Terry Creek Ecological Screening Evaluation
Brunswick, Georgia
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U. S. Environmental Protection Agency
Science and Ecosystem Support Division
Ecological Assessment Branch
Athens, Georgia
July 1997
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Terry Creek Ecological Screening Evaluation
Brunswick, Georgia
1.0 INTRODUCTION
An ecological screening evaluation of Terry Creek and nearby streams was initiated by the
United States Environmental Protection Agency (USEPA), Region 4, Science and Ecosystem
Support Division on February 18, 1997. This action was in response to a request for assistance
by the USEPA Emergency Response Team. The purpose of this study was to evaluate the
potential for impacts to human health and the environment from contaminants in Terry Creek.
Terry Creek is used as a fishing and blue crab collection site by the general public. Concerns
have been raised about dangers to consumer health from possible contaminants in biological
organisms collected from this area. The primary contaminant of concern was toxaphene.
Sample collection activities were a joint venture involving the Georgia Department of Natural
Resources (GDNR) and the USEPA.
2.0 SITE DESCRIPTION
2.1 Study Area
The study area is located in the Atlantic coastal region of the southeastern United States, east of
the city of Brunswick in Glynn County, Georgia (Figure 1). The habitats selected for evaluation
were tidally influenced streams flowing through emergent herbaceous wetlands. Marsh
vegetation was primarily smooth cordgrass (Spartina alterniflora) and needle rush (Juncus
roemerianus).
2.2 Station Locations
A reconnaissance of the area was conducted February 18, 1997 to ensure access and suitability of
stations for sample collection. Based on the field reconnaissance, the following five stations
were selected for collection of surface water, sediment, and blue crab (Callinectes sapidus)
samples (Figure'2):
001 Terry and Dupree Creeks
002 Mouth of Terry Creek
003 Mouth of Back River
004 Back Landing
005 Jove Creek (control station)
Four additional stations (1 A, IB, 1C, ID) were selected for sediment sampling in small tidal
streams draining the two dredge spoil sites located adjacent to Dupree and Terry Creeks (Figure
2). Nine stations were selected for collection of forage fish in and near Dupree and Terry Creeks
(Figure 3). Consumer fish were collected from four zones as shown by the shaded areas labeled
Zone A through Zone D (Figure 4). Zone A included Back Landing north of Clubbs Creek, Zone
B included the upstream segment of Terry Creek, Zone C included the downstream reach of
Tern Creek east of its confluence with Dupree Creek, and Zone D included Dupree Creek and a
small part of Terry Creek.
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3.0 METHODS
3.1 Field Sampling Methods
3.1.1 Sediment and Surface Water Samples
Sediment and surface water samples were collected near the margin of tidal channels during a
low tide. Surface water was collected as subsurface grab samples. Sediment samples were
collected from the top 15 cm of sediment in depositional areas on the inside bend of a tidal
channel.
Pre-cleaned bottles, glass pans, and stainless steel scoops were used to collect sediment and
surface water samples at each station. Bottles and plastic bags were labeled immediately prior to
sampling. Clean gloves were used at each station. Sample collection information was recorded
in a bound field notebook. Samples were placed in coolers on ice immediately after collection.
Sample collection activities followed guidelines described in USEPA Environmental Compliance
Branch Standard Operating Procedures (USEPA 1991).
3.1.2 Biological Samples
Baited crab pots were deployed during the reconnaissance and remained in place for four
complete tidal cycles. Upon retrieval, blue crabs were removed from the crab pots, placed in
plastic bags and immediately packed on ice.
Forage and consumer fish sampling activities were conducted over a period of several weeks
from February 18 to March 19, 1997, due to delays caused by availability of biological
organisms and appropriate daily tidal cycles. Mummichogs (Fundulus heteroclitus) were
selected as the main forage fish species. Mummichogs were collected using non-baited minnow
traps placed in small tidal streams. Traps were placed in the streams during a high tide and
retrieved during the falling tide. The traps functioned as a block net. Mummichogs were
funneled into the traps as they moved from the marsh during the falling tide. Upon retrieval,
mummichogs were removed from the traps, placed in plastic bags, and packed on ice.
Efforts to collect consumer fish were conducted at various times during the tidal cycles.
Consumer fish were collected using a variety of collection techniques (otter trawls, trammel nets,
and hook and line). The most successful methods were trammel nets and hook and line.
Immediately after collection, consumer fish samples were packed on ice. These fish were fileted
within 48 hours, and the filets were then frozen, since only the edible portion was to be used for
chemical analysis. Based on collection results, spotted sea trout (Cynoscion nebulosus) was
selected as the target species (USEPA 1995) for chemical analysis.
On two separate occasions, attempts were made to collect clapper rails (Rallus longirostris).
However, no clapper rails were sited at or near the study area.
Field handling and processing of biological samples were conducted following guidelines
suggested in Fish Field and Laboratory Methods for Evaluating the Biological Integrity of
Surlace Waters (Klemm et al. 1993).
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3.2 Laboratory Methods
3.2.1 Tissue Preparation
To prevent loss of fluids, tissue samples were kept frozen during processing. Tissue samples
were removed from the freezer, chopped into manageable pieces, and ground in a pre-chilled
Waring blender with dry ice. Tissue then was transferred from the blender to a chilled glass jar,
and immediately returned to the freezer. Tissue preparation followed basic guidelines suggested
in Fish Field and Laboratory Methods for Evaluating the Biological Integrity of Surface Waters
(Klemm et al. 1993).
3.2.2 Chemical Analysis
Surface water and sediment samples were analyzed for volatile organics, extractable organics,
pesticides, PCB's, and metals. In addition, two sediment samples were scanned for dioxin.
Tissue samples were analyzed for extractable organics, pesticides, PCB's, and metals. Chemical
analyses were performed by USEPA Analytical Support Branch Laboratories in Athens, Georgia.
The laboratory practices, sample handling, quality control, and analytical methods that were used
are described in the Laboratory Operations and Quality Control Manual (USEPA 1990) and
Methods for Chemical Analysis of Water and Wastes (USEPA 1983).
4.0 RESULTS AND DISCUSSION
4.1 Surface Water Data
Results of surface water analyses are presented in Appendix A. Carbon tetrachloride was
detected in surface water at 0.69 ug/L and 0.75 ug/L at Station 001 and its duplicate Station 101,
respectively. Carbon tetrachloride is a colorless, nonflammable liquid used as a solvent, grain
fumigant, refrigerant, and as a starting material for the manufacture of organic compounds. It
was formerly used as a dry-cleaning agent and as a component of fire extinguisher solutions.
References suggest that this compound may be a carcinogen (Merck 1989; USEPA 1980).
Levels detected at Station 001 are well below the USEPA Region 4 Waste Management Division
(WMD) freshwater screening levels of 3520 ug/L for acute toxicity and 352 ug/L for chronic
effects (USEPA 1980).
Toxaphene, although listed as a primary contaminant of concern, was not detected in surface
water samples collected during this study. The acute screening criteria (USEPA 1995) for
toxaphene is 0.21 ug/L for saltwater. The minimum quantitation limit for toxaphene reported by
USEPA Region 4 Analytical Support Branch was 5.0 ug/L. Analyses for other organic
compounds and metals did not reveal any major contaminants in the surface water samples.
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4.2 Sediment Data
Results of sediment sample analyses are presented in Appendix B. Additionally, results of
sediment analysis for toxaphene are shown in Table 1. Toxaphene was present in four of the
sediment sampling stations located in Terry and Dupree Creeks (001, 1A, 1C, and ID) but was
not detected at the remaining stations IB and 002-005. Toxaphene concentrations in Dupree and
Terry Creek sediment samples ranged from 7900J ug/kg to 230,000J ug/kg with the highest value
occurring at Station 1A in Dupree Creek. Because of the complex sample matrix, the values for
toxaphene could only be estimated as indicated by the "J" qualifier. Toxaphene is a complex
mixture of chlorinated camphenes. It has been used widely as an insecticide on cotton, livestock,
grains, vegetables, soybeans, and forage. Toxaphene is persistent in soil with a half-life of about
10 years. Toxaphene is especially hazardous to aquatic organisms which readily accumulate
toxaphene from the ambient environment and biomagnify the chemical through food chains.
References suggest this compound may be a carcinogen (USFWS 1985).
Table 1. Results of toxaphene analysis of sediment samples.
Sediment Sampling Stations
Analyte
Units
001
101
1A
IB
1C
ID
002
003
004
005
Toxaphene
ug/kg
9100J
81003
230000J
3800JN
7900J
18000J
1500JN
390U
830U
710U
U - The analyte was not present in concentrations above detection limits. The value preceding the "U" is the
"minimum quantitation limit".
J - The analyte was identified in the sample, but the quantitative value is an estimate. The value preceding the "J"
is the "estimated value".
JN - There is some reasonable indication that organic constituents similar to some of those found in
toxaphene are present in the sample, but there is not enough proof to positively identify the compound as
toxaphene.
Carbon disulfide was detected at Stations 001-005 at levels ranging from 7.5 ug/L to 33 ug/L.
Carbon disulfide is clear, colorless or faintly yellow liquid, usually with a strong disagreeable
odor. Carbon disulfide may be released to the environment from natural or artificial sources. It
can be found in emissions and wastewater and is used in the manufacture of viscose rayon,
cellophane, carbon tetrachloride, and as a solvent and fumigant. It also may be formed and
released during treatment of sewage and from landfills containing municipal refuse and
wastewater sludges. Carbon disulfide also has been used for insect control in stored grain and
for soil fumigation to control soil fungi and deep-rooted perennial weeds. If released into water,
carbon disulfide will be lost primarily due to volatilization. Carbon disulfide also may occur in
the environment as a natural product of anaerobic biodegradation and it is released to the
atmosphere from oceans and land masses. Current data suggests that coastal areas and other
areas of high biological productivity have greater fluxes of carbon disulfide than the open ocean.
Carbon disulfide would not be expected to bioconcentrate significantly in aquatic organisms.
The USHPA presently has no established screening value in place for acceptable levels of carbon
disulfide in sediments.
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Results of dioxin analyses on sediment samples from the background Station 005 and from
Station 001 located in Dupree/Terry Creek are shown in Appendix B. Some dioxin compounds
were detected at both stations. However, values at Station 001 did not exceed those found at the
background Station 005. Metals analysis of sediment samples did not reveal any significant
contamination.
4.3 Biological organisms
Results of blue crab tissue analyses (Appendix C) revealed no substantial signs of organic or
metals contamination.
Results of forage fish tissue analysis are presented in Appendix D. Forage fish were collected at
seven of the nine stations sampled. Constituents which fell within the toxaphene retention time
window were detected and calculated against a toxaphene standard. These constituents were
present in all forage fish samples at values ranging from 1.9 JN mg/kg to 27 JN mg/kg (Table 2),
with the highest concentrations occurring at Station 4 (Hercules effluent channel). However,
neither the amount nor the identification of this constituent could be confirmed as indicated by
the "JN" qualifier. Toxaphene is a complex mixture of compounds. When released to the
environment, toxaphene constituents degrade so that the material is no longer identifiable as
toxaphene, but may appear as toxaphene constituents in the sample. However, a number of other
compounds from natural and anthropogenic sources may also resemble toxaphene constituents.
"JN" indicates there is some reasonable indication of the presence of organic constituents similar
to some of those found in toxaphene, but there is not enough proof to positively identify this
compound as toxaphene in environmental samples. Therefore, the "JN" qualifier on this data
indicates these values should be interpreted with caution.
Table 2. Results of toxaphene analysis of forage fish tissue samples.
Forage Fish Sampling Stations
Analyte
Units
02
03
03
04
04
05
05
05
07
08
09
Toxaphene
mg/kg
4.8JN
5 1 JN
6.6JN
27JN
14JN
5.6JN
5.3JN
2.3JN
1.9JN
2.7JN
2.3JN
Constituents similar to some of those found in toxaphene were also found in consumer fish
(edible fish) at all four zones sampled. Concentrations of this material ranged from 1.6JN mg/kg
at Zone A to 3.9JN mg/kg at Zone D (Appendix E; Table 3).
Table 3. Results of toxaphene analysis of consumer fish samples.
Consumer Fish Sampling Stations
Analyte
Units
Zone A
Back
Landing
Zone B
Terry Cr.
Upstream
Zone C
Terry Cr.
Downstream
Zone D
Dupree/
Terry Cr.
Toxaphene
mg/kg
1.6JN
1.7JN
2.6JN
3.9JN
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No substantial metals contamination was detected in biological organisms collected during this
study.
5.0 SUMMARY
Results of chemical analyses of surface water samples were similar for all five stations with the
exception of low levels of carbon tetrachloride detected at Station 001. Toxaphene was not
detected in surface water samples collected during this study.
Toxaphene was present at four sediment sampling stations (001, 1A, 1C, and ID) in Terry and
Dupree Creeks, but was not detected at the remaining stations (IB and 002-005). Toxaphene
concentrations at the Terry and Dupree Creek stations were one to three orders of magnitude
higher than the minimum detection level at the background station. No screening criterion has
been established by USEPA Region 4 for toxaphene concentrations in sediment.
There was some indication that organic constituents similar to those found in toxaphene were
present in all forage fish samples collected from Dupree and Terry Creeks. These constituents
were two to three times higher at Station 4 (Hercules effluent) than at the remaining stations.
Consumer fish filets also revealed some indication of the presence of these constituents.
Toxaphene is especially hazardous to aquatic organisms which readily accumulate this
compound from the ambient environment and biomagnify the chemical through food chains.
Levels of confirmed toxaphene have been detected in the sediment and may pose a risk of
migration.
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6.0 REFERENCES
Klemm, Donald J., Q. J. Stober, and J. M. Lazorchak. 1993. Fish Field and Laboratory Methods
for Evaluating the Biological Integrity of Surface Waters. United States Environmental
Protection Agency, Environmental Monitoring Systems Laboratory, Office of Research and
Development. Cincinnati, OH. 348 pp. EPA/600/R-92/111.
Merck. 1989. The Merck Index, Eleventh Edition.
USEPA. 1995. Guidance for Assessing Chemical Contamination Data for Use in Fish
Advisories, Volume 1: Fish Sampling and Analysis. U.S. Environmental Protection Agency,
Office of Science and Technology, Office of Water. Washington, DC. EPA 823-R-95-007.
USEPA. 1991. Environmental Compliance Branch Standard Operating Procedures and Quality
Assurance Manual. U.S. Environmental Protection Agency, Region IV. Environmental Services
Division. Athens, GA.
USEPA. 1990. Laboratory Operations and Quality Control Manual. United States
Environmental Protection Agency, Region IV. Athens, GA.
USEPA. 1983. Methods for Chemical Analysis of Water and Wastes. United States
Environmental Protection Agency. Environmental Monitoring and Support Laboratory, Office
of Research and Development. Cincinnati, OH. EPA-600/4-79-020.
USEPA. 1980. Ambient Water Quality Criteria for Carbon Tetrachloride. United States
Environmental Protection Agency. Office of Water Regulations and Standards, Criteria and
Standards Division. Washington, DC.
USFWS. 1985. Toxaphene Hazards to Fish, Wildlife, and invertebrates: a Synoptic Review.
United States Department of the Interior, Fish and Wildlife Service. Washington, DC.
Biological Report 85(1.4).
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FIGURE 1
TERRY CREEK STUDY AREA
BRUNSWICK. GA
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FIGURE 2
SAMPLING STATIONS
TERRY CREEK PROJECT
BRUNSWICK, GA
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A Surface Water, Sediment & Blue
Crab Sampling Stations
0 Sediment Only Sampling Stations
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FIGURE 3
FORAGE FISH SAMPLING STATIONS
TERRY CREEK PROJECT
BRUNSWICK, GA
ferry Creek
6
W
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FIGURE 4
CONSUMER FISH SAMPLING STATIONS
TERRY CREEK PROJECT
BRUNSWICK, GA
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APPENDICES
Terry Creek Ecological Screening Evaluation
Brunswick, Georgia
1997 Chemical Data
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List of Appendices
Appendix A.
A-l.
A-2.
A-3.
A-4.
Appendix B.
B-l.
B-2.
B-3.
B-4.
B-5.
Appendix C.
C-l.
C-2.
C-3.
Appendix D.
D-l.
D-2.
D-3.
Appendix E.
E-l.
E-2.
E-3.
Surface Water Data
Volatile Organic Compounds
Extractable Organic Compounds
Pesticides/PCB's
Metals
Sediment Data
Volatile Organic Compounds
Extractable Organic Compounds
Pesticides/PCB's
Metals
Dioxin Scan
Blue Crab Tissue Data
Extractable Organic Compounds
Pesticides/PCB's
Metals
Forage Fish Tissue Data
Extractable Organic Compounds
Pesticides/PCB's
Metals
Consumer Fish Tissue Data
Extractable Organic Compounds
Pesticides/PCB's
Metals
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Volatile Organic Compounds in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
101
005
002
003
004
Blank
TRICHLOROFLUOROMETHANE
UG/L
1
U
1
U
1
U
1
U
1 u
1
U
1 u
CHLOROMETHANE
UG/L
1
U
1
U
1
U
1
U
1 u
1
U
1 u
BROMOMETHANE
UG/L
1
u
1
u
1
u
1
u
1 u
1
U
1 u
VINYL CHLORIDE
UG/L
1
u
1
u
1
u
1
u
1 u
1
U
1 u
CHLOROETHANE
UG/L
1
u
1
u
1
u
1
u
1 u
1
U
1 u
METHYLENE CHLORIDE
UG/L
5
u
5
u
5
u
5
u
5 u
5
U
5 U
1,1-DICHLOROETHENE (1,1-DICHLOROETHYLENE)
UG/L
1
u
1
u
1
u
1
u
1 u
1
U
1 U
ACETONE
UG/L
25
u
25
u
25
u
25
u
25 U
25
U
25 U
CARBON DISULFIDE
UG/L
25
u
2 5
u
2.5
u
2.5
u
2 5 U
2 5
U
2 5 U
1,1 -DICHLOROETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
CIS-1,2-DICHLOROETHENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
2,2-DICHLOROPROPANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
METHYL ETHYL KETONE
UG/L
25
u
25
u
25
u
25
u
25 U
25
U
25 U
BROMOCHLOROMETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
TRANS-1,2-DICHLOROETHENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
CHLOROFORM
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
1,2-DICHlOROETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
1.1.1 -TRICHLOROETH ANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
1,1 -DICHLOROPROPENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
U
1 U
CARBON TETRACHLORIDE
UG/L
0 69
AJ
0 75
AJ
1
u
1
u
1 U
1
U
1 U
BROMODICHLOROMETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
METHYL ISOBUTYL KETONE
UG/L
2.5
u
25
u
2.5
u
2.5
u
2 5 U
25
u
2.5 U
1,2-DICHLOROPROPANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
DIBROMOMETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
TRANS-1,3-DICHLOROPROPENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
TRICHLOROETHENE (TRICHLOROETHYLENE)
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
BENZENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
DIBROMOCHLOROMETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
1.1,2-TRICHLOROETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
CIS-1.3-DICHLOROPROPENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
BROMOFORM
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
BROMOBENZENE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
1,1,2,2-TETRACHLOROETHANE
UG/L
1
u
1
u
1
u
1
u
1 U
1
u
1 U
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A-1 (cont). Volatile Organic Compounds in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
101
005
002
003
004
Blank
TETRACHLOROETHENE (TETRACHLOROETHYLEN
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
1,3-DICHLOROPROPANE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
METHYL BUTYL KETONE
UG/L
2 5 U
2 5
u
2.5 U
2 5
u
2 5
u
25
u
2 5 U
TOLUENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
CHLOROBENZENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,1,1,2-TETRACHLOROETHANE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
ETHYL BENZENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
(M- AND/OR P-)XYLENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
O-XYLENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
STYRENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,2,3-TRICHLOROPROPANE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
O-CHIOROTOLUENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
P-CHLOROTOLUENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,3-DICHLOROBENZENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,4-DICHLOROBENZENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,2-DICHLOROBENZENE
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
1,2-DIBROMOETHANE (EDB)
UG/L
1 U
1
u
1 u
1
u
1
u
1
u
1 U
ISOPROPRYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
N-PROPYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
1,3.5-TRIMETHYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
TERT-BUTYLBENZENE
UG/L
1 u
1
u
1 u
1
u
u
1
u
1 u
1,2,4-TRIMETHYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
SEC-BUTYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
P-ISOPROPYLTOLUENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
N-BUTYLBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
1.2-DJBROMO-3-CHLOROPROPANE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
1,2,4-TRICHLOROBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
HEXACHLORO-1.3-BUTADIENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
1,2,3-TRICHLOROBENZENE
UG/L
1 u
1
u
1 u
1
u
1
u
1
u
1 u
g x^puaddv
0 xjpuaddw
r TCTorttcVfT
-------
A-2. Extractable Organic Compounds in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
101
002
003
004
005
BIS(2-CHLOROETHYL) ETHER
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
HEXACHLOROETHANE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
BIS(2-CHLOROISOPROPYL) ETHER
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
N-NITROSODI-N-PROPYLAMINE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
NITROBENZENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
HEXACHLOROBUTADIENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
2-METHYLNAPHTHALENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
1 ,2.4-TRICHLOROBENZENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
NAPHTHALENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
4-CHLOROANILINE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
BIS(2-CHLOROETHOXY)METHANE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
ISOPHORONE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
HEXACHLOROCYCLOPENTADIENE (HCCP)
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
2-CHLORONAPHTHALENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
2-NITROANILINE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
ACENAPHTHYLENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
ACENAPHTHENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
DIMETHYL PHTHALATE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
DIBENZOFURAN
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
2.4-DINITROTOLUENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
2,6-DINITROTOLUENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
3-NITROANILINE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
4-CHLOROPHENYL PHENYL ETHER
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
4-NITROANILINE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
FLUORENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
DIETHYL PHTHALATE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
N-NITROSODIPHENYLAMINE/DIPHENYLAMIN
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
HEXACHLOROBENZENE (HCB)
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
4-BROMOPHENYL PHENYL ETHER
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
PHENANTHRENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
ANTHRACENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
DI-N-BUTYLPHTHALATE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
FLUORANTHENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
PYRENE
UG/L
10
u
10
u
10
u
10
u
10
u
10
u
g x^puaddy
3 xfpuaddv
q xTpuaddy
T VTnnaH^'
-------
A-2 (cont). Extractable Organic Compounds in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
101
002
003
004
005
BENZYL BUTYL PHTHALATE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
BIS(2-ETHYLHEXYL) PHTHALATE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
BENZO(A)ANTHRACENE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
CHRYSENE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
3,3'-DICHLOROBENZIDINE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
DI-N-OCTYLPHTHALATE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
BENZO(B AND/OR K)FLUORANTHENE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
BENZO-A-PYRENE
UG/L
10
U
10
u
10
u
10
u
10
u
10 u
INDENO (1,2,3-CD) PYRENE
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
DIBENZO(A,H)ANTHRACENE
UG/L .
10
u
10
u
10
u
10
u
10
u
10 u
BENZO(GH!)PERYLENE
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2-CHLOROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2-METHYLPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
(3-AND/OR 4-)METHYLPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2-NITROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
PHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2,4-DIMETHYLPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2,4-DICHLOROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2,4,6-TRICHLOROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2,4,5-TRICHLOROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
4-CHLORO-3-METHYLPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
2,4-DINJTROPHENOL
UG/L
20
u
20
u
20
u
20
u
20
u
20 U
2-METHYL-4.6-DINITROPHENOL
UG/L
20
u
20
u
20
u
20
u
20
u
20 U
PENTACHLOROPHENOL
UG/L
20
u
20
u
20
u
20
u
20
u
20 U
4-NITROPHENOL
UG/L
20
u
20
u
20
u
20
u
20
u
20 U
2,3,4,6-TETRACHLOROPHENOL
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
CARBAZOLE
UG/L
10
u
10
u
10
u
10
u
10
u
10 u
g xjpuaddy
-------
A-3. Pesticides/PCB's in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte Units 001 101 002 003 004 005
ALDRIN
UG/L
0 1
U
0 1
u
0.1
U
0 1
U
0.1
u
0.1
U
HEPTACHLOR
UG/L
0 1
U
0 1
U
0 1
U
0 1
U
0.1
U
0 1
U
HEPTACHLOR EPOXIDE
UG/L
0 1
U
0 1
U
0 1
U
0 1
U
0.1
U
0.1
U
ALPHA-BHC
UG/L
0 1
U
0 1
U
0 1
U
0 1
U
0.1
U
0 1
U
BETA-BHC
UG/L
0 1
U
0 1
u
0 1
U
0 1
U
0.1
U
0 1
U
GAMMA-BHC (LINDANE)
UG/L
0 1
U
0 1
u
0 1
U
0 1
U
0.1
U
0 1
U
DELTA-BHC
UG/L
0 1
U
0 1
u
0 1
U
0 1
U
0.1
U
0 1
U
ENDOSULFAN 1 (ALPHA)
UG/L
0 1
U
0 1
u
0.1
U
0.1
U
0.1
U
0.1
U
DIELDRIN
UG/L
0 1
U
0 1
u
0.1
U
0 1
U
0 1
U
0.1
U
4,4 -DDT (P.P'-DDT)
UG/L
0 1
U
0 1
u
0 1
U
0 1
U
0 1
U
0 1
U
4,4-DDE (P.P'-DDE)
UG/L
0.1
U
0 1
u
0 1
U
0.1
U
0 1
U
0 1
U
4,4'-DDD (P,P'-DDD)
UG/L
0 1
U
0 1
u
0.1
U
0 1
U
0.1
U
0.1
U
ENDRIN
UG/L
0.1
U
0 1
u
0.1
U
0.1
U
0.1
U
0.1
U
ENDOSULFAN II (BETA)
UG/L
0.1
U
0 1
u
0 1
U
0 1
U
0.1
U
0.1
U
ENDOSULFAN SULFATE
UG/L
0 1
U
0 1
u
0 1
U
0 1
U
0.1
u
0.1
U
CHLORDANE (TECH. MIXTURE)
/ UG/L
0 25
U
0.25
u
0.25
U
0.25
U
0 25
u
0 25
U
PCB-1242 (AROCLOR 1242)
UG/L
0.5
u
05
u
0 5
U
0.5
U
0.5
u
0.5
U
PCB-1254 (AROCLOR 1254)
UG/L
0 5
u
05
u
05
U
05
U
0.5
u
0.5
U
PCB-1221 (AROCLOR 1221)
UG/L
05
u
05
u
05
u
0 5
U
0.5
u
0.5
U
PCB-1232 (AROCLOR 1232)
UG/L
0.5
u
0 5
u
0.5
u
05
u
0.5
u
0.5
u
PCB-1248 (AROCLOR 1248)
UG/L
0.5
u
0.5
u
0.5
u
0.5
u
0.5
u
0.5
u
PCB-1260 (AROCLOR 1260)
UG/L
05
u
0.5
u
05
u
0.5
u
0.5
u
0.5
u
PCB-1016 (AROCLOR 1016)
UG/L
0 5
u
0.5
u
0.5
u
0.5
u
0.5
u
05
u
TOXAPHENE
UG/L
5
u
5
u
5
u
5
u
5
u
5
u
METHOXYCHLOR
UG/L
0 25
u
0.25
u
025
u
0.25
u
025
u
0.25
u
ENDRIN KETONE
UG/L
0 1
u
0 1
u
0.1
u
0.1
u
0.1
u
0.1
u
-------
A-4. Metals in Surface Water.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte Units 001 101 002 003 004 005 Blank
SILVER
UG/L
40
U
40
U
40
U
40
u
40
U
40
U
40
u
ARSENIC
UG/L
120
U
120
U
120
U
120
U
120
U
120
U
120
U
BARIUM
UG/L
40
U
40
U
40
U
40
U
40
U
40
U
40
U
BERYLLIUM
UG/L
20
U
20
U
20
U
20
U
20
U
20
U
20
U
CADMIUM
UG/L
20
U
20
U
20
U
20
U
20
U
20
U
20
U
COBALT
UG/L
40
U
40
U
40
U
40
U
40
U
40
U
40
U
CHROMIUM
UG/L
40
U
40
U
40
U
40
U
40
U
40
U
40
U
COPPER
UG/L
40
U
40
U
40
U
40
U
40
U
40
U
40
U
MOLYBDENUM
UG/L
40
U
40
U
40
U
40
U
40
U
40
U
40
U
NICKEL
UG/L
80
U
80
U
80
U
80
U
80
U
80
U
80
U
LEAD
UG/L
160
U
160
U
160
u
160
U
160
U
160
U
160
U
ANTIMONY
UG/L
120
U
120
U
120
u
120
U
120
U
120
U
120
U
SELENIUM
UG/L
160
U
160
U
160
u
160
U
160
U
160
U
160
U
TIN
UG/L
100
u
100
U
100
u
100
U
100
U
100
U
100
U
STRONTIUM
UG/L
2900
3200
2800
3300
3200
1700
40
U
TELLURIUM
UG/L
200
u
200
U
200
u
200
U
200
U
200
U
200
U
TITANIUM
UG/L
40
u
40
U
40
u
40
U
40
U
40
u
40
U
THALLIUM
UG/L
400
u
400
U
400
u
400
U
400
U
400
u
400
U
VANADIUM
UG/L
40
u
40
U
40
u
40
U
40
U
40
u
40
U
YTTRIUM
UG/L
40
u
40
U
40
u
40
U
40
U
40
u
40
U
ZINC
UG/L
40
u
40
U
40
u
40
U
40
U
40
u
40
U
TOTAL MERCURY UG/L
02
u
02
U
02
u
0.2
U
0.2
U
0.2
u
02
u
ALUMINUM
UG/L
940
790
U
870
870
730
660
400
u
MANGANESE
UG/L
140
140
54
46
130
60
40
u
CALCIUM
MG/L
170
180
160
190
190
97
2
u
MAGNESIUM
MG/L
490
520
480
570
550
280
0.4
u
IRON
MG/L
0 49
048
0 44
0 53
0.43
0 55
02
u
SODIUM
MG/L
4100
4400
4000
4700
4600
2400
4
u
POTASSIUM
MG/L
170
170
170
190
180
96
8
u
-------
>
•o
ro
s
a
H*
X
w
-------
B-1. Volatile Organic Compounds in Sediment.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte Units 001 101 1A IB 1C 1D 002 003 004 005 BLANK
TRICHLOROFLUOROMETHANE
UG/KG
14
U
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1 9 u
CHLOROMETHANE
UG/KG
14
U
14
U
110
UJ
140
UJ
110
UJ
75
UJ
5 3
U
5 1
U
49
U
16
U
1.9 U
BROMOMETHANE
UG/KG
14
u
14
U
110
UJ
140
UJ
110
UJ
75
UJ
53
U
5.1
U
49
U
16
U
19 U
VINYL CHLORIDE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
CHLOROETHANE
UG/KG
14
u
14
U
110
UJ
140
UJ
110
UJ
75
UJ
5.3
U
5 1
U
49
U
16
U
1 9 U
METHYLENE CHLORIDE
UG/KG
240
u
280
U
110
UJ
140
UJ
110
UJ
75
UJ
110
U
110
U
250
U
280
U
32 U
1,1-DICHLOROETHENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5 1
U
49
U
16
U
1.9 U
ACETONE
UG/KG
140
u
140
U
440
J
280
UJ
210
UJ
150
UJ
53
U
51
U
490
U
160
U
19 U
CARBON DISULFIDE
UG/KG
19
29
21
J
22
J
21
UJ
10
J
7 5
14
33
J
20
19 U
1,1 -DICHLOROETHANE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5 1
U
49
U
16
U
1 9 U
CIS-1.2-DICHLOROETHENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
19 U
2,2-DICHLOROPROPANE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1 9 U
METHYL ETHYL KETONE
UG/KG
140
u
140
U
220
UJ
280
UJ
210
UJ
150
UJ
53
U
51
U
490
U
160
u
19 U
BROMOCHLOROMETHANE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5 1
U
49
U
16
u
1.9 U
TRANS-1.2-DICHLOROETHENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5 1
U
49
U
16
u
1.9 U
CHLOROFORM
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5 1
U
49
U
16
u
19 U
1,2-DICHLOROETHANE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
u
1 9 U
1,1,1 -TRICHLOROETH ANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
u
49
U
16
u
1.9 U
1,1 -DICHLOROPROPENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
1.9 U
CARBON TETRACHLORIDE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
1.9 U
BROMODICHLOROMETHANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
1.9 U
METHYL ISOBUTYL KETONE
UG/KG
34
u
36
u
55
UJ
70
UJ
53
UJ
37
UJ
13
U
13
u
120
U
39
u
4 3 J
1,2-DICHLOROPROPANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
19 U
DIBROMOMETHANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
1.9 U
TRANS-1,3-DICHLOROPROPENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
U
16
u
1.9 U
TRICHLOROETHENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
u
49
u
16
u
1.9 U
BENZENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
u
16
u
1.9 U
DIBROMOCHLOROMETHANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
u
16
u
1.9 U
1,1,2-TRICHLOROETHANE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
u
5.1
u
49
u
16
u
1.9 U
CIS-1,3-DICHLOROPROPENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
u
49
u
16
u
1.9 U
BROMOFORM
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
u
5.1
u
49
u
16
u
1.9 U
BROMOBENZENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
5.3
u
5.1
u
49
u
16
u
1.9 U
1.1,2,2-TETRACHLOROETHANE
UG/KG
14
u
14
u
110
UJ
140
UJ
110
UJ
75
UJ
53
u
5.1
u
49
u
16
u
1.9 U
TETRACHLOROETHENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
u
5.1
u
49
u
16
u
1.9 U
-------
B-1 (cont). Volatile Organic Compounds in Sediment.
Terry Creek, Brunswick, Georgia. 1997.
Analyte
Units
001
101
1A
1B
1C
Station
1D
002
003
004
005
BLANK
1,3-DICHLOROPROPANE
UG/KG
14
U
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
METHYL BUTYL KETONE
UG/KG
34
U
36
U
55
UJ
70
UJ
53
UJ
37
UJ
13
U
13
U
120
U
39
U
4 J
TOLUENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
19 U
CHLOROBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5.1
U
49
U
16
U
19 U
1,1,1,2-TETR ACHLOROETHANE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
19 U
ETHYL BENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
(M- AND/OR P-)XYLENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
O-XYLENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1.9 U
STYRENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5.1
U
49
U
16
U
1 9 U
1,2,3-TRICHLOROPROPANE
UG/KG
14
u
14
U
110
UJ
140
UJ
110
UJ
75
UJ
5 3
U
5 1
U
49
U
16
U
1.9 U
O-CHLOROTOLUENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5.1
U
49
U
16
U
1 9 U
P-CHLOROTOLUENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5.1
U
49
U
16
U
1 9 U
1,3-DICHLOROBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
1,4-DICHLOROBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5 1
U
49
U
16
U
1 9 U
1,2-DICHLOROBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1 9 U
1,2-DIBROMOETHANE (EDB)
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5 3
U
5 1
U
49
U
16
U
1 9 U
ISOPROPRYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
U
1 9 U
N-PROPYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5 1
U
49
U
16
U
19 U
1,3,5-TRIMETH YLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
U
19 U
TERT-BUTYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1 9 U
1,2,4-TRIMETHYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
U
19 U
SEC-BUTYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
u
1.9 U
P-ISOPROPYLTOLUENE
UG/KG
14
u
14
U
31
J
28
UJ
21
UJ
15
UJ
53
U
5.1
U
49
U
16
U
1 9 U
N-BUTYLBENZENE
UG/KG
14
u
14
U
22
UJ
28
UJ
21
UJ
15
UJ
5.3
U
5.1
U
49
U
16
u
19 U
1.2-DIBROMO-3-CHLOROPROPANE
UG/KG
14
u
14
u
110
UJ
140
UJ
110
UJ
75
UJ
5.3
U
5.1
U
49
u
16
u
19 U
1,2,4-TRICHLOROBENZENE
UG/KG
14
u
14
u
110
UJ
140
UJ
110
UJ
75
UJ
5.3
u
5.1
U
49
u
16
u
1 9 U
HEXACHLORO-1,3-BUTADIENE
UG/KG
14
u
14
u
22
UJ
28
UJ
21
UJ
15
UJ
53
u
5.1
U
49
u
16
u
19 U
1,2,3-TRICHLOROBENZENE
UG/KG
14
u
14
u
110
UJ
140
UJ
110
UJ
75
UJ
5.3
u
5.1
U
49
u
16
u
1.9 U
% MOISTURE
%
76
75.3
77.1
74 6
66.6
52 3
53.2
48 8
74.7
71
10
-------
B-Z. Extractabfe Organic Compounds in Sediments.
Terry Creek, Brunswick, Georgia. 1997.
Analyte
Units
001
101
1A
1B
Station
1C 1D
002
003
004
005
BIS(2-CHLOROETHYL) ETHER
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
u
1900
U
4200
U
3900 U
HEXACHLOROETHANE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
u
1900
U
4200
U
3900 U
BIS{2-CHLOROISOPROPYL) ETHER
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
N-NITROSODI-N-PROPYLAMINE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
NITROBENZENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
HEXACHLOROBUTADIENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
2-METHYLNAPHTHALENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
1,2,4-TRICHLOROBENZENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
NAPHTHALENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
4-CHLOROANILINE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
BIS(2-CHLOROETHOXY)METHANE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
ISOPHORONE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
HEXACHLOROCYCLOPENTADIENE (HCCP)
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
2-CHLORONAPHTHALENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
2-NITROANILINE
UG/KG
4300
j
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
ACENAPHTHYLENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
ACENAPHTHENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
U
4200
U
3900 U
DIMETHYL PHTHALATE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
u
4200
U
3900 U
DIBENZOFURAN
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
u
2700
U
2700
U
1900
u
4200
U
3900 U
2,4-DINITROTOLUENE
UG/KG
4300
U
4300
U
5700
U
4800
u
3600
u
2700
U
2700
U
1900
u
4200
u
3900 U
2,6-DINITROTOLUENE
UG/KG
4300
U
4300
U
5700
U
4800
u
3600
u
2700
U
2700
U
1900
u
4200
u
3900 U
3-NITROANILINE
UG/KG
4300
u
4300
U
5700
U
4800
u
3600
u
2700
u
2700
U
1900
u
4200
u
3900 U
4-CHLOROPHENYL PHENYL ETHER
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
U
1900
u
4200
u
3900 U
4-NITROANILINE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
U
1900
u
4200
u
3900 U
FLUORENE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
U
1900
u
4200
u
3900 U
DIETHYL PHTHALATE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
U
1900
u
4200
u
3900 U
N-NITROSODIPHENYLAMINE/DIPHENYLAMIN UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
HEXACHLOROBENZENE (HCB)
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
4-BROMOPHENYL PHENYL ETHER
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
PHENANTHRENE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
ANTHRACENE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
DI-N-BUTYLPHTHALATE
UG/KG
4300
J
4300
J
5700
J
4800
J
2800
J
2700
u
2700
J
1900
u
4200
u
3900 U
FLUORANTHENE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
1 x-ppuaddv
q xfpuaddy
3 XTpuarf'T
-------
B-2 (cont). Extractable Organic Compounds in Sediments.
Terry Creek, Brunswick, Georgia. 1997.
Analyte
Units
001
101
1A
1B
Station
1C 1D
002
003
004
005
PYRENE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
u
1900
U
4200
U
3900 U
BENZYL BUTYL PHTHALATE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
BIS(2-ETHYLHEXYL) PHTHALATE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
BENZO(A)ANTHRACENE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
CHRYSENE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
3,3-DICHL0R0BENZIDINE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
DI-N-OCTYLPHTHALATE
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
BENZO(B AND/OR KJFLUORANTHENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
BENZO-A-PYRENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
INDENO (1,2,3-CD) PYRENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
DIBENZO(A,H)ANTHRACENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
BENZO(GHI)PERYLENE
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
2-CHLOROPHENOL
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
2-METHYLPHENOL
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
(3-AND/OR 4-)METHYLPHEN0L
UG/KG
4300
U
4300
U
5000
J
4800
U
3600
U
2700
U
2700
U
1900
U
4200
U
3900 U
2-NITR0PHEN0L
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
u
3900 U
PHENOL
UG/KG
4300
U
4300
U
5700
U
4800
U
3600
U
2700
U
2700
U
1900
U
4200
u
3900 U
2,4-DIMETHYLPHENOL
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
u
3900 U
2.4-DICHLOROPHENOL
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
U
4200
u
3900 U
2,4,6-TRICHLOROPHENOL
UG/KG
4300
U
4300
U
5700
u
4800
U
3600
U
2700
U
2700
U
1900
u
4200
u
3900 U
2,4,5-TRICHLOROPHENOL
UG/KG
4300
U
4300
u
5700
u
4800
u
3600
U
2700
U
2700
U
1900
u
4200
u
3900 U
4-CHLORO-3-METHYLPHENOL
UG/KG
4300
U
4300
u
5700
u
4800
u
3600
U
2700
U
2700
U
1900
u
4200
u
3900 U
2,4-DINITROPHENOL
UG/KG
8500
U
8500
u
11000
u
9500
u
7100
U
5400
u
5500
U
3900
u
8300
u
7700 U
2-METHYL-4.6-DINITROPHENOL
UG/KG
8500
U
8500
u
11000
u
9500
u
7100
u
5400
u
5500
u
3900
u
8300
u
7700 U
PENTACHLOROPHENOL
UG/KG
8500
U
8500
u
11000
u
9500
u
7100
u
5400
u
5500
u
3900
u
8300
u
7700 U
4-NITROPHENOL
UG/KG
8500
U
8500
u
11000
u
9500
u
7100
u
5400
u
5500
u
3900
u
8300
u
7700 U
2,3,4,6-TETRACHLOROPHENOL
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
CARBAZOLE
UG/KG
4300
u
4300
u
5700
u
4800
u
3600
u
2700
u
2700
u
1900
u
4200
u
3900 U
% MOISTURE
%
75.8
33.9
45
53.2
51 2
74 7
73 2
-------
g_2 (cont.). Miscellaneous Extractabl© Compounds in Sediment.
Terry Creek, Brunswick, Georgia. 1997.
Compound
1A
Station
1D
005
1 UNIDENTIFIED COMPOUND
10 UNIDENTIFIED COMPOUNDS 100000 J
3 UNIDENTIFIED COMPOUNDS
CAMPHENE UG/KG 300 JN
DECAHYDROTRIMETHYLMETHANOAZULENE 7000 JN
METHYL(METHYLETHYL)BENZENE 40000 JN
METHYL(METHYLETHYL)CYCLOHEXANE 20000 JN
OCTAHYDRO(DIMETHYLETHYL)PHENANTHRENECARBOXYLIC ACID, METHYL ESTE 6000 JN
PINENE B000 JN
TRIMETHYLBICYCLOHEPTANONE 8000 JN
TWO UNIDENTIFIED CO UG/KG 800 JN
4000 J
10000 J
-------
B-3. Pesticides / PCB's in Sediment.
Terry Creek, Brunswick, Georgia. 1997.
Analyte
Units
ALDRIN
UG/KG
HEPTACHLOR
UG/KG
HEPTACHIOR EPOXIDE
UG/KG
ALPHA-BHC
UG/KG
BETA-BHC
UG/KG
GAMMA-BHC (LINDANE)
UG/KG
DELTA-BHC
UG/KG
ENDOSULFAN I (ALPHA)
UG/KG
DIELDRIN
UG/KG
4,4'-DDT (P,P'-DDT)
UG/KG
4,4'-DDE (P.P'-DDE)
UG/KG
4,4'-DDD (P.P'-DDD)
UG/KG
ENDRIN
UG/KG
ENDOSULFAN II (BETA)
UG/KG
ENDOSULFAN SULFATE
UG/KG
CHLORDANE (TECH. MIXTURE)
/ UG/KG
PCB-1242 (AROCLOR 1242)
UG/KG
PCB-1254 (AROCLOR 1254)
UG/KG
PCB-1221 (AROCLOR 1221)
UG/KG
PCB-1232 (AROCLOR 1232)
UG/KG
PCB-1248 (AROCLOR 1248)
UG/KG
PCB-1260 (AROCLOR 1260)
UG/KG
PCB-1016 (AROCLOR 1016)
UG/KG
PCB-1268 (AROCLOR 1268)
UG/KG
TOXAPHENE
UG/KG
METHOXYCHLOR
UG/KG
ENDRIN KETONE
UG/KG
% MOISTURE
%
Station
001 101 1A 1B 1C 1D 002 003 004 005
210
U
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
U
18 U
210
U
210
U
5700
u
240
U
180
U
1400
U
50
U
10
U
21
U
18 U
210
U
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
210
u
210
U
5700
U
240
U
180
U
1400
U
50
U
10
U
21
u
18 U
800
u
530
U
11000
u
600
U
440
U
3400
U
200
U
24
U
52
u
44 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
U
500
U
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
U
500
U
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
U
500
U
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
U
500
U
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
u
500
u
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
U
890
U
6800
u
500
u
48
U
100
u
89 U
1600
u
1100
u
22000
u
1200
u
890
U
6800
u
500
u
48
U
100
u
89 U
530
u
530
u
22000
u
1100
u
890
U
6800
u
500
u
48
U
100
u
89 U
9100
J
8100
J
230000
J
3800
JN
7900
J
18000
J
1500
JN
390
U
830
u
710 U
430
u
420
u
5700
u
240
U
180
U
1400
u
200
U
19
u
41
u
36 U
210
u
210
u
5700
u
240
U
180
u
1400
u
50
U
10
u
21
u
18 U
76
75
79
77
66
55
53
49
75
71
-------
B-4. Metals In Sediment.
Terry Creek, Brunswick, Georgia. 1997
Analyte
Units
001
101
1A
1B
1C
Station
1D
002
003
004
005
SILVER
MG/KG
3
U
3
U
3
U
3
U
4
U
2
U
2
U
2
U
3
U
3 U
ARSENIC
MG/KG
15
14
14
16
19
10
12
89
17
17
BARIUM
MG/KG
28
32
44
27
36
20
22
18
26
39
BERYLLIUM
MG/KG
1.5
U
1 5
U
1.5
U
1 5
U
2
U
1
U
1
U
1
U
1 5
U
1.6
CADMIUM
MG/KG
1.5
U
1 5
U
1 5
U
1 5
U
2
U
1
U
1
U
1
U
1 5
U
1 5 U
COBALT
MG/KG
7
8.3
65
69
7.3
4 9
46
4 2
7 2
98
CHROMIUM
MG/KG
44
51
44
42
55
28
30
26
43
52
COPPER
MG/KG
15
17
31
12
14
9.6
7.2
56
10
15
MOLYBDENUM
MG/KG
3
U
3
U
3
U
3
U
4
U
2
U
2
U
2
U
3
U
3 U
NICKEL
MG/KG
12
16
18
12
15
79
8.6
6.1
10
18
LEAD
MG/KG
23
24
32
22
26
12
12
10
21
24
ANTIMONY
MG/KG
9
U
9
U
9
U
9
U
12
U
6
U
6
U
6
U
9
U
9 U
SELENIUM
MG/KG
12
U
8
U
12
U
12
U
16
U
8
U
8
U
8
U
12
U
12 U
TIN
MG/KG
7.5
U
8
U
8.5
U
9
U
10
U
5
U
6
U
6
U
7.5
U
8 U
STRONTIUM
MG/KG
56
59
79
63
70
48
100
150
57
61
TELLURIUM
MG/KG
15
U
15
U
15
U
15
U
20
U
10
U
10
U
10
U
15
U
15 U
TITANIUM
MG/KG
260
250
250
240
280
240
220
230
240
310
THALLIUM
MG/KG
30
U
30
U
30
U
30
U
40
U
20
U
20
U
20
U
30
U
30 U
VANADIUM
MG/KG
57
63
55
56
74
37
39
32
53
74
YTTRIUM
MG/KG
17
19
15
17
19
12
13
12
14
21
ZINC
MG/KG
69
78
110
64
75
35
41
34
55
79
TOTAL MERCURY
MG/KG
0.075
0.8
0 12
0053
0 068
0.052
005
U
0.05
U
0.074
0.056
ALUMINUM
MG/KG
30000
35000
27000
27000
37000
18000
19000
15000
27000
35000
MANGANESE
MG/KG
260
260
260
330
520
310
360
260
350
510
CALCIUM
MG/KG
4200
4300
7600
5600
5400
8400
14000
25000
5000
4100
MAGNESIUM
MG/KG
6700
7300
, 7000
6200
7600
4100
5000
4700
6400
6600
IRON
MG/KG
25000
28000
24000
24000
32000
17000
20000
16000
24000
33000
SODIUM
MG/KG
19000
19000
20000
16000
14000
8600
11000
9100
18000
8700
POTASSIUM
MG/KG
3700
4300
3500
3600
4200
2200
2000
2000
3700
3400
% MOISTURE
%
70
74
77
75
67
52
53
53
73
71
-------
•JIOXI/V SCAN
Facility TERRY CREEK DRUDGE
Program SSF
Id/Station 001
Media SOIL
BRUNSWICK. GA
D Number 001
Collected By
Beginning 02/19/97 14:10
Ending
SAS NumberSPR
Org Contractor: SWOK
RESULTS
UNITS
10U
NG/KG
10UJ
NG/KG
25U
NG/KG
25UJ
NG/KG
25U
NG/KG
25U
NG/KG
25U
NG/KG
8 6J
NG/KG
25U
NG/KG
9 3J
NG/KG
77
NG/KG
10U
NG/KG
14 J
NG/KG
25U
NG/KG
25U
NG/KG
22J
NG/KG
25U
NG/KG
25U
NG/KG
25U
NG/KG
25U
NG/KG
25UJ
NG/KG
25U
NG/KG
25U
NG/KG
25UJ
NGfKG
50U
NG/KG
0 08
NG/KG
79
%
ANALYTE
2.3.7,8-TETRACHLORODIBENZODIOXIN
TETRACHLORODIBENZOOIOXIN (TOTAL)
1.2,3.7.8-PENTACHLORODIBENZODIOXIN
PENTACHLORODIBENZODIOXIN (TOTAL)
1,2,3,4.7,8-HEXACHLORODIBENZODIOXIN
1.2.3.6.7.8-HEXACHLORODIBENZODIOXIN
1.2.3.7.8.9-HEXACHLORODIBENZODIOXIN
HEXACHLORODIBENZODIOXIN (TOTAL)
1.2,3.4.6.7.8-HEPTACHLORODIBENZODIOXIN
HEPTACHLORODIBENZODIOXIN (TOTAL)
OCTACHLORODIBENZODIOXIN
2,3.7,8-TETRACHLORODIBENZOFURAN
TETRACHLORODIBENZOFURAN (TOTAL)
1,2,3,7,8-PENTACHLORODIBENZOFURAN
2.3.4,7,8-PENTACHLORODIBENZOFURAN
PENTACHLORODIBENZOFURAN (TOTAL)
1,2,3,4,7,8-HEXACHLORODIBENZOFURAN
1.2.3.6.7.8-HEXACHLORODIBENZOFURAN
1.2.3.7.8.9-HEXACHLORODIBENZOFURAN
2,3,4.6,7.8-HEXACHLORODIBENZOFURAN
HEXACHLORODtBENZOFURAN (TOTAL)
1.2,3.4,6,7.8-HEPTACHLORODIBENZOFURAN
1.2,3.4.7,0.9-HEPTACHLORODIBENZOFURAN
HEPTACHLORODIBENZOFURAN (TOTAL)
OCTACHLORODIBE NZOFURAN
TEQ (TOXIC. EQUIV VALUE. FROM l-TEF/89)
% MOISTURE
A-average value NA-not analyzed NAI-tnterferences J-esttmated value N-presumpllve evidence of presence ot material
K-actual value Is known lo be less than value given L-actual value Is known to be greater than value given U-material was analyzed for but not detected, the number Is the minimum quantitation Rmlt
R-qc Indicates thai data unusable, compound may or may not be present resampling and reanalysls Is necessary for verification
confirmed by ocms 1 when no value is reported, see r.hlorrianp constituents 7 constituents rw metabolites of technlral rMnrrian*
-------
UtOXtT* SCAN
Facility TERRY CREEK DRUDGE
Program' SSF
Id/Station 005
Media SOIL
i t am i*b
BRUNSWICK, GA
D Number' 005
Collected By
Beginning 02/19/97 15:20
Ending.
SAS NumberSPR
Org Contractor: SWOK
RESULTS
UNITS
7 OU
NG/KG
7 OUJ
NG/KG
18U
NG/KG
18UJ
NG/KG
18U
NG/KG
18U
NG/KG
18U
NG/KG
14J
NG/KG
8.4J
NG/KG
19J
NG/KG
80
NG/KG
7 0U
NG/KG
7 OUJ
NG/KG
18U
NG/KG
18U
NG/KG
18UJ
NG/KG
18U
NG/KG
18U
NG/KG
18U
NG/KG
18U
NG/KG
18UJ
NG/KG
18U
NG/KG
18U
NG/KG
18UJ
NG/KG
35U
NG/KG
0 16J
NG/KG
72
%
ANALYTE
2,3,7,8-TETRACHLORODIBENZODIOXIN
TETRACHLORODIBENZODIOXIN (TOTAL)
1,2.3,7.8-PENTACHLORODIBENZODIOXIN
PENTACHLORODIBENZODIOXIN (TOTAL)
1,2,3,4,7,8-HEXACHLORODIBENZODIOXIN
1.2.3.6.7.8-HEXACHLORODIBENZODIOXIN
1.2.3.7.8.9-HEXACHLORODIBENZODIOXIN
HEXACHLORODIBENZODIOXIN (TOTAL)
1,2,3,4,6,7,8-HEPTACHLORODIBENZODIOXIN
HEPTACHLORODIBENZOOIOXIN (TOTAL)
OCTACHLORODIBENZODIOXIN
2,3,7.8-TETRACHLORODIBENZOFUR AN
TETRACHLORODIBENZOFURAN (TOTAL)
1,2.3,7,8-PENTACHLORODIBENZOFURAN
2,3.4.7,8-PENTACHLORODIBENZOFURAN
PENTACHLORODIBENZOFURAN (TOTAL)
1,2,3,4,7,8-HEXACHLORODIBENZOFURAN
1.2.3.6.7.8-HEXACHLORODIBENZOFURAN
1.2.3.7.8.9-HEXACHLORODIBENZOFURAN
2,3,4,6,7,8-HEXACHLORODIBENZOFURAN
HEXACHLORODIBENZOFURAN (TOTAL)
1.2.3.4.6.7.8-HEPTACHLORODIBENZOFURAN
1.2.3.4.7.8.9-HEPTACHLORODIBENZOFURAN
HEPTACHLORODIBENZOFURAN (TOTAL)
OCTACHLORODIBENZOFURAN
TEQ (TOXIC. EQUIV. VALUE, FROM l-TEF/89)
% MOISTURE
A-average value NA-not analyzed. NAI-lnterferences. J-estimated value. N-presumpttve evidence of presence of material.
K-actual value Is known to be less than value given. I.-actual value Is known to be greater than value plven, U-material was analyzed for but no< detected, the number Is the minimum quantitation Hmlt.
R-qc indicates that data unusable compound may or may not be present, resampling and reanalysls Is necessary for verification
confirmed by gems 1 when no value is reported, see chlordane constituents 2 constituents or metabolites of technical chlorrlane
-------
,..~r
dioxin scan
Facility TERRY CREEK DRUDGE BRUNSWICK, GA
Program: SSF
Id/Stafion LVPE
Media LVPE D Number LVPE
SAS Number SPR
Orq Contractor: SWOK
Collected By
Beginning 02/20/97 10 45
Ending
#BJV279
RESULTS
UNITS
260
NG/KG
2800J
NG/KG
5 0U
NG/KG
5 OUJ
NG/KG
5 0U
ng/kg
5 0U
NG/KG
5 0U
NG/KG
5 OUJ
NG/KG
0 27J
NG/KG
0.27J
NG/KG
10U
NG/KG
2 0U
NG/KG
1 1J
NG/KG
5.0U
NG/KG
5 0U
NG/KG
5 OUJ
NG/KG
5.0U
NG/KG
5 OU
NG/KG
5 0U
NG/KG
5.0U
NG/KG
5.OUJ
NG/KG
5 OU
NG/KG
5.0U
NG/KG
5 OUJ
NG/KG
10U
NG/KG
—
NG/KG
NA
%
ANALYTE
2.3,7,8-TETRACHLORODIBENZODIOXIN
TETRACHLORODIBENZODIOXIN (TOTAL)
1,2,3,7.8-PENTACHLORODIBENZODIOXIN
PENTACHLORODIBENZODIOXIN (TOTAL)
1,2.3,4,7,8-HEXACHLORODIBENZODIOXIN
1.2.3.6.7.8-HEXACHLORODIBENZODIOXIN
1.2.3.7.8.9-HEXACHLORODIBENZODIOXIN
HEXACHLORODIBENZODIOXIN (TOTAL)
1.2.3.4,6,7,8-HEPTACHLORODIBENZODIOXIN
HEPTACHLORODIBENZODIOXIN (TOTAL)
OCTACHLORODIBENZODIOXIN
2,3,7,8-TETRACHLORODIBENZOFURAN
TETRACHLORODIBENZOFURAN (TOTAL)
1,2,3,7,8-PENTACHLORODIBENZOFURAN
2.3,4.7.8-PENTACHLORODIBENZOFURAN
PENTACHLORODIBENZOFURAN (TOTAL)
1.2,3,4.7,8-HEXACHLORODIBENZOFURAN
1.2.3.6.7.8-HEXACHLORODIBENZOFURAN
1.2.3.7.8.9-HEXACHLORODIBENZOFURAN
2.3,4,6.7,8-HEXACHLORODIBENZOFURAN
HEXACHLOROOIBENZOFURAN (TOTAL)
1.2.3.4.6.7.8-HEPTACHLORODIBENZOFURAN
1.2.3.4.7.8.9-HEPT ACHLORODIBENZOFUR AN
HEPTACHLORODIBENZOFURAN (TOTAL)
OCTACHLORODIBENZOFURAN
TEQ (TOXIC. EQUIV. VALUE. FROM l-TEF/89)
% MOISTURE
A-average value NA no< snatyzed NAI-lnlerferences. J-esltmated value N-presumptlve evidence of presence of material.
K-actual value Is known to be less than value given L-actual value Is known to be greater than value given U-materlal was analyzed for but not detected the number Is the minimum quantitation Smtt,
R-qc Indicates that data unusable compound may or may not be present resampling and reanalysls Is necessary for verification.
- infirmed by gems 1 when no value Is reported, see chlordane constituents 7 constituents or metabolites of technical chlordane
-------
. . 9
tncrxif» scan
rncilily TERRY CREEK DRUDGE
Program SSF
Id/Station QCBLK
Media. QCBLK
, i — r i* * *
BRUNSWICK. GA
D Number: BLK
SAS Number.SPR
Org Contractor: SWOK
Collected By
Beginning 02/20/97 10 45
Ending-
#PC01196
RESULTS
UNITS
2 OU
NG/KG
2 OUJ
NG/KG
5 OU
NG/KG
5 OUJ
NG/KG
SOU
NG/KG
5 OU
NG/KG
5 OU
NG/KG
5 OUJ
NG/KG
5 OU
NG/KG
5 OU
NG/KG
1 5J
NG/KG
2 OU
NG/KG
2 OUJ
NG/KG
5 OU
NG/KG
5 OU
NG/KG
5 OUJ
NG/KG
5 OU
NG/KG
5 OU
NG/KG
5 OU
NG/KG
5 OU
NG/KG
5.OUJ
NG/KG
0 16J
NG/KG
5 OU
NG/KG
0 16J
NG/KG
10U
NG/KG
—
NG/KG'
NA
%
ANALYTE
2.3,7,8-TETRACHLORODIBENZODIOXIN
TETRACHLORODIBENZODIOXIN (TOTAL)
1,2.3.7,8-PENTACHLORODIBENZODIOXIN
PENTACHLORODIBENZODIOXIN (TOTAL)
1.2.3,4.7,8-HEXACHLORODIBENZODIOXIN
1.2.3.6.7.8-HEXACHLORODtBENZODIOXIN
1.2.3.7.8.9-HEXACHLORODIBENZODIOXIN
HEXACHLORODIBENZODIOXIN (TOTAL)
1.2,3.4,6,7,8-HEPTACHLORODIBENZODIOXIN
HEPTACHLOROOIBENZODIOXIN (TOTAL)
OCTACHLORODIBENZODIOXIN
2,3,7.8-TETRACHLORODIBENZOFUR AN
TETRACHLORODIBENZOFURAN (TOTAL)
1,2,3.7.8-PENT ACHLORODIBENZOFUR AN
2,3,4,7,8-PENTACHLORODIBENZOFURAN
PENTACHLORODIBENZOFURAN (TOTAL)
1.2.3,4,7,8-HEXACHLORODIBENZOFURAN
1.2.3.6.7.8-HEXACHLORODIBENZOFURAN
1.2.3.7.8.9-HEXACHLORODIBENZOFURAN
2,3.4,6,7,8-HEXACHLORODIBENZOFURAN
HEXACHLORODIBENZOFURAN (TOTAL)
1.2.3.4.6.7.8-HEPTACHLORODIBENZOFUR AN
1.2.3.4.7.8.9-HEPTACHLORODIBENZOFURAN
HEPT ACHLORODIBENZOFUR AN (TOTAL)
OCT ACHLORODIBENZOFUR AN
TEQ (TOXIC EQUIV VALUE. FROM l-TEF/89)
% MOISTURE
A-average value NA-not analyzed. NAt-lnferfereoces J-estlmated value. N-presumptlve evidence of presenc« of material
K-actual value Is known (o be less than value given. L-actual value Is known to be greater than value given U-rnatertal was analyzed for In if not detected the number Is the minimum quantitation limit
R-qc Indicates that data unusable compound may or may not be present resampling and reanalysls Is necessary for verification
-confirmed by gems t.when no value Is reported, see chlordane constituents 2 constituents or metabolites of technical chtordarte
-------
DATA OTTAT.TFTFT? PEPORT
Project No,
Site Name:
97-0146
Terry Creek Dredge
Affected
gampi pc anaiyr.e
All
total congeners
Flag
Used
Assumed Resp. Factors/
Cal. Stds not available
for all congeners
005
1234678 HpCDD
TEQ's : The Toxic Equivalent (TEQ) represents a summation of
values from the individual equivalents that are calculated for
each of the 2,3,7,8 containing isomers. If 10% or greater of the
TEQ value was from data considered to be estimated, then the TEQ
is reported as estimated (J flag).
Abbreviation Key:
TCDD = Tetrachlorodibenzodioxin
PeCDD * Pentachlorodibenzodioxin
HxCDD = Hexachlorodibenzodioxin
HpCDD = Heptachlorodibenzodioxin
OCDD E Octachlorodibenzodioxin
Is •= Internal Standard
TCDF » Tetrachlorodibenzofuran
PeCDF « Pentachlorodibenzofuran
HxCDF « Hexachlorodibenzofuran
HpCDF - Heptachlorodibenzofuran
OCDF - Octachlorodibenzofuran
Eaasfls rndoc
;¦ Results lower than the minimum quantitation limit
Results higher than the maximum calibration limit
-------
>
(t)
3
&
H*
X
n
-------
C-1. Extractable Organic Compounds in Blue Crab Tissue.
Terry Creek, Brunswick, Georgia. 1997.
Analyte
BIS(2-CHLOROETHYL) ETHER
HEXACHLOROETHANE
BlS(2-CHLOROlSOPROPYL) ETHER
N-NITROSODI-N-PROPYLAMINE
NITROBENZENE
hexachlorobutadiene
2-METHYLNAPHTHALENE
1,2,4-TRICHLOROBENZENE
NAPHTHALENE
4-CHLOROANILINE
BIS(2-CHLOROETHOXY)METHANE
ISOPHORONE
HEXACHLOROCYCLOPENTADIENE (HCCP)
2-CHLORONAPHTHALENE
2-NITROANILINE
ACENAPHTHYLENE
ACENAPHTHENE
DIMETHYL PHTHALATE
DIBENZOFURAN
2,4-DINITROTOLUENE
2,6-DINITROTOLUENE
5-NITRO AN I LI N E
4-CHLOROPHENYL PHENYL ETHER
NITROANILINE
¦UORENE
IETHYL PHTHALATE
•NITROSODIPHENYLAMINE/DIPHENYLAMIN
EXACHLOROBENZENE (HCB)
¦BROMOPHENYL PHENYL ETHER
HENANTHRENE
NTHRACENE
"-N-BUTYLPHTHALATE
•UORANTHENE
^RENE
::-NZYL BUTYL PHTHALATE
¦S(2-ETHYLHEXYL) PHTHALATE
-NZO(A)ANTHRACENE
•HRYSENE
•3-DlCHLOROBENZIDINE
•'•S-OCTYLPHTHALATE
;^0(B AND/OR K)FLUORANTHENE
-NZO-A-PYRENE
,:>EN0 (1,2.3-CD) PYRENE
;EN20(A,H) ANTH R AC E N E
;^0(GHI)PERYLENE
•-^OROPHENOL
^ethvlphenol
•^ND/OR 4-)METHYLPHENOL
vtR0PHENOL
Station
Units
001
002
003
004
005
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
17
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
U
1.6
U
1.6
U
1.7
U
1 3
U
MG/KG
1.9
u
1.6
U
1.6
U
1.7
U
1.3
U
MG/KG
1.9
u
1.6
U
1.6
U
1.7
U
1 3
u
MG/KG
1 9
u
1.6
U
1.6
U
1.7
U
1.3
u
MG/KG
1.9
u
1.6
U
1.6
U
1.7
u
1.3
u
MG/KG
1.9
u
1.6
U
1.6
U
1.7
u
1.3
u
MG/KG
1 9
u
1.6
U
1.6
U
1.7
u
1.3
u
MG/KG
1.9
u
1.6
U
1.6
U
1.7
u
1 3
u
MG/KG
1.9
u
1.6
U
1.6
U
1.7
u
1.3
u
MG/KG
1.9
u
1.6
U
1.6
U
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
U
1 7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
U
1.7
u
1.3
u
MG/KG
1 9
u
1.6
u
1.6
U
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1 3
u
MG/KG
1 9
u
1.6
u
1.6
u
1.7
u
1 3
u
MG/KG
1.9
u
1 6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1 6
u
1.7
u
1 3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1 3
u
MG/KG
1.9
u
1 6
u
1.6
u
1 7
L
1 3
u
MG/KG
1 9
u
1.6
u
1 6
u
1.7
u
1 3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1 9
u
1.6
u
1.6
u
1 7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1 3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1 6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1 3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
MG/KG
1.9
u
1.6
u
1.6
u
1.7
u
1.3
u
-------
C-1 (cont). Extractable Organic Compounds in Blue Crab Tissue.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
002
003
004
005
PHENOL
MG/KG
1.9
U
1.6 U
1.6
U
1.7
U
1.3 U
2,4-DIMETHYLPHENOL
MG/KG
1.9
U
1.6 U
1.6
U
1.7
U
1.3 U
2,4-DICHLOROPHENOL
MG/KG
1.9
u
1.6 U
1.6
U
1.7
U
1.3 U
2,4,6-TRICHLOROPHENOL
MG/KG
1.9
u
1.6 U
1.6
U
1.7
u
1 3 U
2,4,5-TRICHLOROPHENOL
MG/KG
1.9
u
1.6 U
1.6
U
1.7
U
1.3 U
4-CHLORO-3-METHYLPHENOL
MG/KG
1.9
u
1.6 U
1.6
U
1.7
u
1.3 U
2,4-DINITROPHENOL
MG/KG
3.7
u
3.2 U
3.2
U
3.3
u
2.5 U
2-METHYL-4.6-DINITROPHENOL
MG/KG
3.7
u
3.2 U
3.2
U
3.3
u
2.6 U
PENTACHLOROPHENOL
MG/KG
37
u
3.2 U
3.2
U
3.3
u
2.6 U
4-NITROPHENOL
MG/KG
3.7
u
3.2 U
3.2
U
1.7
U
1.3 U
2,3,4,6-TETRACHLOROPHENOL
MG/KG
1.9
u
1.6 U
1.6
U
1.7
U
1.3 U
CARBAZOLE
MG/KG
1.9
u
1 6 U
1.6
U
1 7
u
1.3 U
Miscellaneous Extractable Organic Compounds in Blue Crab Tissue.
Station
Analyte Units 001 002 003 004 005
UNIDENTIFIED COMPOUND
10 J
10 J
UNIDENTIFIED COMPOUNDS
10 J
EXADECANOIC ACID
20 JN
20 JN
20 JN
30 JN
EXADECENOIC ACID
7 JN
10 JN
10 JN
10 JN
ETHYLEICOSAPENTAENOATE
40 JN
IACINAMIDE
CTADECANOIC ACID
3 JN
30 JN
8 JN
10 JN
1EIC ACID
20 JN
10 JN
30 JN
40 JN
ETRADECANOIC ACID
2 JN
3 JN
3 JN
ETRADECANOOIC ACID
2 JN
1TAMIN E
8 JN
9 JN
10 JN
10 JN
-------
C-2. Pesticides I PCB's in Blue Crab Tissue.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
002
003
004
005
ALDRIN
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
HEPTACHLOR
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
HEPTACHLOR EPOXIDE
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
ALPHA-BHC
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
BETA-BHC
MG/KG
0.01
UJ
0.008 U
0.008 U
0.006 U
0.006 U
GAMMA-BHC (LINDANE)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
DELTA-BHC
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
ENDOSULFAN I (ALPHA)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
DIELDRIN
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
4,4'-DDT (P.P'-DDT)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
4,4'-DDE (P.P'-DDE)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
4,4'-DDD (P,P'-DDD)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
ENDRIN
MG/KG
0 01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
ENDOSULFAN II (BETA)
MG/KG
0.01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
ENDOSULFAN SULFATE
MG/KG
0 01
UJ
0.008 U
0.008 U
0.008 U
0.006 U
CHLORDANE (TECH. MIXTURE) 11 MG/KG
0.024 UJ
0.019 U
0 02 U
0 021 U
0.016 U
PCB-1242 (AROCLOR 1242)
MG/KG
0.048
UJ
0.039 U
0 04 U
0.041 U
0.032 U
PCB-1254 (AROCLOR 1254)
MG/KG
0.048 UJ
0 039 U
0 04 U
0.041 U
0.032 U
PCB-1221 (AROCLOR 1221)
MG/KG
0.048
UJ
0 039 U
0 04 U
0.041 U
0.032 U
PCB-1232 (AROCLOR 1232)
MG/KG
0 048
UJ
0.039 U
0.04 U
0.041 U
0.032 U
PCB-1248 (AROCLOR 1248)
MG/KG
0.048 UJ
0.039 U
0 04 U
0.041 U
0.032 U
PCB-1260 (AROCLOR 1260)
MG/KG
0.048
UJ
0.039 U
0.04 U
0.041 U
0.032 U
PCB-1016 (AROCLOR 1016)
MG/KG
0.048 UJ
0.039 U
0.04 U
0.041 U
0.032 U
PCB-1268 (AROCLOR 1268)
MG/KG
0.048 UJ
0.039 U
0.04 U
0.041 U
0.032 U
TOXAPHENE
MG/KG
0 39 UJ
0.31 U
0.32 U
0.33 U
0.26 U
METHOXYCHLOR
MG/KG
0 019 UJ
0.016 U
0.016 U
0.017 U
0.013 U
ENDRIN KETONE
MG/KG
001
UJ
0.008 U
0.008 U
0.008 U
0.006 U
-------
C-3. Metals in Blue Crab Tissue.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
001
002
003
004
005
SILVER
MG/KG
0.18
U
0.19
U
0.2
U
0.19
U
0.19 U
ARSENIC
MG/KG
2.9
3.6
3.1
2
0.95
BARIUM
MG/KG
0.18
u
0 19
U
0.2
u
0.19
U
0.19 U
BERYLLIUM
MG/KG
0.09
u
0.09
U
0.1
u
0.09
U
0.1 u
CADMIUM
MG/KG
0 09
u
0.09
U
0.1
u
0.09
U
0.1 u
COBALT
MG/KG
018
u
0 19
U
0.2
u
019
U
0.19 U
CHROMIUM
MG/KG
0.18
u
0.19
U
0.21
0.24
0.19 U
COPPER
MG/KG
11
9.7
12
6.5
9
MOLYBDENUM
MG/KG
0 18
u
0.19
U
0.2
u
0.19
U
0.19 U
NICKEL
MG/KG
0.35
u
0.37
U
0.39
u
0.38
U
0.38 U
LEAD
MG/KG
07
u
0.75
U
0 78
u
075
U
0.76 U
ANTIMONY
MG/KG
0 53
u
0.56
U
0.59
u
0.56
U
0.57 U
SELENIUM
MG/KG
0 09
u
0.09
U
0.1
u
0.09
U
0.1 U
TIN
MG/KG
0 62
u
0.66
U
0.68
u
0.66
U
0.67 U
STRONTIUM
MG/KG
7,1
7
7.6
11
9.1
TELLURIUM
MG/KG
0 88
U
0.94
U
0 98
U
0.94
U
0.96 U
TITANIUM
MG/KG
0 18
U
0 19
U
0.2
u
0.19
U
0.19 U
THALLIUM
MG/KG
0 04
u
0.04
U
0.04
U
0.04
U
0.04 U
VANADIUM
MG/KG
0.18
u
0 19
U
0.2
u
0.19
U
0.19 U
YTTRIUM
MG/KG
0 18
u
0.19
U
0.2
u
0.19
U
0.19 U
ZINC
MG/KG
34
29
36
41
32
TOTAL MERCURY MG/KG
0 18
0 27
0.16
0.17
0.09
ALUMINUM
MG/KG
35
3.9
4.8
4.2
2.9
MANGANESE
MG/KG
1 2
2 3
0.82
1 5
1.5
CALCIUM
MG/KG
600
570
600
930
750
MAGNESIUM
MG/KG
290
280
300
340
320
IRON
MG/KG
A A
6
6.3
6.4
4.9
SODIUM
MG/KG
1800
1800
2300
2500
2300
POTASSIUM
MG/KG
3000
3400
3400
3300
3300
-------
>
•o
•u
(D
3
a.
-------
, ,Co„«i. L*tr.«wbio organic Compounds in Forage Fish Tissue.
° Terry Creek, Brunswick, Georgia. 1997.
Station
233445559
Analyte Units 03/07/97 03/06/97 03/06/97 03/05/97 03/07/97 03/05/97 03/05/97 03/07/97 03/07/97
PYRENE
MG/KG
68
U
14
U
74
U
14
U
8
U
13
U
13
U
8.2
U
7 U
BENZYL BUTYL PHTHALATE
MG/KG
6 8
U
14
u
74
U
14
U
8
U
13
U
13
U
82
U
7 U
B!S{2-ETHYLHEXYL) PHTHALATE
MG/KG
6 8
U
14
u
74
U
14
U
8
U
13
U
13
U
82
U
7 U
BENZO(A)ANTHRACENE
MG/KG
6 8
U
14
U
7.4
U
14
U
8
U
13
U
13
U
82
U
7 U
CHRYSENE
MG/KG
6 8
U
14
U
74
U
14
U
8
U
13
U
13
U
82
U
7 U
3,3'-DICHLOROBENZIDINE
MG/KG
6.8
U
14
U
74
U
14
U
8
U
13
U
13
U
82
U
7 U
DI-N-OCTYLPHTHALATE
MG/KG
6 8
U
14
U
7.4
U
14
U
8
U
13
U
13
U
8.2
U
7 U
BENZO(B AND/OR K)FLUORANTHENE
MG/KG
68
U
14
U
74
U
14
U
8
U
13
U
13
U
8 2
U
7 U
BENZO-A-PYRENE
MG/KG
6.8
U
14
U
74
U
14
U
8
U
13
U
13
U
82
U
7 U
INDENO (1,2,3-CD) PYRENE
MG/KG
6 8
U
14
U
74
U
14
U
8
U
13
U
13
U
8.2
U
7 U
D»BENZO\A,H)ANTHRACENE
MG/KG
68
U
14
U
7 4
U
14
U
8
U
13
U
13
U
82
U
7 U
BENZO(GHI)PERYLENE
MG/KG
6.8
U
14
U
7.4
U
14
U
8
U
13
U
13
U
8.2
U
7 U
2-CHLOROPHENOL
MG/KG
6 8
U
14
U
74
U
14
U
8
U
13
U
13
U
8.2
U
7 U
2-METHYLPHENOL
MG/KG
6.8
U
14
U
74
U
14
U
8
U
13
U
13
U
82
U
7 U
(3-AND/OR 4-)METHYLPHENOL
MG/KG
68
U
14
U
74
U
14
U
8
U
13
U
13
U
8.2
U
7 U
2-NITROPHENOL
MG/KG
6.8
U
14
U
7.4
U
14
U
8
U
13
U
13
U
82
U
7 U
PHENOL
MG/KG
6 8
U
14
U
7.4
U
14
U
8
U
13
U
13
U
1.7
J
7 U
2.4-DIMETHYLPHENOL
MG/KG
6 8
U
14
U
74
U
14
U
8
U
13
U
13
U
8.2
u
7 U
2,4-DICHLOROPHENOL
MG/KG
6.8
u
14
U
74
u
14
U
8
U
13
U
13
U
8.2
u
7 U
2,4,6-TRICHLOROPHENOL
MG/KG
6.8
u
14
U
74
u
14
U
8
U
13
U
13
U
82
u
7 U
2,4,5-TRICHLOROPHENOL
MG/KG
6.8
u
14
U
74
u
14
U
8
U
13
U
13
U
82
u
7 U
4-CHLORO-3-METHYLPHENOL
MG/KG
6.8
u
14
U
7.4
u
14
U
8
U
13
U
13
U
82
u
7 U
2.4-DINITROPHENOL
MG/KG
14
u
29
U
15
u
28
U
16
U
26
U
27
U
16
u
14 U
2-METHYL-4.6-DINITROPHENOL
MG/KG
14
u
29
U
15
u
28
U
16
U
26
U
27
U
16
u
14 U
PENTACHLOROPHENOL
MG/KG
14
u
29
U
15
u
28
U
16
U
26
U
27
U
16
u
14 U
4-NITROPHENOL
MG/KG
14
u
29
U
15
u
28
U
16
U
26
U
27
u
16
u
14 U
2,3,4,6-TETRACHLOROPHENOL
MG/KG
68
u
14
u
7.4
U
14
U
8
u
13
U
13
u
82
u
7 U
CARBAZOLE
MG/KG
6.8
u
14
u
7.4
U
14
u
8
u
13
u
13
u
82
U
7 U
-------
0-2. Pesticides f PCB's in Forage Fish Tissu©.
Terry Creek, Brunswick, Georgia. 1997.
Station
3 4 5 5
Analyte
Units
03/05/97
03/05/97
03/05/97
03/05/97
ALDRIN
MG/KG
0 02
U
0 025
u
0 028
U
0.018 U
HEPTACHLOR
MG/KG
0011
U
0 025
U
0 028
U
0.018 U
HEPTACHLOR EPOXIDE
MG/KG
0 029
U
0 032
U
0.028
U
0.018 U
ALPHA-BHC
MG/KG
001
U
0 025
U
0 028
U
0 018 U
BETA-BHC
MG/KG
0 019
u
0 025
U
0 028
U
0 018 U
GAMMA-BHC (LINDANE)
MG/KG
0012
u
0 025
U
0 028
U
0018 U
DELTA-BHC
MG/KG
0 024
u
0 025
U
0 028
U
0018 U
ENDOSULFAN I (ALPHA)
MG/KG
0 028
u
0 065
U
0.028
U
0 018 U
OIELDRIN
MG/KG
0.18
u
0 23
U
0 13
U
0 059 U
4,4'-DDT (P,P'-DOT)
MG/KG
0 037
u
0 05
U
0 045
U
0.034 U
4,4'-DDE (P.P'-DDE)
MG/KG
0 042
u
0 05
U
0.045
U
0.034 U
4,4'-DDD (P.P'-DDD)
MG/KG
0 038
u
0 05
U
0 045
U
0.034 U
ENDRIN
MG/KG
0.036
u
01
U
0.045
U
0.034 U
ENDOSULFAN II (BETA)
MG/KG
0 037
u
0 05
U
0.045
U
0.034 U
ENDOSULFAN SULFATE
MG/KG
0 037
u
0 05
U
0 045
U
0.034 U
CHLORDANE (TECH. MIXTURE) I
MG/KG
0 18
u
0 12
U
0.094
U
0091 U
PCB-1242 (AROCLOR 1242)
MG/KG
0 22
u
0.18
U
0.21
U
02 U
PCB-1254 (AROCLOR 1254)
MG/KG
0 22
u
0 32
U
0.21
U
02 U
PCB-1221 (AROCLOR 1221)
MG/KG
0 22
u
0 18
U
021
U
0.2 U
PCB-1232 (AROCLOR 1232)
MG/KG
0 22
u
0 18
U
021
U
0.2 U
PCB-1248 (AROCLOR 1248)
MG/KG
0 22
u
0 18
u
0 21
U
0 2 U
PCB-1260 (AROCLOR 1260)
MG/KG
0 22
u
0.32
U
0.21
U
02 U
PCB-1016 (AROCLOR 1016)
MG/KG
0 22
u
0 18
u
0.21
u
0.2 U
PCB-1268 (AROCLOR 1268)
MG/KG
0 18
u
0.18
u
0 16
u
0 17 U
TOXAPHENE
MG/KG
66
JN
14
JN
5.3
JN
2 3 JN
METHOXYCHLOR
MG/KG
0072
u
0 07
U
0 065
u
0 066 U
ENDRIN KETONE
MG/KG
0.04
u
0.048
U
0.045
U
0 039 U
-------
D-2 (cont). Forage Fish Tissue Analyzed for Toxaphene and PCB-1268 Only.
Terry Creek, Brunswick, Georgia. 1997.
Station
2 3 4 5 7 8 9
Analyte Units 03/07/97 03/06/97 03/07/97 03/07/97 03/07/97 03/07/97 03/07/97
PCB-1268 (AROCLOR 1268) MG/KG 0 22 U 0.39 U 0 41 U 02U 0 32 U 0.18 U 0.18 U
TOXAPHENE MG/KG 4 8 JN 5.1 JN 27 JN 5 6 JN 1 9 JN 2 7 JN 2.3 JN
-------
£7-3. Metals In Forage Fish Tissue.
Terry Creek, Brunswick, Georgia. 1997.
Station
23344559
Analyte
Units
03/07/97
03/05/97
03/06/97
03/05/97
03/07/97
03/05/97
03/05/97
03/07/97
SILVER
MG/KG
0 19
U
0 8
U
02
U
08
U
02
U
08
U
1 U
0.19 U
ARSENIC
MG/KG
0 95
U
0 5
U
048
0.5
U
0 28
05
U
0.5 U
0.52
BARIUM
MG/KG
1 2
0 97
1.1
1 5
1.5
08
U
0 98
094
BERYLLIUM
MG/KG
0 095
U
04
U
0 098
U
04
U
0.1
U
04
U
05 U
0 095 U
CADMIUM
MG/KG
0 095
U
04
U
0 098
U
04
U
0 1
U
04
U
0 5 U
0.095 U
COBALT
MG/KG
0 19
U
08
U
0 2
U
08
U
0.2
U
08
U
1 U
0.19 U
CHROMIUM
MG/KG
06
08
U
0 35
08
U
0 31
0.8
U
3 U
0 36
COPPER
MG/KG
2 5
1 4
1 6
1 2
1 3
15
2
2.7
MOLYBDENUM
MG/KG
0 19
U
08
U
02
U
08
U
02
U
0 8
U
1 U
0 19 U
NICKEL
MG/KG
0.38
U
1.6
U
0 39
U
1 6
U
04
U
2.7
25 U
0.38 U
LEAD
MG/KG
0 76
U
0.1
U
0 78
U
0 1
U
08
U
0 42
U
0 1 U
0 76 U
ANTIMONY
MG/KG
0 57
U
0 1
U
0 59
U
0.1
U
0.6
U
0.1
U
0.1 U
0.57 U
SELENIUM
MG/KG
0 95
UJ
0 14
0 52
J
0.14
0.58
J
0.1
0.1
0.48 J
TIN
MG/KG
0.65
U
2
U
0 75
U
2
U
0.7
U
2
U
2 5 U
0.65 U
STRONTIUM
MG/KG
63
56
67
46
44
63
72
71
TELLURIUM
MG/KG
0.95
U
4
U
098
U
4
U
1
U
4
U
5 U
0 95 U
TITANIUM
MG/KG
3
0.95
U
1
U
08
U
1
U
0.8
U
1 U
0.95 U
THALLIUM
MG/KG
005
U
0.04
U
0.05
U
0.04
U
0.05
U
004
U
0.04 U
0.05 U
VANADIUM
MG/KG
0 79
0.8
U
0.82
0.8
U
0 31
0.8
U
1 U
0.38
YTTRIUM
MG/KG
0.19
U
0.8
U
02
U
0.8
U
0.2
U
0.8
u
1 U
0.19 U
ZINC
MG/KG
37
32
32
31
32
42
32
30
TOTAL MERCURY MG/KG
0.02
U
0.02
U
0.022
0.02 U
ALUMINUM
MG/KG
260
90
84
15
15
31
82
24
MANGANESE
MG/KG
7.4
10
10
4.9
3.8
84
29
88
CALCIUM
MG/KG
12000
11000
11000
12000
12000
12000
14000
12000
MAGNESIUM
MG/KG
480
470
480
460
460
470
460
480
IRON
MG/KG
160
63
54
17
18
26
81
24
SODIUM
MG/KG
1400
1500
1600
1500
1600
1400
1400
1400
POTASSIUM
MG/KG
3000
2900
3100
2700
2900
3200
2900
3000
-------
>
"O
•o
n>
3
a
K
x
w
-------
e-1 Extractabie Organic Compounds in Consumer Fish
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
ZONE A
ZONEB
ZONE C
ZONED
BIS(2-CHL0R0ETHYl) ETHER
MG/KG
64
U
62
U
6 8
U
64 U
HEXACHLOROETHANE
MG/KG
64
U
62
U
68
U
64 U
BIS(2-CHLOROISOPROPYL) ETHER
MG/KG
64
U
62
u
68
U
6 4 U
N-NITROSODI-N-PROPYLAMINE
MG/KG
64
U
6.2
u
68
U
64 U
NITROBENZENE
MG/KG
64
U
6.2
u
68
U
64 U
H EXACHLOROBUTADIENE
MG/KG
64
U
6.2
u
68
U
64 U
2-METHYLNAPHTHALENE
MG/KG
64
U
6 2
u
68
U
6.4 U
1,2,4-TRICHLOROBENZENE
MG/KG
64
U
62
u
68
U
64 U
NAPHTHALENE
MG/KG
64
U
62
u
68
U
6.4 U
4-CHLOROANILINE
MG/KG
6.4
U
62
u
6.8
U
6.4 U
BIS(2-CHLOROETHOXY)METHANE
MG/KG
64
U
6.2
u
6.8
U
6.4 U
ISOPHORONE
MG/KG
64
U
6.2
u
68
U
6.4 U
HEXACHLOROCYCLOPENTADIENE (HCCP)
MG/KG
64
U
6.2
u
6.8
U
6 4 U
2-CHLORONAPHTHALENE
MG/KG
6.4
U
6.2
u
68
U
6.4 U
2-NITROANILINE
MG/KG
64
U
6.2
u
68
U
6.4 U
ACENAPHTHYLENE
MG/KG
6.4
U
6.2
u
6.8
U
6.4 U
ACENAPHTHENE
MG/KG
6.4
U
6.2
u
68
U
6.4 U
DIMETHYL PHTHALATE
MG/KG
64
U
6.2
u
6.8
U
6.4 U
DIBENZOFURAN
MG/KG
64
U
6.2
u
6.8
U
6.4 U
2,4-DINITROTOLUENE
MG/KG
64
U
6.2
u
6.8
U
6.4 U
2,6-DINITROTOLUENE
MG/KG
6.4
U
62
u
68
U
6.4 U
3-NITROANILINE
MG/KG
6.4
U
6.2
u
68
U
6.4 U
4-CHLOROPHENYL PHENYL ETHER
MG/KG
64
U
6.2
u
68
U
6.4 U
4-NITROANILINE
MG/KG
64
U
62
u
6.8
U
6 4 U
FLUORENE
MG/KG
6.4
U
6.2
u
6.8
u
6.4 U
DIETHYL PHTHALATE
MG/KG
64
U
62
u
6.8
u
6 4 U
N-NITROSODIPHENYLAMINE/DIPHENYLAMIN
MG/KG
64
U
6.2
u
6 8
u
6 4 U
HEXACHLOROBENZENE (HCB)
MG/KG
6.4
u
62
u
68
u
6 4 U
4-BROMOPHENYL PHENYL ETHER
MG/KG
64
u
62
u
6.8
u
6 4 U
PHENANTHRENE
MG/KG
64
u
62
u
6.8
u
6 4 U
ANTHRACENE
MG/KG
64
u
62
u
68
u
6 4 U
DI-N-BUTYLPHTHALATE
MG/KG
6.4
u
62
u
68
u
64 U
FLUORANTHENE
MG/KG
6.4
u
62
u
6.8
u
6 4 U
-------
E-1 (cont). Extractable Organic Compounds in Consumer Fish.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
PYRENE
BENZYL BUTYL PHTHALATE
BIS(2-ETHYLHEXYL) PHTHALATE
BENZO(A)ANTHRACENE
CHRYSENE
3,3'-DICHLOROBENZIDINE
DI-N-OCTYLPHTHALATE
BENZO(B AND/OR K)FLUORANTHENE
BENZO-A-PYRENE
tNDENO (1.2.3-CD) PYRENE
DIBENZO(A,H)ANTHRACENE
BENZO(GHI)PERYLENE
2-CHLOROPHENOL
2-METHYLPHENOL
(3-AND/OR 4-)METHYLPHENOl
2-NITROPHENOL
PHENOL
2,4-DIMETHYLPHENOL
2,4-DICHLOROPHENOL
2,4,6-TRICHLOROPHENOL
2,4,5-TRICHLOROPHENOL
4-CHLORO-3-METHYLPHENOL
2,4-DINITROPHENOL
2-METHYL-4,6-D>N»TROPHENOL
PENTACHLOROPHENOL
4-NITROPHENOL
2,3,4,6-TETRACHLOROPHENOL
CARBAZOLE
Units
ZONE A
ZONEB
ZONE C
ZONED
MG/KG
64
U
62
U
68
U
6.4 U
MG/KG
64
U
62
U
6.8
U
6.4 U
MG/KG
64
U
62
U
68
U
6 4 U
MG/KG
64
U
62
U
68
U
6.4 U
MG/KG
6.4
U
6 2
U
68
U
6 4 U
MG/KG
6.4
U
6.2
U
68
U
6.4 U
MG/KG
6.4
U
62
U
68
U
64 U
MG/KG
6.4
U
62
U
6.8
U
6 4 U
MG/KG
6.4
U
6 2
U
6.8
U
64 U
MG/KG
6.4
U
6.2
U
68
U
6.4 U
MG/KG
64
U
6.2
U
68
U
6 4 U
MG/KG
6.4
U
6.2
U
68
U
6 4 U
MG/KG
64
U
62
U
6.8
U
6 4 U
MG/KG
6.4
U
6 2
U
68
U
6.4 U
MG/KG
6.4
U
6.2
U
68
U
6 4 U
MG/KG
64
U
62
U
6.8
U
64 U
MG/KG
64
U
6.2
U
68
U
6 4 U
MG/KG
64
U
62
U
6.8
U
64 U
MG/KG
64
U
6.2
U
68
U
64 U
MG/KG
64
U
62
U
68
U
64 U
MG/KG
64
U
6 2
U
68
U
64 U
MG/KG
64
u
6.2
U
68
U
6.4 U
MG/KG
13
u
12
U
14
U
13 U
MG/KG
13
u
12
U
14
U
13 U
MG/KG
13
u
12
U
14
U
13 U
MG/KG
13
u
12
U
14
u
13 U
MG/KG
64
u
62
u
68
u
64 U
MG/KG
64
u
62
u
68
u
6.4 U
-------
e-1 (cont). Miscellaneous Extractable Organic Compounds in Consumer Fish.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte
Units
ZONE A
ZONEB
ZONE C
ZONE D
1 UNIDENTIFIED COMPOUND
MG/KG
20 J
30 J
2 UNIDENTIFIED COMPOUNDS
MG/KG
40 J
60 J
3 UNIDENTIFIED COMPOUNDS
MG/KG
4 UNIDENTIFIED COMPOUNDS
MG/KG
5 UNIDENTIFIED COMPOUNDS
MG/KG
HEPTADECANOIC ACID
MG/KG
HEXADECANOIC ACID
MG/KG
100 JN
60 JN
100 JN
90 JN
HEXADECANOIC ACID, METHYL ESTER-
MG/KG
HEXADECANOIC ACID,METHYL ESTER-
MG/KG
HEXADECENOIC ACID
MG/KG
80 JN
40 JN
100 JN
70 JN
HEXADECENOIC ACID, METHYL ESTER-
MG/KG
NIACINAMIDE
MG/KG
7 JN
OCTADECANOIC ACID
MG/KG
20 JN
20 JN
9 JN
OLEIC ACID
MG/KG
100 JN
20 JN
60 JN
50 JN
PENTADECANOIC ACID
MG/KG
TETRADECANOIC ACID
MG/KG
-------
E-2. Pesticides / PCB's In Consumer Fish.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte Units ZONE A ZONE B ZONE C ZONE D
PCB-1268 (AROCLOR 1268 MG/KG 0 18 U 0.18 U 02 U 0.35 U
TOXAPHENE MG/KG 1 6 JN 1 7 JN 2 6 JN 3 9 JN
-------
E-3. Metals in Consumer Fish.
Terry Creek, Brunswick, Georgia. 1997.
Station
Analyte Units ZONE A ZONE B ZONE C ZONE D
SILVER
MG/KG
02
U
02
U
02
U
0 2 U
ARSENIC
MG/KG
0 33
0 34
0.57
0 29
BARIUM
MG/KG
0 2
U
0.2
U
02
U
0.2 U
BERYLLIUM
MG/KG
0.1
U
0 1
U
0.1
U
0 099 U
CADMIUM
MG/KG
0 1
U
0.1
U
0 1
U
0 099 U
COBALT
MG/KG
02
U
02
U
0.2
U
0.2 U
CHROMIUM
MG/KG
0 2
U
02
U
0.2
U
02 U
COPPER
MG/KG
0 26
0 21
0 22
0.22
MOLYBDENUM
MG/KG
02
U
02
U
0.2
U
02 U
NICKEL
MG/KG
0.4
U
0.4
U
0.4
U
0.4 U
LEAD
MG/KG
0.8
U
0.8
U
08
U
0.8 U
ANTIMONY
MG/KG
0.6
U
06
U
06
U
06 U
SELENIUM
MG/KG
0 41
J
0 38
J
0.47
J
0.47 J
TIN
MG/KG
0 65
U
0 7
U
0 65
U
0 75 U
STRONTIUM
MG/KG
0.46
0.75
0.5
08
TELLURIUM
MG/KG
1
U
1
U
1
U
0 99 U
TITANIUM
MG/KG
0.2
U
0.2
U
0.2
U
0 2 U
THALLIUM
MG/KG
0 05
U
0 05
U
0 05
U
0.05 U
VANADIUM
MG/KG
02
U
02
U
0.2
U
0 2 U
YTTRIUM
MG/KG
02
U
02
U
0.2
U
0 2 U
ZINC
MG/KG
65
7 3
6.7
7.2
ALUMINUM
MG/KG
2
U
2
U
2
U
2 U
MANGANESE
MG/KG
02
U
02
U
02
U
0 2 U
CALCIUM
MG/KG
150
220
160
250
MAGNESIUM
MG/KG
290
300
290
300
IRON
MG/KG
2 8
34
2
2.7
SODIUM
MG/KG
430
400
370
410
POTASSIUM
MG/KG
4300
4500
4300
4300
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