HomeMy WebLinkAbout17056_2014APR-Limited GW & Sediment Report_S&MELimited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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1.0 INTRODUCTION.................................................................................1
2.0 PROJECT BACKGROUND AND PURPOSE ........................................1
3.0 SITE ACTIVIITES...............................................................................3
3.1 HEALTH AND SAFETY ...................................................................................................... 3
3.2 GROUNDWATER ............................................................................................................... 3
3.3 SEDIMENT ........................................................................................................................ 3
4.0 RESULTS ...........................................................................................5
4.1 GROUNDWATER ............................................................................................................... 5
4.2 SEDIMENT ........................................................................................................................ 5
5.0 CONCLUSIONS..................................................................................7
5.1 GROUNDWATER ............................................................................................................... 7
5.2 SEDIMENT ........................................................................................................................ 7
Tables
Table 1 Temporary Monitor Well Completion Details
Table 2 Sample Location Coordinates
Table 3 Field Parameters
Table 4 Summary of Groundwater Analytical Data
Table 5 Summary of Sediment Analytical Data
Table 6 Grain Size Analysis
Figures
Figure 1 Vicinity Map
Figure 2 Site Map with Sampling Locations
Figure 3 Monitor Well Sampling Results Map
Figure 4 Sediment Sampling Results Map
Appendices
Appendix I Photographic Log
Appendix II Laboratory Analytical Report
Appendix III Charts
Appendix IV Grain Size Analysis Reports
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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1.0 INTRODUCTION
S&ME, Inc.’s scope of services were performed in general accordance with proposal number 43-
14000148 Revision 1.2, dated February 26, 2014, and as authorized by the North Carolina
Department of Environment and Natural Resources (NCDENR) Task Authorization dated
February 26, 2014 under Contract #N10005S.
S&ME completed the following scope of services approved for this task authorization:
Prepared a site specific health and safety plan;
Installed four temporary monitor wells;
Collected groundwater samples from the four temporary monitor wells and two existing
monitor wells, MW-3 and MW-10;
Submitted groundwater samples for laboratory analysis for volatile organic compounds
(VOCs) by EPA Method 8260B, semi-volatile organic compounds (SVOCs) by EPA
Method 8270D, and metals by EPA Method 6010C;
Collected 43 sediment samples from the South Fork of the Catawba River, including
nine background samples and five down-stream samples from 18 stream sample
locations;
Submitted sediment samples for laboratory analysis for metals by EPA Method 6010C,
and for SVOCs by EPA Method 8270D (background and downstream samples were
analyzed for metals only);
Submitted sediment samples for grain size analysis according to ASTM Method D422-
L002; and,
Prepared this report.
2.0 PROJECT BACKGROUND AND PURPOSE
The Crompton & Knowles site (State ID No. NCD044444735) is located at 1602 North Main
Street, Lowell, Gaston County, North Carolina (Figures 1 and 2). The site is a former industrial
complex and is currently unoccupied. The approximate central coordinates are 35.2858° north
latitude and 81.1049° west longitude. The Crompton & Knowles site was a textile dye
manufacturing facility that operated between 1958 and 2004. Facility names associated with the
site include Yorkshire Americas Dye & Chemicals Corp. (1996-2004), Crompton & Knowles
(1978- 1995), Harshaw Chemicals (1968-1978), Belle Chemical (1961-1968), and Gaston
Chemical (1958-1960). Groundwater contamination was discovered during Crompton &
Knowles ownership years and Yorkshire Americas operated the groundwater treatment system
during its operational years. Chemtura Chemical, a successor to Crompton & Knowles, was
identified as the responsible party for the groundwater contamination from 2004 until its
bankruptcy in 2010.
The current property owner, Kings Mountain Venture #1 LLC, purchased the facility property in
2006 through bankruptcy court. Kings Mountain Venture #1 LLC sold some of the equipment
and proposed to develop the property for mixed use (residential, commercial, and office space)
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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under the North Carolina Brownfields Agreement. As of the date of this report, the agreement is
not finalized.
The site is currently vacant. A groundwater contaminant plume is present in the unconfined
groundwater aquifer. The chemicals of concern are primarily trimethylbenzenes, polynuclear
aromatic hydrocarbons, and suspect metals, including arsenic, chromium, copper, manganese,
and nickel. The immediate groundwater contaminant plume receptor is the South Fork of the
Catawba River.
On February 6, 2014, Mr. Ed Woloszyn of S&ME, Inc. (S&ME), Mr. James Batson and Mr.
Harry Zinn of the NCDENR Inactive Hazardous Sites Branch (IHSB), Ms. Sharon Eckard of the
Brownfields Program, Tom McKittrick of Kings Mountain Ventures, and other stakeholders met
at the site. The purpose of the meeting was to discuss the scope of services requested by IHSB
and to be performed by S&ME. Mr. Woloszyn walked the property along the perimeter to
identify locations for the installation of temporary monitor wells and to evaluate river access in
advance of collecting sediment samples from the south bank. A photographic log of the
activities performed is provided in Appendix I.
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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3.0 SITE ACTIVITIES
3.1 Health and Safety
Prior to site activities, S&ME prepared a site specific health and safety plan to comply with 29
CFR 1910.120, hazardous waste operations and emergency response (HAZWOPER) rule for the
protection of workers at uncontrolled hazardous sites prior to commencing field activities.
3.2 Groundwater
On March 10 and 11, 2014, S&ME advanced four borings with a hand auger and installed a
temporary monitor well in each boring. The wells were constructed of 5 feet of 1-inch PVC
0.010-inch slotted screen and 1-inch PVC riser to the ground surface. Temporary monitor wells
TW-1 and TW-3 were installed at approximately 6 feet below ground surface (ft. bgs.), and TW-
2 and TW-4 were installed at 7 ft. bgs. Each boring was advanced to auger refusal. A filter pack
consisting of #2 washed sand was installed in the annulus surrounding the well to one foot above
the well screen. The temporary monitor well completion details are presented in Table 1. The
locations of the temporary monitor wells were recorded using a Trimble Geoexplorer 6000
Series global positioning system (GPS) unit. The coordinates are presented in Table 2, and the
well locations are shown in Figure 2.
On March 11 and 12, 2014, S&ME personnel sampled temporary monitor wells TW-1 through
TW-4 and monitor wells MW-3 and MW-10. Prior to sampling, depth to water was measured
using a water level indicator. The depth to groundwater measurements are included in Table 1.
The wells were sampled using a peristaltic pump and dedicated ¼” polyethylene and silicone
tubing. Field parameters including pH, temperature, specific conductance, oxidation-reduction
potential, and turbidity were monitored using a YSI 6920 multi meter with a flow-through cell.
Parameters were recorded approximately every three minutes until the parameters stabilized; the
turbidity was reduced to below 10 nephelometric turbidity units (ntu) where possible. The field
parameter measurements are summarized in Table 3.
Groundwater samples were collected directly into laboratory supplied containers, placed in a
cooler on ice, and shipped under standard chain-of-custody procedure to ENCO Laboratories of
Cary, North Carolina, a North Carolina Certified Laboratory. Samples were analyzed for VOCs
by EPA Method 8260B, SVOCs by EPA Method 8270D, and for five metals (arsenic, chromium,
copper, manganese, and nickel) by EPA Method 6010C. A copy of the laboratory analytical
report is included in Appendix II. For quality assurance/quality control (QA/QC), one duplicate
sample, one equipment blank, and one trip blank were submitted for analysis.
3.3 Sediment
On March 27 and 28, 2014, S&ME personnel collected 43 sediment samples (SS-1 through SS-
29, B-1 through B-9, and D-1 through D-5) at 18 stream stations along the South Fork of the
Catawba River (Figure 3). Samples were collected from a boat using a hand auger which was
decontaminated between borings. At each station, one sample was collected from the sediment
at the water line, one below the waterline, and a third sediment sample from at a deeper depth
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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below the water line, if possible. The sample depths for samples collected below the water line
varied in depth from 1.5 to 7.0 feet, dependent upon the depth of the river and the depth to auger
refusal. Background samples B-1 through B-9 were collected upstream from the site, and the
downstream samples D-1 through D-5 were collected downstream of the site. The locations of
the stream stations at which the samples were collected are shown in Figure 2.Table 2
documents the coordinates of each stream station.
Each sediment sample was split into two portions. One portion was collected into laboratory
supplied containers, placed in a cooler on ice and shipped under standard chain-of-custody
procedures to ENCO Laboratories for analysis for five metals (arsenic, chromium, copper,
manganese, and nickel) by EPA Method 6010C and for SVOCS by EPA Method 8270D. A
second portion was collected into jars for sediment grain size analysis by ASTME Method D422-
L002 at S&ME’s soils laboratory in Raleigh, North Carolina. One duplicate sample and one
equipment rinsate sample were collected per day, and one trip blank was included in each cooler.
The QA/QC samples were included in the laboratory analysis with the exception of the grain size
analysis.
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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4.0 RESULTS
4.1 Groundwater
The laboratory analytical results of the groundwater samples collected on March 11 and 12, 2014
indicated that the following constituents were reported at concentrations above their respective
15A NCAC 2L Groundwater Standards (2L Standards):
1,2,4-trichlorobenzene in MW-3;
1,4-dichlorobenzene in MW-3;
Benzene in MW-3;
Manganese in TW-2, TW-3, MW-3 and MW-10; and,
Chromium in TW-3.
Additional constituents were reported at concentrations above the laboratory analytical method
detection limits, but below their respective 2L Standards in the groundwater samples collected
from temporary monitor wells TW-1 through TW-4, and permanent monitor wells MW-3 and
MW-10. A summary of the groundwater analytical results is presented in Table 4 and shown in
Figure 3, and a copy of the laboratory analytical report in presented in Appendix II.
The laboratory analytical results of the QA/QC samples indicated that the Duplicate sample
results, which was collected from monitor well MW-3, were within 20 percent the of the record
sample results. No VOCs were reported in the trip blank or the equipment blank. No SVOCs
were reported in the equipment rinsate sample. One metal, manganese, was reported at a
concentration of 1.68 µg/L in the equipment rinsate sample. The concentration was flagged “J”
as an estimated concentration, indicating that the detection was below the laboratory reporting
limit but above the analytical method’s detection limit.
4.2 Sediment
The laboratory analytical results of the sediment samples collected March 24 and 25, 2014,
indicated the following constituents were reported at concentrations above their respective IHSB
Preliminary Soil Remediation Goals (PSRGs) for residential (unrestricted use) health-based
concentrations:
Arsenic in samples SS-5, SS-7 through SS-29, BG-1 through BG-9, and DS-1 through
DS-5;
Chromium in all samples collected. Because hexavalent chromium was not analyzed, the
results represent total chromium, trivalent and hexavalent chromium combined, the more
stringent regulatory standard was applied. If based upon the assumption that trivalent
chromium constituent present in the sediment samples, then none of sample results
exceed the PSRGs.
Manganese in samples SS-2 through SS-7, SS-10 through SS-12, SS-15 through SS-17,
SS-19 through SS-24, SS-26, SS-27, SS-29, BG-1, BG-2, BG-9, and DS-3; and,
Benzo(a) pyrene in sample SS-17.
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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Industrial exposure scenario health-based concentrations were also compared to the sample
concentrations. Additional constituents were reported at concentrations above the laboratory
method detection limits but below their respective PSRGs. A summary of the sediment sample
analytical results is presented in Table 5 and shown in Figure 4. Charts of metals
concentrations in sediment samples are presented in Appendix III. A copy of the laboratory
analytical report is provided in Appendix II.
The laboratory analytical results of the QA/QC samples indicated that the duplicate samples
were within an acceptable range of the record sample values; Replicate 1 is a duplicate of sample
BG-7, and Replicate 2 is a duplicate of sample SS-29. One constituent, manganese, was reported
at in the equipment blank sample. The detection was flagged with a “J”, indicating that the
detection was below the laboratory reporting limit and is an estimated concentration.
The grain size analysis of the soil samples indicated that the river sediments consist
predominantly of sandy clayey silt, clayey silt, sandy silt, and silty sand. The general grain size
distribution of the samples is presented in Table 6. Charts of the grain size distribution are
presented in Appendix III. Copies of the individual sediment grain size analysis reports are
provided in Appendix IV.
Limited Groundwater and Sediment Assessment Report April 28, 2014
Crompton & Knowles Corp, Lowell, Gaston County, North Carolina S&ME Project No. 1054-14-2084
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5.0 CONCLUSIONS
A limited groundwater and sediment assessment was conducted at the Crompton & Knowles
Corp. Site, located at 1602 North Main Street, Lowell, Gaston County, North Carolina. The
results of the site activities are summarized below.
5.1 Groundwater
Laboratory analytical results of groundwater samples collected from four temporary and two
permanent monitor wells indicated that VOCs were reported at concentrations above their
respective 2L Standards in monitor well MW-3. Manganese was reported above the 2L standard
in permanent well MW-10, but no VOCS or SVOCs were above North Carolina’s ground quality
standard. No VOCs or SVOCs were reported in the groundwater samples collected from the
temporary monitor wells TW-1 through TW-4. The detections of manganese in the temporary
monitor wells as well as in the permanent monitor wells indicate that manganese may be present
in the groundwater as a naturally occurring element. Chromium was reported at a concentration
above the 2L Standard in the groundwater sample collected from temporary monitor well TW-3.
In the absence of other chemicals of concern in at the locations of temporary well, the detection
of chromium in shallow groundwater may also be naturally occurring in the groundwater, but
due to elevated turbidity in the groundwater sample, there is some uncertainty if chromium is
present in the dissolved element in groundwater or if chromium is present in the soil minerals.
5.2 Sediment
The laboratory analytical results of the sediment samples collected from the South Fork of the
Catawba indicated that arsenic, chromium and manganese were reported at concentrations above
the PSRGs; however, the concentrations of these metals did not vary between background
samples and samples collected along the stream bank adjacent to the Crompton Knowles site.
The metals detected, therefore, could be naturally occurring. Charts of metals concentrations are
provided in Appendix III. One SVOC, benzo(a)pyrene, was detected at a concentration above
the PSRGs in sample SS-17, respectively. Since SVOCs are constituents of concern at the site,
the detections of these SVOCs in the sediment samples may be related to the chemicals of
concern historically reported in the groundwater at the site.
The grain size analysis results indicated that sediments in the South Fork of the Catawba River in
the vicinity of the site are predominantly fine grained, and consist of sandy clayey silts, sandy
silts, clayey silts, and silty sandy clays. The grain size distribution is likely a function of the
depositional environment.
TABLES
Well ID Date Installed Total Depth
(ft. bgs.)
Screen Interval
(ft. bgs.)
Riser Interval
(ft. bgs.)
Depth to
Groundwater
(ft. bgs.)
TW-1 3/10/2014 6 6-1 1-0 4.67
TW-2 3/11/2014 7 7-2 2-0 4.00
TW-3 3/10/2014 6 6-1 1-0 4.23
TW-4 3/11/2014 7 7-2 2-0 4.10
Notes:
ft. bgs. = feet below ground surface
Table 1
Temporary Monitor Well Construction Details
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
TABLE 2
Sample Location Coordinates
IHSB Crompton Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Location ID X Y
T W -1 1371683.406 566278.746
T W -2 1372730.318 565178.5092
T W -3 1371730.916 566317.4135
T W -4 1372240.149 565928.0205
BG-1 1371719.042 566850.1323
BG-3 1371667.347 566725.1794
BG-6 1371661.084 566612.7499
BG-8 1371710.984 566479.5521
DS -1 1373039.072 565442.2874
DS -4 1372915.77 565481.1364
S S -1 1371983.782 566212.7052
S S -3 1372060.647 566162.0823
S S -6 1372162.096 566071.0663
S S -8 1372266.348 566000.7795
S S -11 1372291.421 565983.3482
S S -14 1372317.449 565949.0656
S S -17 1372376.438 565900.6132
S S -20 1372407.698 565871.5134
S S -22 1372441.668 565844.1109
S S -24 1372473.899 565808.12
S S -26 1372647.97 565677.3836
S S -28 1372536.382 565766.6752
N otes:
CoordinatesbaseduponN orthCarolinaP laneN AD83
TABLE 3
Field Parameters
IHSB Crompton Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Well ID Date Temperature
(°C)1
Specific
Conductance
(mS/cm)2
pH
(SU)3
ORP 4
(mV)5
Tubidity
(ntu)6
TW-1 3/10/2014 8.33 0.072 5.38 228.4 37.8
TW-2 3/11/2014 12.68 0.104 5.46 262.5 5.7
TW-3 3/10/2014 12.29 0.067 5.5 241.4 224.5 7
TW-4 3/11/2014 11.4 0.127 5.93 221.3 18.2 7
MW-3 3/11/2014 12.26 3.026 6.7 -45.2 154.3
MW-10 3/11/2014 13.37 1.887 7.13 15.3 5.6
Notes:
1. °C: degrees Celcius
2. mS/cm: milliSiemens per centimeter
3. SU: standard units
4. ORP: oxidation reduction potential
5. mV: millivolts
6. ntu: nephelometric turbidity units
7. Well was developed and purged in an effort to reduct the turbidity for one hour and samples the well when turbidity no longer decresed with time.
Sample ID TW-1 TW-2 TW-3 TW-4 MW-3 MW-10
Duplicate
(Duplicate
of MW-3)
EQ-1 Trip Blank
Date Collected
Analyte
1,2,3-Trichlorobenzene <0.01 <0.01 <0.01 <0.01 140D <0.01 130D <0.01 <0.01 NE
1,2,4-Trichlorobenzene <0.14 <0.14 <0.14 <0.14 470D <0.14 480D <0.14 <0.14 70
1,2-Dichlorobenzene <0.19 <0.19 <0.19 <0.19 <1.9 <0.19 4.2 <0.19 <0.19 20
1,3-Dichlorobenzene <0.15 <0.15 <0.15 <0.15 30D 15 36 <0.15 <0.15 200
1,4-Dichlorobenzene <0.19 <0.19 <0.19 <0.19 13D 0.77J 13D <0.19 <0.19 6
Benzene <0.15 <0.15 <0.15 <0.15 24D 0.65J 26D <0.15 <0.15 1
Chlorobenzene <0.17 <0.17 <0.17 <0.17 5.0JD 1.3 4.7JD <0.17 <0.17 50
cis-1,2-Dichloroethene <0.15 <0.15 <0.15 <0.15 <1.5 5.0 <1.5 <0.15 <0.15 70
trans-1,2-Dichloroethene <0.21 <0.21 <0.21 <0.21 <2.1 2.3 <2.1 <0.21 <0.21 100
1,1'-Biphenyl <1.5 <1.5 <1.5 <1.5 6.4J <1.5 7.3J <1.5 --400
2-Methylphenol <1.4 <1.4 <1.4 <1.4 2.1 <1.4 4.0 <1.4 --400*
3 & 4-Methylphenol <1.6 <1.6 <1.6 <1.6 15 <1.6 19 <1.6 --40**
4-Chloro-3-methylphenol <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 9.0 <1.5 --NE
4-Chloroaniline <1.2 <1.2 <1.2 <1.2 12J 2.1 13J <1.2 --NE
Bis(2-ethylhexyl)phthalate <1.7 <1.7 <1.7 <1.7 <1.7 <1.7 1.8J <1.7 --3
Naphthalene <1.3 <1.3 <1.3 <1.3 2.4J <1.3 2.7J <1.3 --6
Arsenic <5.40 <5.40 <5.40 <5.40 <5.40 <5.40 <5.40 <5.40 --10
Chromium <1.40 <1.40 26.5 <1.40 9.92J 1.84J 9.50J <1.40 --10
Copper 2.44J <1.60 44.5 <1.60 97.6 <1.60 96.2 <1.60 --1,000
Manganese 40.9 50.1 306 38.9 1,120 388 1,190 1.68J --50
Nickel <1.80 <1.80 10.4 <1.80 8.70J <1.80 8.15J <1.80 --100
Notes:
All parameters reported in micrograms per liter (ug/L)
VOCs: volatile organic compounds
SVOCs: semi-volatile organic compounds
NE: Regulatory standard not established for the listed parameter
--: analysis was not requested for the listed method.
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
*: most stringent standard based on 3-methylphenol
**: based on the interim maximum allowable concentrations (IMAC)
3/11/2014
2L Standards
3/11/20143/12/2014
TABLE 4
Summary of Groundwater Analytical Results
S&ME Project No. 1054-14-2084
IHSB Crompton-Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
3/12/2014 3/11/2014 3/11/20143/11/2014 3/11/2014
SVOCs by EPA Method
8270C
(ug/L)
Metals by EPA Method
6010C
(ug/L)
VOCs by EPA Method
8260B
(ug/L)
SpecificMethod
3/11/2014
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
page 1 of 7
Sample ID SS-1 SS-2 SS-3 SS-4 SS-5 SS-6
Date Collected 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014
3.04 3.70 3.42 5.24 6.26 2.51 0.61 69
24.6 19.7 24.7 35.5 44.4 19.5 Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
62.5 47.6 16.3 24.9 70.6 9.51 620 8,200
138 797 310 392 496 362 360 4,000
9.67 11.7 8.43 10.8 14.1 6.41 300 4,000
<0.13 <0.12 <0.14 <0.14 <0.16 <0.13 2.4 8.6
<0.039 <0.035 <0.041 <0.042 <0.048 <0.038 0.15 2.1
<0.045 <0.042 <0.048 <0.049 <0.056 <0.045 0.015 0.21
<0.025 <0.023 <0.026 <0.027 <0.031 <0.025 1.5 2.1
<0.048 <0.044 <0.051 <0.052 0.070J <0.048 35 120
<0.041 <0.038 <0.044 <0.045 <0.051 <0.041 15 210
<0.039 <0.035 <0.041 <0.042 <0.048 <0.038 9,800 98,000
<0.050 <0.046 <0.053 <0.054 <0.061 <0.049 460 4,400
<0.052 <0.048 <0.056 <0.057 <0.065 <0.052 340 3,400
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
page 2 of 7
SS-7 SS-8 SS-9 SS-10 SS-11 SS-12
3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014
3.36 2.73 3.84 6.02 5.81 5.39 0.61 69
21.7 22.1 34.5 35.8 33.1 44.9 Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
32.8 10.9 17.9 22.5 16.3 153 620 8,200
414 229 339 392 464 508 360 4,000
8.39 7.07 8.74 10.3 10.6 10.9 300 4,000
<0.13 <0.14 0.19J <0.15 <0.14 <0.16 2.4 8.6
<0.040 <0.041 <0.043 <0.044 <0.041 <0.049 0.15 2.1
<0.047 <0.049 <0.050 <0.052 <0.048 <0.058 0.015 0.21
<0.026 <0.027 <0.027 <0.028 <0.026 <0.031 1.5 2.1
<0.050 <0.052 <0.053 <0.055 <0.051 <0.061 35 120
<0.043 <0.044 <0.046 <0.047 <0.044 <0.052 15 210
<0.040 <0.041 <0.043 <0.044 <0.041 <0.049 9,800 98,000
<0.051 <0.053 <0.055 <0.057 <0.053 <0.063 460 4,400
<0.054 <0.056 <0.058 <0.060 <0.056 <0.066 340 3,400
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
page 3 of 7
SS-13 SS-14 SS-15 SS-16 SS-17 SS-18
3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014
3.77 4.37 6.13 6.78 6.64D 10.0 0.61 69
38.3 28.4 34.2 40.2 35.5D 43.5 Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
19.5 13.9 16.1 25.5 20.2D 23.8 620 8,200
322 284 377 614 820D 177 360 4,000
11.2 9.18 10.5 12.5 11.3JD 12.5 300 4,000
<0.14 <0.13 <0.14 <0.14 <0.13 <0.15 2.4 8.6
<0.043 <0.038 <0.041 <0.043 0.099J <0.047 0.15 2.1
<0.051 <0.045 <0.048 <0.051 0.080J <0.055 0.015 0.21
<0.028 <0.025 <0.026 <0.028 0.087 <0.030 1.5 2.1
<0.054 <0.048 <0.051 <0.054 <0.050 <0.058 35 120
<0.046 <0.041 <0.044 <0.046 0.071J <0.050 15 210
<0.043 <0.038 <0.041 <0.043 <0.040 <0.047 9,800 98,000
<0.056 <0.049 <0.052 <0.056 0.068J <0.060 460 4,400
<0.059 <0.052 <0.055 <0.059 0.11J <0.063 340 3,400
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
page 4 of 7
SS-19 SS-20 SS-21 SS-22 SS-23 SS-24
3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014
6.09 6.97 4.81B 5.52B 4.31B 5.89B 0.61 69
42.8 57.1 35.7 36.6 41.7 41.2 Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
25.2 39.4 24.4 23.5 19.5 40.9 620 8,200
502 492 372 993 436 612 360 4,000
12.0 17.9 20.6 12.6 13.9 12.7 300 4,000
<0.15 <0.17 <0.14 <0.15 <0.13 <0.16 2.4 8.6
<0.046 <0.050 <0.042 <0.046 <0.040 <0.048 0.15 2.1
<0.054 <0.059 <0.050 <0.055 <0.047 <0.056 0.015 0.21
<0.029 <0.032 <0.027 <0.030 <0.026 <0.031 1.5 2.1
<0.057 0.070J <0.053 <0.058 <0.050 <0.060 35 120
<0.049 <0.054 <0.045 <0.050 <0.043 <0.051 15 210
<0.046 <0.050 <0.042 <0.046 <0.040 <0.048 9,800 98,000
<0.059 <0.065 <0.054 <0.060 <0.051 <0.061 460 4,400
<0.062 <0.068 <0.057 <0.063 <0.054 <0.065 340 3,400
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
page 5 of 7
SS-25 SS-26 SS-27 SS-28 SS-29
Replicate2
(Record
sample SS-29)
3/24/2014 3/25/2014 3/25/2014 3/25/2014 3/25/2014 3/25/2014
4.52B 5.16B 8.16BD 5.58B 8.53BD 10.5BD 0.61 69
35.8 38.2 57.7D 51.4 56.5D 52.6D Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
18.9 31.1 32.6D 35.6 38.8D 44D 620 8,200
232 515 799D 132 680D 704D 360 3,600
10.6 12.7 18.9D 8.62 19.1D 17.9D 160 2,000
<0.13 <0.15 <0.15 <0.17 <0.15 <0.15 2.4 8.6
<0.040 <0.045 <0.046 <0.050 <0.045 <0.045 0.15 2.1
<0.047 <0.053 <0.054 <0.059 <0.053 <0.053 0.015 0.21
<0.026 <0.029 <0.029 <0.032 <0.029 <0.029 1.5 2.1
<0.050 <0.056 <0.057 <0.062 0.079J 0.066J 35 120
<0.043 <0.048 <0.049 <0.053 <0.048 <0.048 15 210
<0.040 <0.045 <0.046 <0.050 0.19J <0.045 9,800 98,000
<0.051 <0.058 <0.059 <0.064 <0.058 <0.058 460 4,400
<0.054 <0.061 <0.062 <0.068 <0.061 <0.061 340 3,400
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
page 6 of 7
BG-1 BG-2 BG-3 BG-4 BG-5 BG-6 BG-7
Replicate1
(Record sample
BG-7)
3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014 3/24/2014
3.85 6.82 3.19 3.04 4.59 1.96 6.81BD 4.08BD 0.61 69
56.8 46.6 27.7 18.2 37.5 9.45 35D 24.2D Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
82.0 25.2 24.1 15.0 22.3 41.3 16.7D 47.1D 620 8,200
379 421 201 119 277 290 168D 493D 360 4,000
42.0 13.1 9.15 5.77 11.0 4.93 9.98D 10.6JD 300 4,000
----------------
----------------
----------------
----------------
----------------
----------------
----------------
----------------
----------------
Residential Health
PSRG
Industrial Health
PSRG
TABLE 5
Summary of Sediment Sample Analytical Results
IHSB Crompton & Knowles Site NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID
Date Collected
Notes:
All constituents reported in milligrams per kilogram (mg/kg)
SVOC: semi-volatile organic compounds
PSRG: preliminary soil remediation goals
Constituents not shown were not detected for the method
J: detection is below the reporting limit- the value is estimated
D: sample analyzed at dilution
B: the constituent was detected in the associated method blank
Nickel PSRG is presented as Nickel Soluble Salts
Chromium PSRG is presented as hexevalent chromium and trivalent chromium
EPA 6010C
SVOCs by EPA 8270D
(mg/kg)
AnalyteSpecificMethod
Arsenic
Copper
Chromium
Manganese
Nickel
Chrysene
Diethylphthalate
Fluoranthene
Pyrene
4-Chloroaniline
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
BG-8 BG-9 DS-1 DS-2 DS-3 DS-4 DS-5 Equipment
Blank
3/24/2014 3/24/2014 3/25/2014 3/25/2014 3/25/2014 3/25/2014 3/25/2014 3/25/2014
3.58 8.59 3.56 3.01 5.12 2.50 3.49 <5.40 0.61 69
32.5 45.4 21.4 20.3 32.0 17.1 27.2 <1.40 Cr+60.29/Cr+324,000 Cr+65.6/Cr+310,0000
24.8 22.9 22.2 18.3 19.7 43.5 21.5 <1.60 620 8,200
211 475 238 175 585 75.6 104 2.05J 360 4,000
10.2 13.2 7.80 6.76 10.6 5.68 8.66 <1.80 300 4,000
----------------
----------------
----------------
----------------
----------------
----------------
----------------
----------------
----------------
Residential Health
PSRG
Industrial Health
PSRG
TABLE 6
Sediment Grain Size Analysis
IHSB Crompton & Knowles NCD044444735
Lowell, Gaston County, North Carolina
S&ME Project No. 1054-14-2084
Sample ID Silt Clay Colloids Gravel Total Sand Silt & Clay
SS-1 15.8%10.5%6.6%50.3%23.4%26.3%
SS-2 25.5%8.0%4.4%31.4%35.1%33.5%
SS-3 21.9%7.5%4.5%0.0%70.6%29.4%
SS-4 42.0%25.2%16.8%0.0%32.8%67.2%
SS-5 59.0%29.5%18.8%0.0%11.5%88.5%
SS-6 14.7%2.5%2.0%0.0%82.8%17.2%
SS-7 41.4%16.0%8.6%1.6%41.0%57.4%
SS-8 34.6%13.0%8.0%0.0%52.4%47.6%
SS-9 17.2%5.2%2.6%10.5%67.1%22.4%
SS-10 50.3%16.0%8.9%0.0%33.7%66.3%
SS-11 28.9%10.3%6.0%0.0%60.8%39.2%
SS-12 24.7%9.8%5.0%0.1%65.4%34.5%
SS-13 44.6%23.0%14.9%0.0%32.4%67.6%
SS-14 43.2%20.2%12.8%0.0%36.6%63.4%
SS-15 32.3%21.2%14.7%0.0%46.5%53.5%
SS-16 55.1%17.5%9.8%0.0%27.4%72.6%
SS-17 43.0%26.3%18.9%0.0%30.7%69.3%
SS-18 51.9%35.6%20.9%0.0%12.5%87.5%
SS-19 53.0%23.8%14.9%0.0%23.2%76.8%
SS-20 57.4%32.5%17.0%0.0%10.1%89.9%
SS-21 55.6%18.5%9.9%0.0%25.9%74.1%
SS-22 47.4%27.5%16.6%0.7%24.4%74.9%
SS-23 54.1%19.8%10.9%0.0%26.1%73.9%
SS-24 54.5%24.5%13.8%0.0%21.0%79.0%
SS-25 49.4%17.0%8.9%0.0%33.6%66.4%
SS-26 30.5%18.0%11.0%0.0%51.5%48.5%
SS-27 51.7%23.0%14.9%0.0%25.3%74.7%
SS-28 18.5%10.0%6.2%0.5%71.0%28.5%
SS-29 53.6%32.5%20.9%0.0%13.9%86.1%
B-1 21.1%2.5%0.5%33.7%42.7%23.6%
B-2 47.3%30.0%18.8%0.0%22.7%77.3%
B-3 26.1%14.2%8.0%0.2%59.5%40.3%
B-4 19.1%9.0%6.9%20.0%51.9%28.1%
B-5 39.9%17.5%9.9%0.0%42.6%57.4%
B-6 25.8%7.8%5.5%25.3%41.1%33.6%
B-7 50.4%27.5%16.9%0.0%22.1%77.9%
B-8 15.3%7.2%4.4%50.5%27.0%22.5%
B-9 44.7%24.0%14.8%0.0%31.3%68.7%
DS-1 47.2%11.8%7.0%0.0%41.0%59.0%
DS-2 59.0%17.5%8.9%0.4%23.1%76.5%
DS-3 51.0%18.2%9.0%0.0%30.8%69.2%
DS-4 30.0%12.5%8.4%0.2%57.3%42.5%
DS-5 35.5%17.0%10.9%0.0%47.5%52.5%
DATE:
DRAWN BY:
3201 SPRING FOREST RD, RALEIGH, NC 27616
NC ENGINEER LICENSE #F-0176
SCALE:
PROJECT NO:
FIGURE NO.
WWW.SMEINC.COM IHSB CROMPTON KNOWLES SITE
GASTONIA, NORTH CAROLINA
1" = 200'
BTR
APRIL 2014
1054-14-2084
1
A-4302
VICINITY MAP
( IN FEET )
GRAPHIC SCALE
01000 20001000500
S:\PROJECTS\2_IHSB Orphan Priority Sites 2010\!IHSB Contract Projects\1054-14-2084 IHSB Crompton Knowles Site\CAD\A4302.dwg, FIG1, 4/27/2014 2:27:53 PM, 1:1
PROJECT NUMBER:
DATE:FIGURE NO.SCALE:
DRAWN BY:
CHECKED BY:DRAWING NUMBER:
WWW.SMEINC.COM
3201 SPRING FOREST RD, RALEIGH, NC 27616
NC ENGINEER LICENSE #F-01762 BTR1054-14-2084
APRIL 20141" = 200'
IHSB CROMPTON KNOWLES SITE
GASTONIA, NORTH CAROLINA
SITE MAP
B-2326
S:\PROJECTS\2_IHSB Orphan Priority Sites 2010\!IHSB Contract Projects\1054-14-2084 IHSB Crompton Knowles Site\CAD\B2326.dwg, FIG2, 4/27/2014 2:01:24 PM, 1:1
PROJECT NUMBER:
DATE:FIGURE NO.SCALE:
DRAWN BY:
CHECKED BY:DRAWING NUMBER:
WWW.SMEINC.COM
3201 SPRING FOREST RD, RALEIGH, NC 27616
NC ENGINEER LICENSE #F-01763 BTR1054-14-2084
APRIL 20141" = 200'
IHSB CROMPTON KNOWLES SITE
GASTONIA, NORTH CAROLINA
MONITOR WELL SAMPLING RESULTS MAP
B-2327
S:\PROJECTS\2_IHSB Orphan Priority Sites 2010\!IHSB Contract Projects\1054-14-2084 IHSB Crompton Knowles Site\CAD\B2327.dwg, FIG3, 4/27/2014 2:06:07 PM, 1:1
PROJECT NUMBER:
DATE:FIGURE NO.SCALE:
DRAWN BY:
CHECKED BY:DRAWING NUMBER:
WWW.SMEINC.COM
3201 SPRING FOREST RD, RALEIGH, NC 27616
NC ENGINEER LICENSE #F-01764 BTR1054-14-2084
APRIL 20141" = 200'
IHSB CROMPTON KNOWLES SITE
GASTONIA, NORTH CAROLINA
SEDIMENT SAMPLING RESULTS MAP
B-2328
S:\PROJECTS\2_IHSB Orphan Priority Sites 2010\!IHSB Contract Projects\1054-14-2084 IHSB Crompton Knowles Site\CAD\B2328.dwg, FIG4, 4/27/2014 2:14:05 PM, 1:1
S S
-1
S S
-2
S S
-3
S S
-4
S S
-5
S S
-6
S S
-7
S S
-8
S S
-9
S S
-
10
S S
-
11
S S
-
12
S S
-
13
S S
-
14
S S
-
15
S S
-
16
S S
-
17
S S
-
18
S S
-
19
S S
-
20
S S
-
21
S S
-
22
S S
-
23
S S
-
24
S S
-
25
S S
-
26
S S
-
27
S S
-
28
S S
-
29
B-
1
B-
2
B-
3
B-
4
B-
5
B-
6
B-
7
B-
8
B-
9
DS
-1
DS
-2
DS
-3
DS
-4
DS
-5
S ilt& Clay(% P assing#200):26.33.29.67.88.17.57.47.22.66.39.34.67.63.53.72.69.87.76.89.74.74.73.79.66.48.74.28.86.23.77.40.28.57.33.77.22.68.59.76.69.42.52.
T otalS and:23.35.70.32.11.82.41.52.67.33.60.65.32.36.46.27.30.12.23.10.25.24.26.21.33.51.25.71.13.42.22.59.51.42.41.22.27.31.41.23.30.57.47.
Gravel:50.31.0.00.00.00.01.60.010.0.00.00.10.00.00.00.00.00.00.00.00.00.70.00.00.00.00.00.50.033.0.00.220.0.025.0.050.0.00.00.40.00.20.0
0.0%
10.0%
20.0%
30.0%
40.0%
50.0%
60.0%
70.0%
80.0%
90.0%
100.0%PercentageGrainS izeS ummary