.00500
1,2-Dibromoethane U 0.000126 0.00100
Dibromomethane U 0.000122 0.00100
1,2-Dichlorobenzene U 0.000107 0.00100
1,3-Dichlorobenzene U 0.000110 0.00100
1,4-Dichlorobenzene U 0.000120 0.00100
Dichlorodifluoromethane U 0.000374 0.00500
1,1-Dichloroethane U 0.000100 0.00100
1,2-Dichloroethane U 0.0000819 0.00100
1,1-Dichloroethene U 0.000188 0.00100
cis-1,2-Dichloroethene U 0.000126 0.00100
trans-1,2-Dichloroethene U 0.000149 0.00100
1,2-Dichloropropane U 0.000149 0.00100
1,1-Dichloropropene U 0.000142 0.00100
1,3-Dichloropropane U 0.000110 0.00100
2,2-Dichloropropane U 0.000161 0.00100
Di-isopropyl ether U 0.000105 0.00100
Ethylbenzene U 0.000137 0.00100
Hexachloro-1,3-butadiene U 0.000337 0.00100
Isopropylbenzene U 0.000105 0.00100
p-Isopropyltoluene U 0.000120 0.00100
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 11 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 11 of 17
QUALITY CONTROL SUMMARYWG2028890
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 L1595581-01,02
Method Blank (MB)
(MB) R3904852-3 03/23/23 12:51
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
2-Butanone (MEK)U 0.00119 0.0100
Methylene Chloride U 0.000430 0.00500
4-Methyl-2-pentanone (MIBK) U 0.000478 0.0100
Methyl tert-butyl ether U 0.000101 0.00100
Naphthalene U 0.00100 0.00500
n-Propylbenzene U 0.0000993 0.00100
Styrene U 0.000118 0.00100
1,1,1,2-Tetrachloroethane U 0.000147 0.00100
1,1,2,2-Tetrachloroethane U 0.000133 0.00100
Tetrachloroethene U 0.000300 0.00100
Toluene U 0.000278 0.00100
1,2,3-Trichlorobenzene U 0.000230 0.00100
1,2,4-Trichlorobenzene U 0.000481 0.00100
1,1,1-Trichloroethane U 0.000149 0.00100
1,1,2-Trichloroethane U 0.000158 0.00100
Trichloroethene U 0.000190 0.00100
Trichlorofluoromethane U 0.000160 0.00500
1,2,3-Trichloropropane U 0.000237 0.00250
1,2,4-Trimethylbenzene U 0.000322 0.00100
1,3,5-Trimethylbenzene U 0.000104 0.00100
Vinyl chloride U 0.000234 0.00100
o-Xylene U 0.000174 0.00100
m&p-Xylenes U 0.000430 0.00200
Ethanol U 0.0420 0.100
(S) Toluene-d8 115 80.0-120
(S) 4-Bromofluorobenzene 107 77.0-126
(S) 1,2-Dichloroethane-d4 86.1 70.0-130
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3904852-1 03/23/23 11:41 • (LCSD) R3904852-2 03/23/23 12:04
Spike Amount LCS Result LCSD Result LCS Rec. LCSD Rec. Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
Acetone 0.0250 0.0241 0.0237 96.4 94.8 19.0-160 1.67 27
Acrolein 0.0250 0.0247 0.0238 98.8 95.2 10.0-160 3.71 26
Acrylonitrile 0.0250 0.0266 0.0276 106 110 55.0-149 3.69 20
Benzene 0.00500 0.00486 0.00522 97.2 104 70.0-123 7.14 20
Bromobenzene 0.00500 0.00482 0.00499 96.4 99.8 73.0-121 3.47 20
Bromodichloromethane 0.00500 0.00483 0.00508 96.6 102 75.0-120 5.05 20
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:23 12 of 17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Griffith Enterprise L1595581 03/24/23 08:30 12 of 17
QUALITY CONTROL SUMMARYWG2028890
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 L1595581-01,02
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3904852-1 03/23/23 11:41 • (LCSD) R3904852-2 03/23/23 12:04
Spike Amount LCS Result LCSD Result LCS Rec. LCSD Rec. Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
Bromoform 0.00500 0.00490 0.00497 98.0 99.4 68.0-132 1.42 20
Bromomethane 0.00500 0.00482 0.00462 96.4 92.4 10.0-160 4.24 25
n-Butylbenzene 0.00500 0.00506 0.00536 101 107 73.0-125 5.76 20
sec-Butylbenzene 0.00500 0.00517 0.00515 103 103 75.0-125 0.388 20
tert-Butylbenzene 0.00500 0.00511 0.00554 102 111 76.0-124 8.08 20
Carbon tetrachloride 0.00500 0.00478 0.00485 95.6 97.0 68.0-126 1.45 20
Chlorobenzene 0.00500 0.00534 0.00529 107 106 80.0-121 0.941 20
Chlorodibromomethane 0.00500 0.00533 0.00538 107 108 77.0-125 0.934 20
Chloroethane 0.00500 0.00549 0.00514 110 103 47.0-150 6.59 20
Chloroform 0.00500 0.00484 0.00493 96.8 98.6 73.0-120 1.84 20
Chloromethane 0.00500 0.00558 0.00571 112 114 41.0-142 2.30 20
2-Chlorotoluene 0.00500 0.00494 0.00533 98.8 107 76.0-123 7.59 20
4-Chlorotoluene 0.00500 0.00519 0.00519 104 104 75.0-122 0.000 20
1,2-Dibromo-3-Chloropropane 0.00500 0.00493 0.00479 98.6 95.8 58.0-134 2.88 20
1,2-Dibromoethane 0.00500 0.00543 0.00496 109 99.2 80.0-122 9.05 20
Dibromomethane 0.00500 0.00474 0.00497 94.8 99.4 80.0-120 4.74 20
1,2-Dichlorobenzene 0.00500 0.00478 0.00516 95.6 103 79.0-121 7.65 20
1,3-Dichlorobenzene 0.00500 0.00509 0.00513 102 103 79.0-120 0.783 20
1,4-Dichlorobenzene 0.00500 0.00476 0.00497 95.2 99.4 79.0-120 4.32 20
Dichlorodifluoromethane 0.00500 0.00586 0.00559 117 112 51.0-149 4.72 20
1,1-Dichloroethane 0.00500 0.00509 0.00510 102 102 70.0-126 0.196 20
1,2-Dichloroethane 0.00500 0.00454 0.00489 90.8 97.8 70.0-128 7.42 20
1,1-Dichloroethene 0.00500 0.00486 0.00552 97.2 110 71.0-124 12.7 20
cis-1,2-Dichloroethene 0.00500 0.00522 0.00529 104 106 73.0-120 1.33 20
trans-1,2-Dichloroethene 0.00500 0.00511 0.00523 102 105 73.0-120 2.32 20
1,2-Dichloropropane 0.00500 0.00493 0.00500 98.6 100 77.0-125 1.41 20
1,1-Dichloropropene 0.00500 0.00495 0.00512 99.0 102 74.0-126 3.38 20
1,3-Dichloropropane 0.00500 0.00572 0.00517 114 103 80.0-120 10.1 20
2,2-Dichloropropane 0.00500 0.00501 0.00514 100 103 58.0-130 2.56 20
Di-isopropyl ether 0.00500 0.00469 0.00488 93.8 97.6 58.0-138 3.97 20
Ethylbenzene 0.00500 0.00528 0.00524 106 105 79.0-123 0.760 20
Hexachloro-1,3-butadiene 0.00500 0.00532 0.00490 106 98.0 54.0-138 8.22 20
Isopropylbenzene 0.00500 0.00516 0.00506 103 101 76.0-127 1.96 20
p-Isopropyltoluene 0.00500 0.00503 0.00512 101 102 76.0-125 1.77 20
2-Butanone (MEK)0.0250 0.0234 0.0248 93.6 99.2 44.0-160 5.81 20
Methylene Chloride 0.00500 0.00529 0.00531 106 106 67.0-120 0.377 20
4-Methyl-2-pentanone (MIBK) 0.0250 0.0270 0.0259 108 104 68.0-142 4.16 20
Methyl tert-butyl ether 0.00500 0.00497 0.00504 99.4 101 68.0-125 1.40 20
Naphthalene 0.00500 0.00430 0.00460 86.0 92.0 54.0-135 6.74 20
n-Propylbenzene 0.00500 0.00507 0.00510 101 102 77.0-124 0.590 20
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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QUALITY CONTROL SUMMARYWG2028890
Volatile Organic Compounds (GC/MS) by Method 6200B-1997/6200B-2011 L1595581-01,02
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3904852-1 03/23/23 11:41 • (LCSD) R3904852-2 03/23/23 12:04
Spike Amount LCS Result LCSD Result LCS Rec. LCSD Rec. Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
Styrene 0.00500 0.00530 0.00514 106 103 73.0-130 3.07 20
1,1,1,2-Tetrachloroethane 0.00500 0.00549 0.00542 110 108 75.0-125 1.28 20
1,1,2,2-Tetrachloroethane 0.00500 0.00546 0.00541 109 108 65.0-130 0.920 20
Tetrachloroethene 0.00500 0.00560 0.00511 112 102 72.0-132 9.15 20
Toluene 0.00500 0.00528 0.00504 106 101 79.0-120 4.65 20
1,2,3-Trichlorobenzene 0.00500 0.00475 0.00482 95.0 96.4 50.0-138 1.46 20
1,2,4-Trichlorobenzene 0.00500 0.00466 0.00473 93.2 94.6 57.0-137 1.49 20
1,1,1-Trichloroethane 0.00500 0.00460 0.00487 92.0 97.4 73.0-124 5.70 20
1,1,2-Trichloroethane 0.00500 0.00537 0.00520 107 104 80.0-120 3.22 20
Trichloroethene 0.00500 0.00528 0.00504 106 101 78.0-124 4.65 20
Trichlorofluoromethane 0.00500 0.00469 0.00499 93.8 99.8 59.0-147 6.20 20
1,2,3-Trichloropropane 0.00500 0.00526 0.00528 105 106 73.0-130 0.380 20
1,2,4-Trimethylbenzene 0.00500 0.00499 0.00512 99.8 102 76.0-121 2.57 20
1,3,5-Trimethylbenzene 0.00500 0.00526 0.00534 105 107 76.0-122 1.51 20
Vinyl chloride 0.00500 0.00524 0.00548 105 110 67.0-131 4.48 20
o-Xylene 0.00500 0.00540 0.00503 108 101 80.0-122 7.09 20
m&p-Xylenes 0.0100 0.0106 0.0109 106 109 80.0-122 2.79 20
ethanol 0.250 0.338 0.240 135 96.0 10.0-160 J3 33.9 30
(S) Toluene-d8 116 110 80.0-120
(S) 4-Bromofluorobenzene 110 101 77.0-126
(S) 1,2-Dichloroethane-d4 86.0 90.1 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
MDL Method Detection Limit.
ND Not detected at the Reporting Limit (or MDL where applicable).
RDL Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
(S)
Surrogate (Surrogate Standard) - Analytes added to every blank, sample, Laboratory Control Sample/Duplicate and
Matrix Spike/Duplicate; used to evaluate analytical efficiency by measuring recovery. Surrogates are not expected to be
detected in all environmental media.
U Not detected at the Reporting Limit (or MDL where applicable).
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Original Sample The non-spiked sample in the prep batch used to determine the Relative Percent Difference (RPD) from a quality control
sample. The Original Sample may not be included within the reported SDG.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
J3 The associated batch QC was outside the established quality control range for precision.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS
¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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APPENDIX 2
Archie Elledge Treatment Plant 1500 Foot Radius Property Owners
1. Kontos Gus D, Kontos, Soula
2880 Carrollwood Dr
Winston Salem NC 27103
Site Address: 2498 Armstrong Drive, Winston-Salem, NC
Parcel ID: 6813-25-2858 (NO WELL: SEE EMAIL)
2. Kontos Gus D, Kontos, Soula
2880 Carrollwood Dr
Winston Salem NC 27103
Site Address: 2494 Armstrong Drive, Winston-Salem, NC
Parcel ID: 6813-25-1818 (NO WELL: SEE EMAIL)
3. Carros Properties LLC
2150 Country Club Road, Suite 230
Winston-Salem, NC 27104
Site Address: 2490 Armstrong Drive, Winston-Salem, NC
Parcel ID: 6813-15-9888 (NO RESPONSE TO SURVEY, NO WELL OBSERVED
4. AAA STORAGE MANAGEMENT 13 LLC
7622 Bentley Rd
Greensboro NC 27409
Site Address: 2790 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-15-8697 (NO WELL: SEE EMAIL)
5. KRITES A HARRISON
150 CROYDEN DR
KERNERSVILLE NC 27284
Site Address: 2800 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-25-0589 (NO WELL: SEE EMAIL/VOICE MAIL RECEIPT)
6. RANSOM C WEATHERMAN JR TRUST
PO BOX 283
CLEMMONS NC 27012
Site Address: 2774 Nieman Industrial Drive, Winston-Salem, NC
Parcel ID: 6813-15-7732 (YES: WSW confirmed in 2022: No Response this time)
7. RANSOM C WEATHERMAN JR TRUST
PO BOX 283
CLEMMONS NC 27012
Site Address: 0 Nieman Industrial Drive, Winston-Salem, NC
Parcel ID: 6813-15-6712 (VACANT LOT: No Response this time)
8. Lowder Recycling And Disposal Llc
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 2785 Nieman Industrial Drive, Winston-Salem, NC
Parcel ID: 6813-15-5556: (NO WELL: SEE EMAIL)
9. Lowder Recycling And Disposal Llc
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 0 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-15-3398 (NO WELL: SEE EMAIL)
10. Lowder, Marvin Eugene
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 0 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-15-6348 (NO WELL: SEE EMAIL)
11. Lowder Recycling And Disposal Llc
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 2804 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-15-8379 (NO WELL: SEE EMAIL)
12. 2810 Griffith LLC
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 2810 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-15-6135 (NO WELL: SEE EMAIL)
13. Lowder, Marvin Eugene
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 2840 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-14-4874 (NO WELL: SEE EMAIL)
14. Lowder, Marvin Eugene
2810 Griffith RD
Winston-Salem NC 27103
Site Address: 0 Westpoint Blvd., Winston-Salem, NC
Parcel ID: 6813-04-9865 (NO WELL: SEE EMAIL)
15. Newsom Stephen P
PO BOX 24248
Winston Salem NC 27114
Site Address: 110 Salem Creek Drive, Winston-Salem, NC
Parcel ID: 6813-14-0286 (NO RESPONSE TO SURVEY, NO WELL OBSERVED)
16. GRUBBS DAWN THOMAS, GRUBBS FLETCHER KENT
356 NATALIE DR
WINSTON-SALEM NC 27104
Site Address: 2900 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-14-2274 (NO WELL: FLETCHER GRUBBS INTERVIEW)
17. NAFE SCOTT D
201 ELKIN HWY STE F
N WILKSBORO NC 28659
Site Address: 2910 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-14-1414 (NO WELL: SEE WSW FORM)
18. City Of Winston Salem
PO BOX 2511
Winston Salem NC 27102
Site Address: 2927 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-13-7798 (NO WELL: ELLEDGE WWTP STAFF INTERVIEW)
19. City Of Winston Salem
PO BOX 2511
Winston Salem NC 27102
Site Address: 2799 Griffith Road, Winston-Salem, NC
Parcel ID: 6813-35-0360 (NO WELL: ELLEDGE WWTP STAFF INTERVIEW
20. City Of Winston Salem
PO BOX 2511
Winston Salem NC 27102
Site Address: 0 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-44-2610 (NO WELL: ELLEDGE WWTP STAFF INTERVIEW
21. City Of Winston Salem
PO BOX 2511
Winston Salem NC 27102
Site Address: 2301 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-43-7386 (WSW WELL LOCATED IN HOBBY PARK at 2,650 feet away)
22. City Of Winston Salem
PO BOX 2511
Winston Salem NC 27102
Site Address: 0 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-23-0120 (NO WELL: VACANT LOT)
23. Brown Laura H
2365 W Clemmonsville Rd
Winston Salem NC 27127
Site Address: 2365 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-23-6133 (YES: WSW confirmed in 2022: No Response this time)
24. Brown David H
2367 W Clemmonsville Rd
Winston Salem NC 27127
Site Address: 2367 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-23-4620 (YES: WSW confirmed in 2022: No Response this time)
25. Patsy T Haga Irrevocable Trust
177 Wintergreen DR
GARNER NC 27529
Site Address: 2385 W Clemmonsville Road, Winston-Salem, NC
Parcel ID: 6813-22-3839 (YES WSW: SEE WSW Form 2 Residences Connected)
APPENDIX 3
North Carolina 15A NCAC 02B Water Quality Standards for Surface Waters
Freshwater Fresh & Salt Saltwater
Class B Class WS
(I - V)
All waters
(Class C)
All waters (Class
C & SC)
All waters
(Class SC)Class SB Class SA Supplemental Classifica8ons
Pollutant or Parameter CAS #
Primary
Recrea9on8
Water
Supply6
Aqua9c Life1 &
Secondary
Recrea9on4
Fish
Consump9on3
Aqua9c Life1 &
Secondary
Recrea9on4
Primary
Recrea9on8 Shellfish9 Trout2 Swamp
Waters5
High
Quality
Waters7 Synonyms & Other Informa9on
Cancer
Endpoint10
(FC & WS)
Reference Source (See
suppor8ng info tab)
All values reported as ug/L unless labeled otherwise.
Aldrin 309-00-2 0.00005 0.002 0.00005 0.003 Yes EPA QCW 1986; EPA
HHCCM 2002
Ammonia 2000 (E)As Total Ammonia Nitrogen
(TAN) Effluent Limit.NA NC
Arsenic11 7440-38-2 10 (t)
Acute: 340
(d) Chronic:
150 (d)
10 (t)
Acute: 69
(d) Chronic:
36 (d)
Dissolved metal for aqua8c life,
Total metal for HH & WS Yes EPA NRWQC (AL); EPA
NPDWR 2006
Barium 7440-39-3 1000 (t)No IRIS & RAIS 11/08
Benzene 71-43-2 1.19 51 Yes IRIS 2000
Beryllium11 7440-41-7
Acute: 65
(d) Chronic:
6.5 (d)
Dissolved metal for aqua8c life NA
NC calcula8on. Based
on LC50 data from EPA
AWQC 1980
Biological Oxygen
Demand (BOD)5000 (E)Effluent Limit NA NC
Cadmium11 7440-43-9
Acute:
Calc (d,h)
Chronic: Calc
(d,h)
Acute: 40
(d) Chronic:
8.8 (d)
Acute:
Calc
(d,h)
Click to calculate
freshwater aqua8c life
standard
NA EPA AWQC 2001 + GEI-
CED recalcula8on
Carbon Tetrachloride 56-23-5 0.254 1.6 Benzinoform, Carbon Chloride Yes EPA NRWQC(HH) 2002
Chlordane 57-74-9 0.0008 0.004 0.0008 0.004 Yes EPA NRWQC(HH) 2002;
EPA AWQC 1980
Chloride 16887-00-6 250000 230000 No EPA NRWQC(AL); EPA
NSDWR
Chlorine, Total Residual 7782-50-5 17 (N, Tr +
HQW)
TRC. For trout, see entry for
"Disinfec8on" in 15A NCAC 02B
.0224
NA EPA QCW 1986
Chlorinated Benzenes NA 488 (total)Total of all Chlorinated
Benzenes NA EPA AWQC 1980
Chlorinated Phenols NA 1.0 (N)
aesthe8c
Aesthe8c standard. See 15A
NCAC 02B .0211 and .0212 NA EPA AWQC 1980 & EPA
QCW 1976
Chlorophyll-a,
Corrected 479-61-8 40 (N)40 (N)15 (N)See 15A NCAC 02B .0211, .0220,
and .0223 NA NC
Chromium III11 16065-83-1
Acute:
Calc (d,h)
Chronic: Calc
(d,h)
Click to calculate
freshwater aqua8c life
standard
NA EPA NRWQC-Correc8on
1999
Chromium VI11 18540-29-9
Acute: 16
(d) Chronic:
11 (d)
Acute:
1100 (d)
Chronic: 50
(d)
Hexavalent Chromium;
Dissolved metal for aqua8c life NA EPA NRWQC-Correc8on
1999
Coliform Bacteria, Fecal NA ≤ 200/100 mL ≤ 200/100 mL
≤ 14/100 mL
and ≤ 43/100
mL
See 15A NCAC 02B .0211, .0219
& .0222 for addi8onal
requirements
NA NC; EPA NRWQC 1986;
FDA NSSP for SA waters
Copper11 7440-50-8
Acute:
Calc (d,h)
Chronic: Calc
(d,h)
Acute:
4.8 (d) Chronic:
3.1 (d)
Click to calculate
freshwater aqua8c life
standard
NA EPA NRWQC-Correc8on
1999
Cyanide, Total 57-12-5 5 1 NA EPA NRWQC 2009
2,4-D 94-75-7 70 2,4-Dichlorophenoxy Ace8c
Acid, Chlorophenoxy Herbicide No 40 CFR 141.50
4,4’-DDT 50-29-3 0.0002 0.001 0.0002 0.001 Dichlorodiphenyltrichloroethan
e Yes EPA AWQC 1980 (AL);
NRWQC 2002 (HHCCM)
Demeton 8065-48-3 0.1 0.1 NA EPA QCW 1986
Dieldrin 60-57-1 0.00005 0.002 0.00005 0.002 Yes EPA QCW 1986
Dioxin (2,3,7,8-TCDD)1746-01-6 0.000005
ng/L 0.000005 ng/L 2,3,7,8-Tetrachlorodibenzo-p-
dioxin Yes EPA NRWQC 2002
(HHCCM)
Dissolved Gases NA 110% sat (N)110% sat (N)Measured as % satura8on. See
15A NCAC 02B .0211 and .0220 NA EPA QCW 1986
Dissolved Oxygen NA (N)(N)≥6.0 mg/
L (N)(N)6 mg/L (E)
See 15A NCAC 02B .0211 and
.0220 for addi8onal
requirements. Effluent Limit for
HQW
NA EPA QCW 1986, NC for
HQW
Dissolved Solids NA 500000 Total dissolved solids NA EPA QCW 1986
Endosulfan 115-29-7 0.05 0.009 NA EPA AWQC 1980
Endrin 72-20-8 0.002 0.002 NA EPA AWQC 1980
Enterococcus Bacteria NA ≤ 35/100 mL ≤ 35/100 mL
See 15A NCAC 02B .0220 &
.0222 for addi8onal
requirements
NA BEACH Act 2000
Fluoride 16984-48-8 1800 NA ECOTOX
Guthion 86-50-0 0.01 0.01 NA EPA QCW 1986
Hardness NA 100 mg/L As CaCO3 or Ca & Mg NA EPA QCW 1963
Heptachlor 76-44-8 0.00008 0.004 0.00008 0.004 Yes EPA NRWQC(HH) 2002;
EPA AWQC 1980
Hexachlorobutadiene 87-68-3 0.44 18 HCBD Yes EPA NRWQC 2002
(HHCCM)
Lead11 7439-92-1
Acute:
Calc (d,h)
Chronic: Calc
(d,h)
Acute:
210 (d)
Chronic: 8.1
(d)
Click to calculate
freshwater aqua8c life
standard
NA
EPA AWQC - Lead 1984;
EPA NRWQC-Correc8on
1999
Lindane, g-BHC 58-89-9 0.01 0.004 Gamma-BHC, g-HCH NA EPA QCW 1976
Mercury 7439-97-6 0.012 (t)0.025 (t)NA
EPA QCW - Mercury
1986; Based on Final
Residual Value (fish
8ssue)
Methoxychlor 72-43-5 0.03 0.03 NA EPA QCW 1986
Methylene-blue Ac8ve
Substances (MBAS)61-73-4 500 (N)
aesthe8c
See 15A NCAC 02B .0212, .0214,
.0215, .0216, and .0218 NA EMC adopted for
aesthe8cs in 2003
Mirex 2385-85-5 0.001 0.001 NA EPA QCW 1986
1
Nickel11 744-02-0 25 (t)
Acute:
Calc (d,h)
Chronic: Calc
(d,h)
Acute: 74
(d) Chronic:
8.2 (d)
Click to calculate
freshwater aqua8c life
standard
No EPA NRWQC-Correc8on
1999
Nitrate nitrogen 14797-55-8 10000 No EPA QCW 1986
Non-point Source NA (N) See 15A NCAC 02B .0212.
Includes stormwater.NA NC
Nutrients (N) Nitrogen & Phosphorus. See
15A NCAC 02B .0223 & .0224.NA NC
Oil and Grease NA (N)(N)See 15A NCAC 02B .0211 and
.0220.NA EPA QCW 1976
Parathion 56-38-2 0.013 0.178 NA EPA AWQC 1986
PCB, Total NA 0.001 (total)0.000064 (total)0.001 (total)
Total of all polychlorinated
biphenyls (PCBs) and all
congeners.
Yes EPA QCW 1976; EPA
NRWQC 2002 (HHCCM)
pH NA 6.0-9.0 (N)6.8-8.5 (N)(N)See 15A NCAC 02B .0211 and
.0220 for addi8on requirements NA EPA QCW 1976
Phenolic Compounds NA 300 (P)
aesthe8c
300 (P)
aesthe8c
Aesthe8c narra8ve standard for
taste & odor in fish 8ssue.
Based on public policy
document.
NA EPA QCW 1976
Polynuclear Aroma8c
Hydrocarbons (PAH),
Total
NA 0.0028
(total)0.0311 (total)
Total of benzo(a)anthracene,
benzo(a)pyrene,
benzo(b)fluoranthene,
benzo(k)fluoranthene,
chrysene,
dibenz(a,h)anthracene, and
indeno(1,2,3-cd)pyrene
Yes EPA QCW 1986
Radioac8ve Substances NA (N)(N)See 15A NCAC 02B .0211 and
.0220 for details NA 40 CFR 141.26 (adopted
by reference)
Salinity NA (N)See 15A NCAC 02B.0220 NA EPA QCW 1986
Selenium 7782-49-2 5 (t)71 (t)NA EPA AWQC 1987
Sewage & other wastes NA (N) (N) (N) (N)
See 15A NCAC 02B .0211, .0220
& .0221. Includes sewage,
industrial wastes, non-process
industrial waste, or other
wastes
NA
Silver11 7440-22-4
Acute: Calc
(d,h) Chronic:
0.06 (d)
Acute: 1.9
(d) Chronic:
0.1 (d)
Click to calculate acute
freshwater aqua8c life
standard
NA EPA AWQC 1980
Silvex 93-72-1 10 2,4,5-TP, 2,4,5-
Trichlorophenoxypropionoic Acid No EPA QCW 1986
Solids NA (N)(N)(N)
See 15A NCAC 02B .0211, .0220
& .0221. Includes floa8ng,
senleable & sludge solids.
NA EPA QCW 1986
Sulfates NA 250000 NA NSDWR 2003
Suspended Solids NA
10000
(E, Tr+
HQW)
20000 (E)Total suspended solids Effluent
Limit. See 15A NCAC 02B .0224 NA EPA QCW 1986
Temperature NA (N)(N)NCAC 02B .0208, .0211, and
.0220 for details NA EPA QCW 1986
1,1,2,2-
Tetrachloroethane 79-34-5 0.17 4 Acetosol, Acetylene
Tetrachloride Yes EPA NRWQC(HH) 2006
Tetrachloroethylene 127-18-4 0.7 3.3 PERC, PCE, Perchloroethylene Yes EPA NRWQC(HH) 2006
Toluene 108-88-3 11 0.36 Methyl Benzene, Phenyl
Methane NA
NC Dept. of Natural
Resources and Community
Development study 1986
Toxaphene 8001-35-2 0.0002 0.0002 NA EPA AWQC 1986
Toxic Substances (E)
Effluent Limit. See 15A NCAC
02B .0224 for addi8onal
requirements
NA NC
Trialkyl8n compounds NA 0.07 0.007 Expressed as Tributyl8n NA EPA NRWQC 2004
Trichloroethylene 79-01-6 2.5 30 TCE Yes EPA NRWQC(HH) 2002
Turbidity NA
Streams ≤
50 NTU,
Lakes &
Reservoirs ≤ 25
NTU (N)
≤ 25 NTU (N)
≤ 10
NTU
(N)
See 15A NCAC 02B .0211 and
.0220 for more details. NTU =
Nephelometric Turbidity Units
NA EPA QCW 1972
Vinyl Chloride 75-01-4 0.025 2.4 Chloroethylene Yes EPA NRWQC(HH) 2006
Zinc11 7440-66-6
Acute: Calc
(d,h) Chronic:
Calc (d,h)
Acute: 90
(d) Chronic:
81 (d)
Click to calculate
freshwater aqua8c life
standard
NA EPA NRWQC-Correc8on
1999
The values in these tables do not subs8tute for any wrinen regula8ons, nor are they themselves regula8ons.
Hardness-Dependent Metal Calcula9ons
Metal Equa8ons for Hardness-Dependent Metals (ug/L)Enter in-stream hardness
(mg/L)Calculated standard (ug/L)
Cadmium, acute WER*[{1.136672-[ln hardness](0.041838)}*e^{0.9151[ln hardness]-3.1485}]0
Cadmium, chronic WER*[{1.101672-[ln hardness](0.041838)}*e^{0.7998[ln hardness]-4.4451}]0
Cadmium, acute, trout waters WER*[{1.136672-[ln hardness](0.041838)}*e^{0.9151[ln hardness]- 3.6236}]0
Chromium III, acute WER*[0.316*e^{0.8190[ln hardness]+3.7256}]0
Chromium III, chronic WER*[0.860*e^{0.8190[ln hardness]+0.6848}]0
Copper, acute WER*[0.960*e^{0.9422[ln hardness]-1.700}]0
Copper, chronic WER*[0.960*e^{0.8545[ln hardness]-1.702}]0
Lead, acute WER*[{1.46203-[ln hardness](0.145712)}*e^{1.273[ln hardness]-1.460}]0
Lead, chronic WER*[{1.46203-[ln hardness](0.145712)}*e^{1.273[ln hardness]-4.705}]0
Nickel, acute WER*[0.998*e^{0.8460[ln hardness]+2.255}]0
Nickel, chronic WER*[0.997*e^{0.8460[ln hardness]+0.0584}]0
Silver, acute WER*[0.85*e^{1.72[ln hardness]-6.59}]0
Zinc, acute WER*[0.978*e^{0.8473[ln hardness]+0.884}]0
Zinc, chronic WER*[0.986*e^{0.8473[ln hardness]+0.884}]0
2
See the Suppor8ng Info tab for informa8on on all footnotes, notes, and abbrevia8ons
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