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EPA NATIONAL STUDY OF 

CHEMICAL RESIDUES 

United States 

Environmental Protection 

Agency 

Water 

Office of Science and 

Technology (WH-551) 

Washington. D.C. 20460 

EPA 823-R-92-008b 

September 1992 

IN FISH 

Volume II 
EPA 823-R-92-008b 

September 1992 

National Study of 

Chemical Residues 

in Fish 

Volume II 

Office of Science and Technology 

Standards and Applied Science Division 

U.S. Environmental Protection Agency 

401 M Street, SW 

Washington, DC 20460 
Note 

This is the third printing (September 1993) of the National Study of Chemical Residues in Fish. 

All revisions listed on the errata sheet from the first printing have been incorporated into the 

text of Volumes I and II where appropriate. 
Table of Contents 

Chapter Page 

VOLUME I 

1 

1 

1 

3 

4 

LIST OF FIGURES 

LIST OF TABLES 

ACKNOWLEDGMENTS 

EXECUTIVE SUMMARY xv 

INTRODUCTION 

BACKGROUND 

GENERAL, APPROACH 

STUDY DESIGN AND APPROACH 3 

POLLUTANT SELECTION SCREENING PROCESS 3 

FIELD SAMPLING PROCEDURES 4 

Sample Collection 4 

Sample Handling/preparation 6 

Fish Length and Weight Data 6 

ANALYTICAL PROTOCOLS 6 

Dioxins/Furans 7 

other Xenobiotic chemicals 10 

Mercury 12 

Quality Assurance/Quality Control (QA/QC) 12 

SITE SELECTION 15 

DIOXIN AND FURAN RESULTS AND ANALYSTS 21 

PREVALENCE AND CONCENTRATION SUMMARY 21 

Toxicity Equivalency Concentration (TEC) 24 

Comparison of TCDD and other Dioxin/Furan Compounds 30 

GEOGRAPHICAL DISTRIBUTION 30 

SOURCE CORRELATION ANALYSIS 30 

Sources Located Near Highest Concentrations 30 

Concentration Comparison Between Site Categories 39 

OTHER XENOBIOTIC COMPOUND RESULTS AND ANALYSIS 53 

PREVALENCE AND CONCENTRATION SUMMARY 53 

COMPOUNDS DETECTED AT MORE THAN 50 PERCENT OF THE SITES 57 

Total PCBs 57 

Biphenyl 60 

Mercury 64 

Pantachloroanisole 67 

1, 2, 3 and 1, 2, 4 Trichlorobenzene 70 

Pesticides/Herbicides 73 

vii 

xi 

xiii 

1 

2 

iii 
Table of Contents (Cont.) 

Chapter Page 

COMPOUNDS DETECTED AT BETWEEN 10 AND 50 PERCENT OF THE SITES 91 

Hexachlorobenzene 

Pentachlorobenzene 

1,3,5 Trichlorobenzene 

Tetachorobenzenes 

Pesticides/Herbicides 

COMPOUNDS DETECTED AT LESS THAN 10 PERCENT OF THE SITES 

Octachlorostyrene 

Hexachlorobutadiene 

Diphenyl Disulfide 

Pesticides/Herbicides 

COMPARISON WITH NATIONAL CONTAMINANT BIOMONITORING 

PROGRAM 

91 

96 

100 

100 

107 

122 

122 

122 

122 

125 

5 FISH SPECIES SUMMARY AND ANALYSIS 

SUMMARY OF FISH SPECIES SAMPLED 

PREVALENCE AND AVERAGE CONCENTRATION OF CHEMICALS 

BY SPECIES 

HABITAT AND FEEDING STRATEGY OF MOST FREQUENTLY 

SAMPLED SPECIES 

129 

131 

131 

137 

137 

6 ESTIMATE OF POTENTIAL HUMAN HEALTH RISKS 

METHOD OF ESTIMATING RISKS 

Dose-Response Assessment 

Exposure Assessment 

Risk Characterization 

CARCINOGENIC RISK ESTIMATES 

NONCARCINOGENIC RISKS 

147 

148 

148 

148 

150 

151 

156 

REFERENCES 161 

GLOSSARY 165 

APPENDICES 

A LABORATORY QA/QC PROCEDURES AND RESULTS 

A-1 Analysis of Laboratory QA/QC Data 

A-2 Analytical Procedures and Quality Assurance Plan for the Determination of 

PCDD/PDCF in Fish 

A-3 Analytical Procedures and Quality Assurance Plan for the Determination 

of Xenobiotic chemical Contaminants in Fish 

B ADDITIONAL DATA ANALYSES 

B-1 

B-2 

Nomographs for Estimating Cancer Risks 

Nomographs for Estimating Noncarcinogenic Hazard Indices 

B-3 Site Description Matrix (also provided in Volume II, Appendix D) 

B-4 Dioxins/Furans: Episode Numbers Used in Statistical Tests (also provided 

B-5 

in Volume II, Appendix D) 

Xenobiotics: Episode Numbers Used in Statistical Tests (also provided in 

Volume II, Appendix D) 

iv 
Table of Contents (Cont.) 

VOLUME II 

C PROFILES OF BIOACCUMULATION STUDY CHEMICALS 

Dioxins/Furans: 

Dioxin: 2,3,7,8 Tetrachlorodibenzo-p-dioxin 

1,2,3,7,8 Pentachlorodibenzodioxin 

Hexachlorodibenzodioxin 

Furans 

Other Xenobiotics: 

Biphenyl 

Chlordane 

Chlorpyrifos 

p,p’-DDE 

Dicofol 

Dieldrin 

Diphenyl Dusulfide 

Endrin 

Heptachlor 

Heptachlor Epoxide 

Hexachlorobenzene 

Alpha-BHC ( a - Hexachlorocyclohexane) 

Isopropalin 

Gamma-BHC ( g -Hexachlorocyclohexane) 

Mercury 

Methoxychlor 

Mirex 

Nitrofen 

Nonachlor 

Octachlorostyrene 

Oxychlordane 

Pentachloroanisole 

pentachlorobenzene 

Pentachloronitrobenzene 

Pentrachlorophenol 

Perthane 

Polychlorinated Biphenyls (PCBs) 

1,2,3,4 and 1,2,3,5 Tetrachlorobenzene 

1,2,4,5 Tetrachlorobenzene 

1,2.3 Trichlorobenzene 

1,2,4 Trichlorobenzene 

1,3,5 Trichlorobenzene 

Triflralin 

v 
Table of Contents (Cont.) 

VOLUME II (Cont) 

D DATA TABLES 

D-1 

D-2 

D-3 

D4 

D-5 

D-6 

D-7 

D-8 

D-9 

D-10 

Site Description Matrix (also provided in Volume L Appendix B) 

Dioxins/Furans: Episode Numbers Used in Statistical Tests (also provided 

in Volume I, Appendix B) 

Xenobiotics: Episode Numbers Used in Statistical Tests (also provided 

in Volume I. Appendix B) 

Dioxin/Furan Data by Episode Number 

Concentration And Detection Limits 

Xenobiotic Data by Episode Number 

Set 1 Chemicals 

Set 2 Chemicals 

Set 3 Chemicals 

Information on Fish Samples 

- Percent Lipid 

- Sample Wet Weight 

- Number of Fish in Composite Sample 

- Sampling Date 

List of confirmation Samples 

List of Duplicate Samples 

Comments Regarding Sample Analyses from EPA Duluth Laboratory 

Risk Information for Sites Having Composite Fillet Samples with Xenobiotic Data 

vi 
List of Figures 

Figure Page 

2-1 

2-2 

2-3 

24 

2-5 

2-6 

2-7 

3-1 

3-2 

3-3 

3-4 

3-5 

3-6 

3-7 

3-8 

3-9 

3-10 

3-11 

3-12 

3-13 

3-14 

3-15 

3-16 

3-17 

4-1 

4-2 

4-3 

4-4 

4-5 

4-6 

4-7 

Schematic of laboratory procedures for dioxins and furans 

Schematic of laboratory analytical procedure for other xenobiotic chemicals 

Schematic of laboratory analytical procedure for mercury 

Location of bioaccumulation study sampling sites 

Location of targeted sites 

Location of sites representing background conditions 

Location of sites selected from a subset of the USGS NASQAN network 

Summary of dioxin/furans detected in fish tissue 

Cumulative frequency diagrams of concentrations of six dioxin congeners in fish tissue 

Cumulative frequency diagrams of concentrations of six furan congeners in fish tissue 

Cumulative frequency distribution of maximum calculated TEC values in fish tissue by 

percentile of sites 

Toxicity equivalency concentrations (TEC) based on Barnes et al., 1989 method 

Map showing geographical distribution of various concentration ranges of 

2,3,7,8 TCDD in fish tissue 

Map showing geographical distribution of various concentration ranges of 

2,3,7,8 TCDF in fish tissue 

Map showing geographical distribution of various concentration ranges of TEC 

in fish tissue 

Example box plot with explanations of features 

Box and whisker plot for 2,3,7,8 TCDD concentrations in fish tissue 

Box and whisker plot for TEC concentrations in fish tissue 

Box and whisker plot for 2,3,7,8 TCDF concentrations in fish tissue 

Box and whisker plot for 1,2,3,7,8 PeCDD concentrations in fish tissue 

Box and whisker plot for 1,2,3,7,8 PeCDF concentrations in fish tissue 

Box and whisker plot for 2,3,4,7,8 PeCDF concentrations in fish tissue 

Box and whisker plot for total HxCDDs concentrations in fish tissue 

Box and whisker plot for total HxCDFs concentrations in fish tissue 

Summary of other xenobiotic compounds detected in fish tissue 

Total PCBs: a) cumulative frequency distribution and b) map of geographical distribution 

of various concentration ranges in fish tissue 

Box and whisker plot for total PCBs in fish tissue 

Biphenyl: a) cumulative frequency distribution and b) map of geographical distribution of 

various concentration ranges in fish tissue 

Box and whisker plot for biphenyl in fish tissue 

Mercury: a) cumulative frequency distribution and b) map of geographical distribution of 

various concentration ranges in fish tissue 

Box and whisker plot for mercury in fish tissue 

8 

11 

13 

16 

17 

18 

19 

23 

25 

26 

28 

29 

31 

32 

33 

41 

42 

45 

46 

47 

48 

49 

50 

51 

55 

58 

61 

63 

65 

66 

68 

vii 
List of Figures (Cont.) 

Figure Page 

4-8 

4-9 

4-10 

Pentachloroanisole: a) cumulative frequency distribution and b) map of geographical 

distribution of various concentration ranges in fish tissue 

Box and whisker plot for pentachloroanisole in fish tissue 

Cumulative frequency distribution of a) 1,2,3 trichlorobenzene and b) 1,2,4 trichlorobenzene in fish tissue 

4-11 

4-12 

4-13 

4-14 

4-15 

4-16 

Map of geographical distribution of various concentration ranges for a) 1,2,3 trichlorobenzene and b) 1,2,4 trichlorobenzene in fish tissue 

Box and whisker plot for 1,2,3 trichlorobenzene in fish tissue 

Box and whisker plot for 1,2,4 trichlorobenzene in fish tissue 

p,p’ -DDE: a) cumulative frequency distribution and b) map of geographical distribution of 

various concentration ranges in fish tissue 

Box and whisker plot for p,p’ -DDE in fish tissue 

Cumulative frequency distribution of a) total chlordane, b) cis-chlordane, c) trans-chlordane, 

and d) oxychlordane in fish tissue 

4-17 Cumulative frequency distribution of a) trans-nonachlor b) cis-nonachlor and c) total 

nonachlor in fish tissue 

4-18 Map of geographical distribution of various concentration ranges for a) total chlordane 

and b) total nonachlor in fish tissue 

4-19 

4-20 

4-21 

4-22 

4-23 

4-24 

Box and whisker plot for total chIordane in fish tissue 

Box and whisker plot for total nonachlor in fish tissue 

Box and whisker plot for oxychlordane in fish tissue 

Dieldrin: a) cumulative frequency distribution and b) map of geographical distribution of 

various concentrations in fish tissue 

Box and whisker plot for dieldrin in fish tissue 

Cumulative frequency distribution of a) alpha-BHC and b) gamma-BHC (lindane) 

in fish tissue 

4-25 

4-26 

4-27 

4-28 

4-29 

4-30 

Box and whisker plot for alpha-BHC in fish tissue 

Box and whisker plot for gamma-BHC in fish tissue 

Map of geographical distribution of various concentration ranges for a) gamma-BHC 

(lindane) and b) alpha-BHC in fish tissue 

Hexachlorobenzene: a) map of geographical distribution of various concentration ranges 

and b) cumulative frequency distribution in fish tissue 

Box and whisker plot for hexachlorobenzene in fish tissue 

Pentachlorobenzene: a) map of geographical distribution of various concentration ranges and 

b) cumulative frequency distribution in fish tissue. c) Cumulative frequency distribution of 

1,3,5 trichlorobenzene in fish tissue 

4-31 Box and whisker plot for pentachlorobenzene in fish tissue 

4-32 Box and whisker plot for 1,3,5 trichlorobenzene in fish tissue 

69 

71 

72 

74 

75 

76 

77 

79 

81 

82 

83 

85 

87 

88 

89 

90 

92 

93 

94 

95 

97 

98 

99 

101 

102 

viii 
List of Figures (Cont.) 

Figure Page 

4-33 

4-34 

4-35 

4-36 

4-37 

4-38 

4-39 

4-40 

4-41 

4-42 

4-43 

4-44 

4-45 

4-46 

4-47 

4-48 

4-49 

4-50 

4-51 

4-52 

4-53 

6-1 

6-2 

Cumulative frequency distribution of a) 1,2,3,4 tetrachlorobenzene, 

b) 1,2,3,5 tetrachlorobenzene, and c) 1,2,4,5 tetrachlorobenzene in fish tissue 

Map of geographical distribution of various concentration ranges for 

a) 1,2,3,4 tetrachlorobenzene, b) 1,2,3,5 tetrachlorobenzene, and c) 1,2,4,5 tetrachlorobenzene 

in fish tissue 

Box and whisker plot for 1,2,3,4 tetrachlorobenzene in fish tissue 

Cumulative frequency distribution of a) mirex and b) chlorpyrifos in fish tissue 

Box and whisker plot for mirex in fish tissue 

Map of geographical distribution of various concentration ranges for chlorpyrifos in 

fish tissue 

Box and whisker plot for chlorpyrifos in fish tissue 

Cumulative frequency distribution of a) dicofol (kelthane), b) methoxychlor, and c) perthane 

in fish tissue 

Map of geographical distribution of various concentration ranges for 

a) dicofol and b) methoxychlor in fish tissue 

Box and whisker plot for dicofol in fish tissue 

Cumulative frequency distribution of a) trifluralin and b) isopropalin in fish tissue 

Map of geographical distribution of various concentration ranges for a) trifluralin and 

b) isopropalin in fish tissue 

Box and whisker plot for trifluralin in fish tissue 

Box and whisker plot for isopropalin in fish tissue 

Endrin: a) cumulative frequency distribution and b) map of geographical distribution of 

various concentration ranges in fish tissue 

Box and whisker plot for endrin in fish tissue 

Cumulative frequency distribution of a) octachlorostyrene, b) hexachlorobutadiene, 

c) diphenyl disulfide, and d) nitrofen in fish tissue 

Cumulative frequency distribution of a) heptachlor and b) heptachlor epoxide in fish tissue 

Map of geographical distribution of various concentration ranges for a) heptachlor and 

b) heptachlor epoxide in fish tissue 

Box and whir plot for heptachlor epoxide in fish tissue 

Pentachloronitrobenzene: a) cumulative frequency distribution and b) map of geographical 

distribution of various concentration ranges in fish tissue 

Graphical tool for estimating upper-bound cancer risk of p.p’-DDE or equivalents for 

different fish consumption rates 

Graphical tool for estimating upper-bound noncarcinogenic hazard index of p,p’-DDE 

for different fish consumption rate-s 

103 

105 

106 

108 

109 

110 

112 

113 

114 

115 

117 

118 

119 

120 

121 

123 

124 

126 

127 

128 

130 

158 

160 

ix 
x
List of Tables 

Table Page 

2-1 

2-2 

3-1 

3-2 

3-3 

3-4 

3-5 

3-1 

4-2 

4-3 

4-4 

4-5 

5-1 

5-2 

5-3 

5-4 

5-5 

6-1 

6-2 

6-3 

6-4 

6-5 

6-6 

6-7 

List of Target Analytes 

Internal Standard Solutions Used for PCDD/PCDF Analyses and Xenobiotic Analyses 

Summary of Dioxins/Furans Detected in Fish Tissue 

1989 Toxicity Equivalency Factors 

Location of Maximum Measured HxCDD and HpCDD Concentrations in Fish Tissue 

Location of Maximum Measured HxCDF and HpCDF Concentrations in Fish Tissue 

Mann-Whitney U Test Results for Dioxins/Furans Comparing Selected Source Categories 

Summary of Xenobiotic Compounds in Fish Tissue 

Summary of PCBs in Fish Tissue 

Results of Statistical Tests for Selected Xenobiotics and Mercury 

Results of Statistical Tests for Selected Xenobiotics (Pesticides/Herbicides) 

Sites with Highest Concentrations of Chlordane-Related Compounds 

Distribution and Feeding Strategy for Fish Species Collected 

Average Fish Tissue Concentrations of Dioxins and Furans for Major Species 

Detailed Summary of Occurrence of Prevalent Dioxins/Furans by Fish Species 

Average Fish Tissue Concentrations of Xenobiotics for Major Species 

Detailed Summary of Occurrence of Prevalent Xenobiotics by Fish Species 

Dose-Response Variables Used in Risk Assessment 

Estimates of Potential Upper-Bound Cancer Risks at Targeted Sites Based on Fillet 

Samples 

Estimates of Potential Upper-Bound Cancer Risks at Background Sites Based on Fillet 

Samples 

Fish Tissue Concentrations Used to Estimate Cancer Risks 

Number of Sites with Estimated Upper-Bound Risks 

Estimated Upper-Bound Risks at Three Fish Consumption Rates Based on Fillet 

Samples 

Noncarcinogenic Hazard Index Values at Targeted and Background Sites Based on 

Fillet Samples 

5 

9 

22 

27 

37 

38 

43 

54 

59 

62 

80 

84 

132 

138 

139 

140 

141 

149 

152 

153 

154 

155 

157 

159 

xi 
xii 
APPENDIX C 

PROFILES OF BIOACCUMULATION STUDY 

CHEMICALS 

Dioxins/Furans 

Dioxin: 2,3,7,8 Tetrachlorodibenzo-p-dioxin 

1,2,3,7,8 Pentachlorodibenzodioxin 

Hexachlorodibenzodioxins 

Furans 

Other Xenobiotics 

Biphenyl 

Chlordane 

Chlorpyrifos 

p,p’-DDE 

Dicofol 

Dieldrin 

Diphenyl Disulfide 

Endrin 

Heptachlor 

Heptachlor Epoxide 

Hexachlorobenzene 

a -Hexachlorocyclohexane 

Isopropalin 

Other Xenobiotics (cont.) 

Lindane 

Mercury 

Methoxychlor 

Mirex 

Nitrofen 

Nonachlor 

Octachlorostyrene 

Oxychlordane 

Pentachloroanisole 

Pentachlorobenzene 

Pentachloronitrobenzene 

Pentachlorophenol 

Perthane 

Polychlorinated Biphenyls (PCBs) 

1,2,3,4 and 1,2,3,5 Tetrachlorobenzene 

1,2,4,5 Tetrachlorobenzene 

1,2,3 Trichlorobenzene 

1,2,4 Trichlorobenzene 

1,3,5 Trichlorobenzene 

Trifluralin 
DIOXIN: 2,3,7,8 TCDD 

CAS No.: 1746-01-6 

CAS Preferred Nomenclature: 

Dibenzo[b,e][1,4]dioxin,2,3,7,8-tetrachloroEmpirical Formula: C12H4Cl4O2 

Synonyms and Common Names: 

- 23.7.8 Tetrachlorodibenzo-p-dioxin 

- TCDD or TDD 

REGULATORY STATUS 

Standards and Criteria: 

• EPA Water Quality Criteria (for human • 

consumption of fish) for a 10-6 cancer 

EPA Drinking Water Health Advisories (U.S. EPA, 1988) 

risk (ATSDR, 1987): child (10 kg): 

0.000014 ng/L l-day exposure = 1 ng/L 

10-day exposure = 0.1 ng/L 

longer-term exposure = 0.01 ng/L 

adult (70 kg): 

longer-term exposure = 0.04 ng/L 

• EPA Ambient Water Quality Criteria • Food and Drug Administration Health 

(for protection of aquatic organisms): Advisory for Fish* (U.S. EPA, 1987c): 

None established at present <25 parts per trillion (ppt), no serious 

health concerns 

25-50 ppt, restrict consumption to 

twice per month 

>50 ppt. consumption not recommended 

* Guidance developed for fish caught in 

the Great Lakes for use in interstate 

commerce only. 

C-1 
• EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

• Center for Disease Control Level of 

Concern in Soil for residential areas 

(U.S. EPA, 198%): 

1 ppb 

• EPA has required manufacturers to reduce concentrations of TCDD in chemical 

products; most chemicals now have less than 0.02μg/g (ATSDR, 1987). Some 

compounds such as 2.45 T are no longer produced in the U.S. 

SOURCES OF DIOXIN 

Dioxin Formation: 

• TCDD is one of 75 types of dioxin formed as unwanted impurities during the manufacture of other organic compounds including herbicides containing 2,4,5 trichlorophenoxy 

acids (2,4,5 T); 2,4,5 trichlorophenol used in the defoliant Agent Orange; 

hexachlorophene formerly used as a germicide; pentachlorophenol; and PCBs. Other 

dioxins which have been studied include 1,2,3,7,8 PeCDD and two of the HxCDDs 

(1,2,3,6,7,8 and 1,2,3,7,8,9 HxCDD). TCDD is the most toxic and most studied of all 

the isomers. 

• Dioxin can be generated as a by-product of paper and pulp mill bleaching processes 

which use chlorine. It can then be released to aquatic systems in various wastewater 

streams and sludges generated by these industries (U.S. EPA, 1988; NCASI, 1987). 

Uses of Dioxin: 

• No commercial production or importation of dioxin in the U.S., but small quantities are 

produced for research purposes (NTIS, 1980; ATSDR, 1987). 

Other Sources: 

• Examples of levels of dioxin found in other organic compounds are listed below 

(ATSDR), 1987): 

- Until 1960, 2,4,5 T had up to 100 μg/g TCDD, now <0.1 μg/g 

- Agent Orange had 0.02 to 54 μg/g 

- Hexachlorophene had 0.2 to 0.5 μg/g 

- Pentachlorophenol has <0.1 μg/g of other dioxin isomers but no TCDD 

- Polychlorinated Biphenyls (PCBs) also contain TCDD. Oil containing PCBs was 

formerly used in electrical transformers. Utilities are gradually replacing these old 

transformers. 

C-2 
Incineration of municipal and industrial wastes at too low a temperature (c800°C) can 

produce dioxin. (Verschueren, 1983; ATSDR, 1987; U.S. EPA, 1987b). 

Derivatives of pentachlorophenol and other woodtreating wastes (NCASI, 1987; U.S. 

EPA, 1987b). 

Currently, EPA is investigating possible correlations between dioxin and nearby 

petroleum refineries that use chlorine or chlorinated solvents in the catalytic reforming 

process. 

Other sources of dioxin include fms and/or spills involving chlorinated benzenes and 

PCBs, particularly fues involving transformers or capacitors, burning of wood in 

presence of chlorine, and automobile exhaust from leaded gasoline (ATSDR, 1987). 

FATE OF DIOXIN IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, dioxin is only slightly soluble in water (Aq. 

sol. = 0.000317) and strongly sorbs to soil (&w = 10,500,000). It has a high potential 

for bioaccumulation (BCF = 5,000), although experimental data have shown much 

higher values (e.g., over 9,000). 

Persistence: 

l Because dioxin strongly sorbs to sediment, it persists in soils and aquatic systems. 

Photolysis can occur, aided by photosensitizers in surface water (haif-life 1 to 1.5 years) 

or in the top few inches of soil (half-life 1 to 3 years) (U.S. EPA, 1985b and Freeman, 

et al., 1986). Hydrolysis is not thought to be important (Callahan, et al., 1979). 

Biotransformation of dioxin in soils is slow (ATSDR, 1987). 

HEALTH EFFECTS 

Cardnogenidty: 

l Oral exposure causes increased incidence of tumors in liver, tongue, hard palate, and 

lungs in rats (Kociba et al., 1978a,b) and in thyroid and adrenal glands in mice (NTP, 

1982ab). EPA classification is B2, a probable human carcinogen (IRIS, 1989). IARC 

classification 2b (IARC, 1982). 

l In combination with herbicides such as trichlorophenols, dioxin is classified by the EPA 

as Bl, limited evidence of human carcinogenicity (IRIS, 1989). 

c-3 
Mutagenic Activity: 

l Mutagenicity tests have produced inconclusive results. Bacterial tests were negative as 

were most tests using rats and mice except when bone marrow cells were used (Green 

et al., 1977; Meyne et al., 1985). Early tests using yeast cells showed positive results 

(IARC, 1982). 

Reproductive Effects: 

. Adverse reproductive effects are caused in a variety of animals: 

- fetotoxic in monkeys (U.S. EPA, 1985b) 

- embryotoxic and teratogenic in mice, rabbits, ferrets and rats (IARC, 1977; U.S. 

EPA, 1985b) 

- reduced fertility and spontaneous abortions in monkeys (ATSDR, 1987) 

- birth defects in mice (e.g., cleft palates and kidney abnormalities) (U.S. EPA, 

1985b) 

Other ToxicoIogical Effects: 

l Major observed toxic effect on humans is chloracne (U.S. EPA, 1985b). 

. Human exposure through herbicides and other TCDDcontaminated chemicals can also 

cause altered liver function, porphyria, neurotoxicity, and hyperpigmentation (U.S. 

EPA, 1985b). 

l Toxic effects to acutely exposed animals include extreme weight loss, liver and thymus 

damage, immunotoxicity, and hepatotoxicity (IARC, 1977; U.S. EPA, 1985a). 

Toxicological Effects Indices: 

l Cancer potency factor (CPF): 1.56~10~ (mg/kg/day)-’ (U.S. EPA, 1986a). 

l Reference Dose (RfD): 1~10’~ l.@kg/day (ATSDR. 1987). 

l Oral LD50: 0.6 pg/kg in guinea pigs ; 5,500 @kg in hamsters (U.S. EPA 1985b). 

c-4 
PHYSICA L/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight (g/mole): 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Density (g/mL): 

Acid Dissociation Constant, pIQ 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H @ 

25°C (atm . m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log Row: 

Soil Adsorption Coefficient, K&mWg): 

Fish Bioconcentration 

Factor, BCF: 

321.97 

solid, colorless 

needles with no 

odor 

305 

412.2 

1.827 (est.) 

N/A 

1 .93x1o-5 (22OC) 

3.17~10~ (25°C) 

1.4x lo-’ (25OC) 

2.1x1o-6 Schroy et al., 1985 

6.15-7.28 U.S. EPA, 1985a 

6.0-7.39 U.S. EPA, 1985a 

best estimate, 

5000 

7900-9300, 

fathead minnows 

Windholz, 1983 

Windholz, 1983 

Schroy et al., 1985 

Schroy et al., 1985 

Schroy et al., 1985 

Marple et al., 1986 

Schroy et al., 1985 

Schroy et al., 1985 

U.S. EPA, 1986a 

U.S. EPA, 1985b 

C-S 
ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for 2,3,7,8-Tetrachlorodibenzo-p-Dioxin. ATSDR, U.S. Public Health Service, Oak Ridge National Laboratory, Oak Ridge, TN. 

Callahan, M.A., M. W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants. U.S. Environmental Protection Agency, Office of 

Water Planning and Standards. EPA-440/4-79-029a. 

Freeman, R.A., J.M. Schroy, F.D. Hiieman, R.W. Noble. 1986. Environmental Mobility of 

2,3,7,8-TCDD and Comparison Chemicals in a Roadway Soil Matrix. In: Chlorinated Dioxins and 

Dibenzofurans in Perspective. (C. Rappe, G. Choudhary, L.H. Keith, eds.) Lewis Publishers, Inc., 

Chelsea. 

Green, S., Moreland, C. Sheu. 1977. Cytogenic Effect of 2,3,7,8-Tetrachlorodibenzo-p-dioxin on 

Rat Bone Marrow Cells. Food and Drug Administration, Washington, D.C. FDA By-Lines 6:292. 

(Cited in U.S. EPA 1985a.) 

IARC (International Agency for Research on Cancer). 1982. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 29. IARC, Geneva, World Health 

Organization. 

IRIS. 1989. 2,3.7,8,-TCDD. Integrated Risk Information System. U.S. Environmental Protection 

Agency, Washington, DC. 

Kociba, R.J., D.G. Keyes, J.E. Beyer, and R.M. Carreon. 1978a. Results of a Two-year Chronic 

Toxicity and Oncogenicity Study of 2,3,7,8-Tetrachlorodibenzo-p-dioxin in Rats. Toxicol. Appl. 

Pharmacol. 46(2):279-303. 

Kociba, R.J., D.G. Keyes, J.E. Beyer, and R.M. Carteon. 1978b. Toxicologic Studies of 2,3,7,8- 

Tetrachlorodibenzo-p-dioxin (TCDD) in Rats. Toxicol. Occup. Med. (De Toxicol. Environ. Sci.) 

4:281-287. (Cited in U.S. EPA 1985~) 

Marple, L., R. Brunck, and L. Throop. 1986. Water Solubility of 2,3,7,8-Tetrachlorodibenzo-pdioxin. Environ. Sci. Technol. 20: 180- 182. 

Meyne, J., DC. Allison, K. Bose, S.W. Jordan, P.F. Ridolpho, and J. Smith. 1985. Hepatotoxic 

Doses of Dioxin Do Not Damage Mouse Bone Marrow Chromosomes. Mutat. Res. 157:63-69. 

NCASI (National Council of the Paper Industry of Air and Stream Improvement). 1987. Dioxin: 

A Critical Review of Its Distribution, Mechanism of Action, Impacts on Human Health and the 

Setting of Acceptable Exposure Limits. Technical Bulletin No. 254. New York, NY. 
NTIS. 1980. Dioxins. Prepared for EPA Industrial Environmental Research Laboratory. Contract 

Numbers: 68-03-2577,68-03-2659,68-03-2579. 

NTP (National Toxicological Program). 1982a. Bioassay of 2,3,7,8-Tetrachloro-dibenzo-p-dioxin 

for Possible Carcinogenicity (Gavage Study). DHHS Publ. No. (NIH) 82-1765. Carcinogenesis 

Testing Program, NCI, NIH, Bethesda, MD; National Toxicology Program, ResearchTriangle Park, 

NC. 

NTP (National Toxicological Program). 1982b. Bioassay of 2,3,7,8-Tetrachloro-dibenzo-p-dioxin 

for Possible Carcinogenicity (Dermal Study). DHHS Publ. No. (NM) 82-1757. Carcinogenesis 

Testing Program, NCI, NIH, Bethesda, MD; NationalToxicology Program, Research Triangle Park, 

NC. 

Podoll, R.J., H.M. Jaber, and T. Mill. 1986. Tetrachlorodibenzodioxin: Rates of Volatilization and 

Photolysis in the Environment. Environ. Sci. Technol. 20:490-492. 

Schroy, J.M., F.D. Hileman, and SC. Cheng. 1985. Physical/Chemical Properties of 2,3,7,8- 

TCDD. Chemosphere 14:877-880. 

U.S. EPA. 1985a. Drinking Water Criteria Document for 2,3,7,8-Tetrachlorodibenzo-p-dioxin. 

U.S. Environmental Protection Agency, Environmental Criteria and Assessment Office, Cincinnati, 

OH. EPA 6001x-84-194-t. 

U.S. EPA. 1985b. Health Assessment Document for Poiychlorinated Dibenzo-p-dioxins. U.S. 

Environmental Protection Agency, Office of Health and Environmental Assessment, Washington, 

DC. EPA/600/8-84/O 14F. 

U.S. EPA. 1986a. Superfund Public Health Evaluation Manual. Office of Emergency and 

Remedial Response, Washington, DC. EPA/540/i-86/060. 

U.S. EPA. 1986b. Health Assessment Document for PolycNorinated Dibenzofurans (Review 

Draft). Environmental Criteria and Assessment Office, Cincinnati, OH. EPA/600/8-86/O 18-A. 

U.S. EPA. 1987a. The National Dioxin Study. Tiers 3,5,6 and 7. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Washington, DC. EPA 440/4-87-003. 

U.S. EPA. 1987b. National Dioxin Study. U.S. Environmental Protection Agency, Washington, 

DC. EPA 530-SW-87-025. 

U.S. EPA. 1987~. 2,3,7,8-TetracNorodibenzo-pdioxin. Health Advisory. U.S. Environmental 

Protection Agency, Office of Drinking Water, Washington, DC. 

U.S. EPA. 1988. U.S. EPA/Paper Industry Cooperative Dioxin Screening Study. U.S. Environmental Protection Agency, Office of Water, Washington, DC. EPA-440/l-88-025. 

c-7 
Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Windholz, M. ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 

Merck and Co., Rahway, NJ. 
1,2,3,7,8 PeCDD 

(PENTACHLORODIBENZODIOXIN) 

CAS No.: 40321-76-4 

CAS Preferred Nomenclature: 

Dibenzo-[b,e]( 1,4,)dioxin, 

1,2,3,7,8pentachIoroEmpirical formula: c 12H3cw2 

Cl 

:J!g& Cl 

% “3 c’, 0, 

Synonyms and Common Names: 

- 12 , t 3 * 7 . 8 Pentachlorodibenzodioxin 

- PeCDD 

REGULATORY STATUS 

l None established at present. 

SOURCES OF PeCDD 

Formation of PeCDD: 

l PeCDD is not intentionally produced for any commercial purposes in the U.S. It is an 

unwanted by-product of the manufacture of other organic compounds, as is 2,3,7,8 

TCDD. PeCDD can also be formed during the incineration of municipal and industrial 

wastes at low temperatures (<800°C) (U.S. EPA, 1984; ATSDR, 1987). 

l See dioxin: 2,3,7,8 TCDD and hexachlorodibenzodioxins prof&s for more information 

on other dioxins. 

FATE IN ENVIRONMENT 

l Based on its physical/chemical properties, PeCDD is only slightly soluble in water and 

strongly sorbs to soil (ROW z 7x 106). It also has a strong potential for bioaccumulation, 

although experimentaI data on specific BCF values were not found. 

c-9 
Persistence: 

l Photolysis of PeCDD can occur. In hexane, the half-life of PeCDD exposed to sunlight 

was reported to be 5.4 hours (U.S. EPA, 1984). 

PeCDD OBSERVED IN THE ENVIRONMENT 

l PeCDD has been detected in fish tissues (at unspecified concentrations), but not in 

drinking water (U.S. EPA, 1984). 

HEALTH EFFECTS 

Toxicolop3ical Effects: 

l No chronic exposure studies have been conducted with PeCDD. This includes a lack 

of studies on the potential carcinogenicity, teratogenicity, or mutagenicity of the compound. 

l Other forms of dioxin are extremely toxic and carcinogenic in animals. The acute LD50 

value of PeCDD suggests that it is biologically less active than TCDD (2,3,7,8 TCDD), 

but there are insufficient data to quantitatively estimate the health risk from PeCDD 

exposure (U.S. EPA, 1984; ATSDR, 1987). See dioxin: 2,3,7,8 TCDD profile for more 

information. 

Toxicological Efhts Indlces: 

l w LDso vdues: guinea pigs, 0.009 pmol/kg; mice, 0.94 wovkg (U.S. EPA. 1984). 
Value Reference 

Molecular Weight: 356.5 U.S. EPA, 1984 

Melting Point (“C): 240-24 1 U.S. EPA, 1984 

Water Solubility, S (pgk): 0.04 (est.) U.S. EPA, 1984 

&W (Octanol-Water Partition 

Coefficient): 7~10~ (est.) U.S. EPA, 1984 

Soil Adsorption Coefficient, Koc (mug): 5x106 U.S. EPA, 1984 

C-11 
ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for 2,3.7,8-TCDD (Dioxin). ATSDR, U.S. Public Health Service. 

U.S. EPA. 1984. Health Assessment Document for Polychlorinated Dibenzo-p-Dioxins. U.S. 

Environmental Protection Agency, Office of Health and Environmental Assessment, Washington, 

DC. EPA/600/8-84/O 14A. 

c-12 
HEXACHLORODIBENZODIOXINS 

13,3,6,7,8 HxCDD: 

CAS No.: 57653-85-7 

CAS Preferred Nomenclature: 

Dibenzo-[b.e)( 1,4,) dioxin, 

1,2,3,6,7,8-hexachloroEmpirical formula: C 12H2C16@ 

Synonyms and Common Names: 

- 1,2,3,6,7,8 Hexachlorodibenzodioxin 

- HxCDD 

- HxDD 

1,2,3,7,8,9 HxCDD: 

CAS No.: 19408-74-3 

CAS Preferred Nomenclature: 

Dibenzo-[b,e]( lP,)dioxin, 

1,2,3,7,8.9 hexachloroEmpirical formula: c12H2cw2 

Synonyms and Common Names: 

- 1,2,3,7,8,9 Hexachlorodibenzodioxin 

- HxCDD 

- HxDD 

1,2,3,4,7,8 HxCDD: 

CAS No.: 39227-28-6 

CAS Preferred Nomenclature: 

Dibenzo-[b,e]( 1,4)dioxin, 

1,2,3,4,7,8-hexachloroEmpirical formula: c 12H2cw2 

Synonyms and Common Names: 

- 1,2,3,4,7,8 Hexachlorodibenzodioxin 

- HxCDD 

- HxDD 

Cl 

c 

D13: 

o”o c’ 

C 0 Cl 

Cl 

%“2 %% 

c-13 
REGULATORY STATUS 

l None established at present 

SOURCES OF HxCDD 

Total HxCDD Produced: 

l The HxCDDs are not intentionally produced for any commercial purposes in the U.S. 

l The HxCDDs, as well as other forms of dioxin, are produced as unwanted contaminants 

of organic compounds, particularly chlorophenols such as pentachlorophenol (U.S. 

EPA, 1984; ATSDR, 1987). 

l See dioxin: 2,3,7,8 TCDD and 1.2.3.7.8 PeCDD profiles for more information on other 

dioxins. 

FATE IN ENVXRONMENT 

Partitioning: 

l Based on their physical/chemical properties, the HxCDDs are only slightly soluble in 

water and strongly sorb to soil (&w 4.2~10~). They also have strong potential for 

bioaccumulation (BCF for 1,2,3,7,8,9 HxCDD = 5,800). 

Pemistence: 

l Photoiysis of the HxCDDs can occur. In n-hexadecane. the half-life of 1,2,3,6,7,8 

HxCDD exposed to a sunlamp was 6.8 hours. Two other HxCDDs, 1,2,3,6,7,9 and 

1,2,4,6,7,9 HxCDD (in hexane) had ha&lives, respectively, of 17 and 47 hours, when 

exposed to sunlight (U.S. EPA, 1984). 

HxCDDs OBSERVED IN THE ENVIRONMENT 

l HxCDDs (unspecified isomers) have been detected in fish, gelatin, and human milk but 

not in drinking water. Concentrations were not given (U.S. EPA, 1984). 

c-14 
HEALTH EFFECTS 

Carcinogenicity : 

l The HxCDDs are rated as probable (B2) human carcinogens by the U.S. EPA because 

a 2: 1 mixture of 1,2,3,7,8,9 and 1,2,3,6,7,8 HxCDD caused liver tumors in rats and mice 

(U.S. EPA, 1984). 

Other Toxicological Effects: 

l Potency of HxCDD estimated to be V2Ot.b of TCDD, the most toxic form of dioxin (U.S. 

EPA, 1984). See dioxin: 2,3,7,8 TCDD profile for more health effects information. 

l No studies have been conducted on the teratogenicity or mutagenicity of the HxCDDs. 

Toxicological Effects Indices: 

l Cancer Potency Factor: 6.2~10~ (mg/kg/day)-t (U.S. EPA, 1984; PHRED, 1988). 

l 1,2,3,6,7,8 HxCDD oral LDw values: guinea pigs, 0.178 to 0.255 p.mol/kg; mice, 3.19 

cun0ms. 

l 1,2,3,7,8,9 HxCDD oral LD50 values: guinea pigs, 0.153 to 0.255 p.mol/kg; mice, 3.67 

wo~!s. 

C-15 
13,.3,6,7,8 HxCDD PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 390.9 U.S. EPA, 1984 

Melting Point (“C): 285-286 U.S. EPA, 1984 

Water Soiubility S(mg/L>: 8x10” (est.) U.S. EPA, 1984 

Log (Octanol-Water Partician 

Coefficient), log Gar: 7.6 U.S. EPA, 1984 

Soil Adsorption Coefficient, k (mug): 3x10’ (est.) U.S. EPA, 1984 

1,2,3,7,8,9 HxCDD PHYSICAUCHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 390.9 PHRED, 1988 

Melting Point (“C): 243-244 U.S. EPA, 1984 

Water Solubility, S (mg/L): 6~10~ PHRED, 1988 

Log (Cktanoi-Water Partition Coefficient), 

log Kow: 7.6 PHRED, 1988 

Soil Adsorption Coefficient, I& @L/g): 3x10’ PHRED, 1988 

Fish Bioconcentration Factor BCF: 5800 PHRED, 1988 

1,2,3,4,7,8 HxCDD PHYSICAL/CHEMICAL PROPERTIES 

Molecular Weight: 

Value 

390.9 

Reference 

U.S. EPA, 1984 

C-16 
REFERENCES 

ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for 2,3,7,8 TCDD (Dioxin). ATSDR, U.S. Public Health Service, Oak Ridge National Labortary, 

Oak Ridge, TN. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

U.S. EPA. 1984. Health Assessment Document for Polychlorinated Dibenzo-p-Dioxins. U.S. 

Environmental Protection Agency, Office of Health and Environmental Assessment, Washington, 

DC. EPA/600/8-84/O 14A. 

c-17 
C-28 
FURANS 

(POLYCHLORINATED DIBENZOFURANS, PCDFs) 

CAS Preferred Nomenclature: t 1 

2,3,7,8-Tetrachloro-dibenzofuran, 

2,3,7,8 TCDF 

Empirical Formula: CtzH4CktO 

. The polychlorinated dibenzofurans (PCDFs) are a group of 135 halogenated uicyclic 

aromatic hydrocarbons with many structural, distribution, and toxicity similarities to the 

dioxins (polychlorinated dibenzodioxins, PCDDs). A partial list of the furans is shown 

in Table 1. Very little is known about the individual furans because they typically occur 

as mixtures of different forms. For this reason, the sources, environmental fates, and 

health effects of the PCDFs will be discussed as a group, with mention of individual 

furans when appropriate. 

REGULATORY STATUS 

l No criteria or standards established at present. 

SOURCES OF PCDFs 

PCDF Production and Use: 

l PCDFs are not intentionally produced for any commercial purposes. 

l PCDF contamination of products or processes has not caused the banning or restriction 

of use in the U.S. 

Other Soun?es: 

l Just like the PCDDs, PCDFs are unwanted trace impurities of PCBs, chlorinated phenols 

such as hexachlorobenzene or pentachlorophenol, and phenoxy herbicides sue h as 2.4.5 

T. The production of many of these compounds has been restricted or banned (e.g., 

PCBs), but products containing them may still be in use (e.g., electrical transformers). 

Example concentrations are listed below: 

c-19 
. 

- Phenoxy herbicides had 0.008-0.15 mgkg PCDFs (Rappe et al., 1978, 1979; Ahling et al., 1977). 

- Pentachiorophenol has contained 59.8-790 mg/kg PCDFs (Rappe et al., 1979). 

- Hexachiorobenzene was found to contain 0.35 to 58.3 mgkg PCDFs (Viiianueva et 

al., 1974). 

- PCDF contaminants in polychiorinated biphenyls (PCBs) have been measured at 

levels of 0.8 to 13.6 mgkg (CNRC, 1978). 2.3,7,8 TCDF and 2,3.4,7,8 PeCDF are 

generally found at cl ppm in most PCBs (U.S. EPA, 1986). 

Incineration of municipal and industrial wastes at too low a temperature (~800 “C) can 

produce PCDFs, which can be released to the environment either in flue gas or adsorbed 

to fly ash (U.S. EPA, 1986). 

FATE OF PCDFs IN ENVIRONMENT 

Partitioning: 

. As shown in Table C-i, the compound 2,3,7,8 TCDF is the only PCDF for which a 

number of physical and chemical properties have been determined. Based on these 

properties, and its structural similarity to the dioxin 2,3,7,8, TCDD, 2,3,7,8 TCDF is 

likely to be only slightly soluble in water and strongly sorb to soil (I& 3 660,700). It 

also has a high potential for bioaccumulation based on an estimated BCF of 602,600 

(Hansch and Leo, 1981). 

Persistence: 

l Because 2,3,7,8 TCDF strongly sorbs to sediments, it persists in soils and aquatic 

systems. Some photodegradation can occur with tetra- and penta-CDFs losing chlorine 

atoms and forming tri-CDFs. For example, irradiation (254 nm) of 1 pg/L 2,3,7,8 TCDF 

in n-hexane for 4 hours yielded 2,3,8 and 2.3,7 TrCDF (Mazer and Hiieman, 1982). 

l Very little is known about the biodegradation of PCDFs, but they are probably like the 

dioxins and relatively resistant to biodegradation (U.S. EPA, 1986). 

HEALTH EFFECTS 

PCDF Effects on Animals: 

l Toxicological studies of PCDFs demonstrate that the effects of this group of compounds 

are remarkably similar to the PCDDs {U.S. EPA, 1986) (see dioxin: 2,3,7,8 TCDD, 

1,2,3,7,8 PeCDD, or HxCDDs profile for more information on dioxin@. 

l At present only short-term, high-dose, acute-exposure animal tests have been conducted 

with PCDFs. The most studied form has been 2,3,7,8 TCDF, which causes adverse 

health effects very similar to those caused by 2,3,7,8 TCDD. These effects include 

C-20 
weight loss, liver, thymus and immune system damage, and skin changes (U.S. EPA, 

1986). 

l Two of three monkeys died after 6 months of exposure to 5 g/kg 2,3,7.8 TCDF in their 

food (U.S. EPA, 1986). 

PCDF Effects on Humans: 

l Human exposure to PCDFs occurred in two major incidents when PCBs (containing a 

mixture of PCDFs) accidently contaminated rice oil in Japan and China. The resulting 

symptoms (attributed to 2,3,4,7,8 PeCDF exposure) consisted of liver disturbances, skin 

lesions, excessive skin pigmentation, temporary blindness, numbness of feet and hands, 

and weakness (Kuratsune et al., 1972; Kuratsune, 1975,198O; Urabe and Asahi, 1985; 

Lu and Wu, 1985; Hsu et al., 1985). 

l Studies of potential carcinogenesis in humans are still ongoing. No tests have been 

conducted with animals (U.S. EPA, 1986). 

Reproductive Effects: 

l 2,3,4,7,8 PeCDF, 1,2,3,7,8 PeCDF and 1,2,3,4,7,8 HxCDF can cause kidney damage 

and cleft palate in mouse fetuses (U.S. EPA, 1986). 

Mutagenic Activity: 

9 The four PCDFs (2.8 DCDF; 3.6 DCDF; 2,3,7,8 TCDF; and OCDF) tested for 

mutagenicity in bacteria had negative results (U.S. EPA, 1986). 

Toxicological Effects Indices: 

l Reference Dose (RfD), 2,3,7,8 TCDF: 2x10-5 CLg/kg/day (U.S. EPA, 1986). 

l Reference Dose (RfD), 2,3.4,7,8 PeCDF: 3x10-6 t.tgkg/day (U.S. EPA, 1986). 

. Oral LD50 values for 2,3,7,8 TCDF: guinea pigs, 5-10 pg/kg; mice and rats, > 6000 

PgAcg; rhesus monkey, 1000 pg/kg (U.S. EPA, 1986). 

c-21 
TABLE 1. 

Physical/Chemical Properties of Some Polychlorinated Dibenzofurans (from U.S. EPA, 1986) 

CAS No. Name 

Melting 

Point 

Abbreviation (“C) 

Density 

(g/ml) 

Estimated Log (Octanol- Soil 

Vapor Water Partition Adsorption 

Pressure Coefficient), Coefficient, 

(mm Hg, 25’C) log Kow log Koc 

51207-31-9 

57117-41-6 

57117-31-4 

57117-44-9 

72918-21-9 

70648-26-9 

6085 1-34-s 

67562-39-4 

55673-89-7 

2,3,7,8 Tetrachlorodibenzofuran 

1,2,3,7,8 Pentachlorodibenzofuran 

2,3,4,7,8 Pentachlorodibenzofuran 

1,2,3,6,7,8 Hexachlorodibenzofuran 

1,2,3,7,8,9 Hexachlorodibenzofuran 

1,2,3,4,7,8 Hexachlorodibenzofuran 

2,3,4,6,7,8 Hexachlorodibenzofuran 

253 2 19-228 1.72 2.fIxlo-6 5.82 5.61 

TCDF 

12378 , , , , 

PeCDF 

225-227 -- -- -s -- 

23478 , , , , 

PeCDF 

168-170 -- l.1x1o‘6 mm -- 

1,2,Wi7,8 232-234 -- -- -- -_ 

HxCDF 

VJJ,W N/A -- -- -- -- 

HxCDF 

LWV,8 225.5-226.5 -- em -- -- 

HxCDF 

ZV?,6,7,8 N/A -- -- -- -- 

HxCDF 

1,2,3,4,6,7,8 Heptachloro- 1,2,3,4,6,7,8 236-237 -- 0.3-0.4 w.. -- 

dibenzofuran HpCDF 

1,2,3,4,7,8,9 Heptachloro- 1,2,3,4,7,8,9 221-223 -- o-3-0.4 -- -- 

dibenzofuran HpCDF 

c-22 
Ahling, B., A. Lindskog, B. Jansson, and G. Sundstrom. 1977. Formation of Polychlorinated 

Dibenzo-p-Dioxins and Dibenzofurans During Combustion of a 2,4,5-T Formulation. Chemosphere 8:461-468. 

CNRC (Canadian National Research Council). 1978. Polychlorinated Biphenyls: Biological 

Criteria for an Assessment of their Effects on Environment Quality. NRCCXNRC, Ottawa. Publ. 

No. 16077. 

Hansch, C., and A.J. Leo. 198 1. Log P Software Program for Med-Chem Project, Pomona College, 

CA. 

Hsu, S.T., C.I. Ma, and S.K.H. Hsu. 1985. Discovery and Epidemiology of PCB Poisoning in 

Taiwan. A Four-Year Follow-up. Environ. Health Perspect 595. 

Kuratsune, M. 1975. National Conference on Polychlorinated Biphenyls. Chicago, November 

19-2 1, 1975. EPA 560/6-75-004. 

Kuratsune, M. 1980. Yusho. In Halogenated Biphenyls, Terphenyis, Naphthalenes, Dibenzodioxins and Related Products, ed. R.D. Kimbrough. Elsevier, Amsterdam. 

Kuratsune, M., T. Yoshimara, J. Matsuzaka, and A. Yamaguchi. 1972. Epidemiological Study on 

Yusho; a Poisoning Caused by Ingestion of Rice Oil Contaminated with a Commercial Brand of 

Polychlorinated Biphenyls. Environ. Health Perspect 1: 119-128. 

Lu, Y.C., and Y.C. Wu. 1985. Clinical Findings and Immunological Abnormalites in Yu-Cheng 

Patients. Environ. Health Perspect. 59:17. 

Mazer, T., and F.D. Hileman. 1982. The Ultraviolet Photolysis of Tetra-Chlorodibenzofurans. 

Chemosphere 11:65 l-66 1. 

Rappe, C., A. Gara, and H.R. Buser. 1978. Identification of Polychlorinated Dibenzofurans 

(PCDFs) in Commercial Chlorophenol Formulations. Chemosphere 7:98 l-99 1. 

Rappe, C., H.R. Buser and H-P. Bosshardt. 1979. Dioxins, Dibenzofurans and Other 

Polyhalogenated Aromatics: Production, Use, Formation, and Destruction. Ann. N.Y. Acad. Sci. 

320:1-18. 

Urabe, H., and M. Asahi, 1985. Past and&rent Dermatological Status of Yusho Patients. Environ. 

Health Perspect. 59: 11. 

U.S. EPA. 1986. Health Assessment Document for Polychlorinated Dibenzofurans. Review Draft. 

U.S. Environmental Protection Agency, Environmental Criteria and Assessment Office, Cincinnati, 

OH. EPA/600/8-86/O 18A. 

C-23 
Villanueva. E.C., R.W. Jennings, V.W. Burse, and R.D. Kimbrough. 1974. Evidence of 

Chlorodibenzo-p-dioxin and Chlorodibenzofuran in Hexachlorobenzene. J. Agric. Food Chem. 

22(5):916-917. 

c-24 
BIPHENYL 

CAS No.: 92-52-4 

CAS Preferred Nomenclature: 

1 ,1-Biphenyl 

Empirical Formula: C 12HlO 

Synonyms and Common Names: 

- Bibenzene - 1 ,l-Biphenyl 

- Diphenyl - Phenylbenzene 

REGULATORY STATUS 

Standards and Criteria: 

09 

ClPHlO 

l EPA Water Quality Criteria (for human . 

consumption of fish): 

None established at present 

l EPA Ambient Water Quality Criteria . 

(for protection of aquatic organisms): 

None established at present 

l EPA Drinking Water Standard Maxi- . 

mum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

l None found. 

EPA Drinking Water Health Advisories: 

None estabbshed at present 

EPA Tolerance Level for Citrus Fruit 

(40 CFR 180.141): 

110 ppm 

Food and Drug Administration Action 

Level for Fish: 

None established at present 

SOURCES OF BIPHENYL 

Total Biphenyl Produced: 

l Commercial production of biphenyl began in 1926 (Verschueren, 1983). In 1976, 

approximately 88 million pounds of biphenyl were produced (Kirk-Othmer, 1982). 

However, in 1984, production decreased to approximately 35 million pounds (USITC, 

1985). In 1986, four companies were producing biphenyl: Bethlehem Steel Corporation, Dow Chemical, Monsanto Company, and Sybron Corporation. 

c-25 
Uses of Biphenyl: 

l Biphenyl is used as a textile dye carrier, heat exchange medium, hydraulic fluid 

component, and as a plasticizer (Kirk-Othmer. 1982). It is also used during packaging, 

storage, and transport as a citrus wrapper fungicide to control mycelial growth and spore 

formation of blue, green, and stem rot molds. Biphenyl is used primarily on grapefruit, 

lemons, and oranges (Farm Chemicals Handbook, 1985; Thomson, 1985; Worthing, 

1979). 

l Biphenyl is the basic structural unit for the production of polychlorinated biphenyls 

(PCBs) (Waid, 1986) and is a breakdown product of PCBs. 

Other Sources: 

l Biphenyl is also a by-product of benzene production. About 1 kg is generated for every 

100 kg of benzene (Verschueren, 1983). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, biphenyl is soluble in water (Aq. Sol. = 7.5 

mg/l), highly volatile (H estimated as 0.027 atm l m3/mol), and strongly sorbed to 

organic matter (&w = 12,300). Biphenyl has a moderate potential for bioaccumulation 

(BCF ~500). 

Persistence: 

9 Biphenyl is biodegradable. Acclimation can significantly increase the biotransformation rate. For example, in fresh sewage no degradation occurred after 24 hours, whereas, 

in acclimated sewage, 87 percent was degraded after 24 hours (Verschueren, 1983). In 

river water at 20°C, 50 percent of initial biphenyl concentrations from 1 to 100 l.rg/L 

were degraded after 1.5 to 3 days. This corresponds to a degradation rate of 0.46/day 

to 0.9Uday (Bailey et al., 1983). 

l The volatilization half-life in deep water was found to be 7.52 hours (Bailey et al., 1983). 

HEALTH EFFECTS 

Cardnogenidty: 

l PapiIloma and squamous cell tumors of the forestomach were observed in rats (Clayton 

and Clayton, 198 l- 1982). 

C-26 
l The carcinogenic potential of this compound has not been evaluated by IARC or the 

U.S. EPA. 

Mutagenic Activity: 

l Biphenyl produced chromosome damage (sister chromatid exchange} in hamster 

fibroblast cells (Sax, 1984). 

Reproductive Effects: 

+ No effect was observed in rats fed biphenyl during fetal development (Shepard, 1980). 

Other Toxicological Effects: 

l Repeated exposure to dust may result in irritation of human skin and the respiratory tract 

l Chronic (long-term, low-dose) exposure may affect the central nervous system causing 

symptoms such as fatigue, headache, tremors, insomnia, sensory impairment, and mood 

changes (Sittig, 1985). 

l Brain damage and nerve degeneration were reported in workers exposed to biphenyl 

(Gosselin et al., 1984). 

Toxicologkai Effects indices: 

l Reference Dose (RfD): 5 x low2 mg/kg/day (PHRED, 1988). 

l TWA-TL,V (time-weighted average, threshold limit value) for occupational exposure: 

0.2 ppm (1.5 mg/m3) (ACGIH, 1986). 

l Oral LD50: rat, 328 g/kg; rabbit, 2.41 g/kg (Goss&r et al., 1984). 

c-27 
PHYSICAL/CHEMICAL PROPERTIES 

Valtle Reference 

Molecular Weight: 154.2 Verschueren, 1983 

Physical State @ 20°C: solid, light tan flakes 

Melting Point (“Cl: 69-7 1 Hartley & Kidd, 1983 

Boiling Point (“Cl: 254-255 Hartley & Kidd, 1983 

Specific Gravity: 1.18 @ 4OC Verschueren, 1983 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 7.5 (25°C) Verschueren, 1983 

Vapor Pressure, P (mm Hg): 1 (70°C) Hartley & Kidd, 1983 

Henry’s Law Constant, 

H @ 25°C (atm . m3/rno1): 0.027 (talc.) Lyman et al., 1982 

Log (Octanol-Water Partition Coefficient), 

log Kow: 4.09 Leo, 1983 

Soil Adsorption Coefficient, 

Koc (mUgI: 4.4x 1 o3 (cab) Lyman et al., 1982 

Fish Bioconcentration Factor, BCF: 590 (cab) Lyman et al., 1982 

437 (exptl.) Verschueren, 1983 

C-28 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Bailey, R.E., S.J. Gonsior, and W.L. Rhinehart. 1983. Biodegradation of the Monochlorobiphenyls 

and Biphenyl in River Water. Environ. Sci. Technol. 17( 10):621-624. 

Clayton, G.D. and F.E. Clayton, eds. 1981-82. Patty’s Industrial Hygiene and Toxicology. 3rd 

rev. ed., Vol. 2A, 2B, 2C, Toxicology. John Wiley and Sons, Inc., New York. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Gosselin, R.E., R.P. Smith, H.C. Hodge, and J.E. Braddock. 1984. Clinical Toxicology of 

Commercial Products. 5th ed. The Williams and Wilkins Co., Baltimore. 

Hartley, D. and H. Kidd, eds. 1983. The Agrochemicals Handbook. The Royal Society of 

Chemistry, Nottingham, England. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1984. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Klaassen, C.D., M.D. Amdur. and J. Doull, eds. 1986. Casarett and Doull’s Toxicology. The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Leo, A.J. 1983. Log P Parameter Database. Pomona College, Claremont, CA. 

Lyman, W.J., ed. 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill, New 

York. 

Public Health Risk Evaluation Database (PHRED). 1988. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, D.C. 

Reynolds, J.E.F., and A.B. Prasad, eds. 1982. Martindale: The Extra Pharmacopeia. 28th ed. The 

Pharmaceutical Press. London. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold Co., 

New York. 

Shepard, T.H. 1980. Catalog of Teratogenic Agents. 3rd ed. The Johns Hopkins University Press, 

Baltimore. 

Sittig, M., ed. 1985. Handbook of Toxic and Hazardous Chemicals and Carcinogens. 2nd ed. 

Noyes Publications, Park Ridge, NJ. 

C-29 
Thomson, W.T. 1985. Agricultural Chemicals Book IV - Fungicide. 1985 revision. 

U.S. EPA. 1986. Superfund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

U.S. International Trade Commission (USITC). 1985. Synthetic OrganicChemicals. United States 

Production and Sales. 1984. U.S. Government Printing Office, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Waid, J.S., ed. 1986. PCBs and the Environment. CRC Press, Boca Raton, FL. 

Worthing, C.R., ed. 1979. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-30 
CHLORDANE 

CAS No.: 57-74-9 (combined form) 

5 103-74-2 (tram- form) 

5 103-7 1-9 (cis- form) 

CAS Preferred Nomenclature: 

4,7-Methano- lH-indene 

1,2,4,5,6,7,8,8+ctachloro2,3,3a,4,7,7a-hexahydro 

Empirical Formula: CtoH6C 18, occurs in cis and trans forms 

Synonyms and Common Names: 

- Chlor Kil 

- Corodan 

- Kypchlor 

- Octa-Klor 

- Oktaterr 

- Synklor 

- Toxichlor 

Chlorindan 

Dowchlor 

NiIlUl 

Topiclor 

Ortho-Klor 

Octachlorodi-hydrodicyclopentadiene 

Velsicol 1068 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of fish) for a 1O-6 cancer 

risk (U.S. EPA, 1986b): 

0.48 rig/L 

l 

l EPA Ambient Water Quality Criteria . EPA Tolerance Levels for Raw 

{for protection of aquatic organisms) Agricultural Commodities (5 1 FR 

(IRIS, 1989): 46668): 

Chronic, clg/L -E-F 4.3x10- 

Acute, @L 2.4 9:ox1o‘2 

All tolerances revoked, 1 U24/86 

EPA Drinking Water Health Advisories (IRIS, 1989) 

m( 10 kg): 

l-day exposure = 60 pg/L 

lo-day exposure = 60 j.tg/L 

longer-term exposure = 0.5 pg/L 

adult(70 kg): 

longer-term exposure = 2 pg/L 

c-31 
l EPA Drinking Water Standard (50 FR l Food and Drug Administration Action 

4696): Level for Fish!55 FR 1436 1): 

Proposed Maximum Contaminant 0.3 ppm , 

Level = 0.002 mg/L Action Level for Other Food 

Proposed Maximum Contaminant 0.1 to 0.1 to 0.3 ppm* 

Level Goal = 0 mg/L 

* FDA Action Levels are for use in 

interstate commerce. 

Use Restrictions and Bans: 

9 All uses except subsurface ground insertion for termite control cancelled in 1987. All 

other uses except the dipping of roots or tops of nonfood plants were cancelled in 1978, 

although some uses were phased out gradually through 1983 (43 FR 12372). Limited 

sales, distribution and use of existing stocks of chlordane products allowed, with the 

requirement that all applications must be done by a licensed applicator (1987, 

52 FR 42145). 

SOURCES OF CHLORDANE 

Total Chlordane Produced: 

+ In 1971, 25 million pounds were produced by Velsicol Chemical Co. (Ouellette and 

King, 1977). In 1974, production had decreased to 22 million pounds (U.S. EPA, 1980). 

Most uses were phased out between 1978 and 1980. Velsicol Corp. is still the only U.S. 

producer (U.S. EPA, 1986b). 

l Oxychlordane, although not found in technical-grade chlordane, is a major metabolic 

product of chlordane. It has comparable toxic effects (see Oxychlordane profile) 

(Bamett and Dorough, 1974). 

Uses of Chlordane: 

4 Chlordane is a chlorinated hydrocarbon originally registered as a pesticide in 1948. Prior 

to cancellation in 1980, it was used for control of ants, cutworms, grasshoppers. and 

other insects for corn, grapes, strawberries, and other crops (Hartley and Kidd, 1987). 

l Until 1987, chlordane was used as a dip for nonfood roots and tips of plants. 

l No sale, distribution, or use is permitted after A@ 15.1988 (52 FR 42 145, Nov. 3, lP87). 

C-32 
FATE JN ENVIRONMENT 

Partitioning: 

l Based on t;” physical/chemical properties, chlordane is moderately volatile (H = 9.6x 10’ 

atm l m /mole), sorbs moderately to soil (&w = 2,100), and has a high potential for 

bioaccumulation (BCF = 14,000). 

Persistence: 

l The cis- form of chlordane can hydrolyze under alkaline conditions (Kh = 4.3~10~ 

mol/hr). The trans- form did not hydrolyze at pH 3,7, or 11 during the 5-day duration 

of the experiments (Ellington et al., 1987). Chlordane can undergo photolysis in the 

presence of photosensitizers. One degradation product is photo-cis-chlordane (more 

toxic to some animals and can be bioaccumulated (IRIS, 1989)). Little information is 

available on the biotransformation of chlordane in aquatic systems. The half-life is 

estimated to be about 1 year (Hartley and Kidd, 1987). 

HEALTH EFFECTS 

Carcinogenicity: 

l Chlordane administered orally has been shown to cause liver carcinomas in mice and 

rats of both sexes (IRIS, 1989; Williams et al., 1984). The EPA classification is B2, a 

probable human carcinogen (IARC Class 2b) (IARC, 1979; IRIS. 1989). 

Mutagenic Activity: 

l Tests with chiordane in cultured mammalian cells has shown it to be mutagenic. Results 

have been negative, however, in mouse and bacterial tests. Chlordane has induced gene 

conversions in yeast. (U.S. EPA, 1984; IRIS, 1989). 

Reproductive Effects: 

l Orally-administered chlordane was not fetotoxic or teratogenic to rat offspring. It did 

cause decreased fertility in both sexes for rats and in female mice. The viability of mice 

and rat offspring was also decreased (U.S. EPA, 1984). 

Other Toxicological Effects: 

l Acute (short-term, high-dose) poisoning effects are due to chlordane neurotoxicity and 

can result in hyperexcitability, convulsions, depression, muscle tremors, coma, and 

possible death (U.S. EPA, 1984). Chronic (long-term, low-dose) exposure can result in 

c-33 
liver toxicity and blood disorders such as anemia (U.S. EPA, 1984). Chronic chlordane 

exposure causes liver disease in rats, mice. and dogs (IRIS, 1989; TDB, 19851986). 

Toxicologkal Effects Indices: 

l Cancer potency factor (CPF) = 1.3 (mg/kg/day)“ (IRIS, 1989) 

Concentration 

1 in 10,000 3 Ns 

1 in 100,000 0.3 pgL 

1 in l,OOO,OOO 0.03 J.&/L 

l Reference Dose (IUD) for noncarcinogenic effects: 6~10.~ mg/kg/day (IRIS, 1989) 

l TWA-TLV (Time-weighted average, threshold limit value for occupational exposures): 

0.5 mg/m3 for skin exposure (ACGIH, 1986). 

c-34 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0: 

Boiling Point (“C): 

Specific Gravity: 

Water Solubility, S (mg/L): 

Vapor pressure, P (mm Hg): 

Henry’s Law Constant H @ 

25OC (atm l m3/mol): 

Hydrolysis Rates: 

Octanol-Water Partition 

Coefficient, log Kow: 

Org. Carbon Adsorption 

Coefficient, K~c (mL/g): 

Fish Bioconcentration 

Factor, BCF: 

409.8 

pure-solid; 

technical gradeamber viscous liquid 

103.0- 105.0 (cis) 

107.0-108.8 (trans-) 

175 

1.56-1.57 

0.056- 1.85 

1~10’~ (25OC) 

9.6~10’~ U.S. EPA, 1986b 

tram-: no 

degradation in 5 days 

cis-: Rb = 4.3x103/ 

mol/hr 

Ellington et al., 

1987 

3.32 

2.4x105 

l.4x104 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

U.S. EPA, 1986b 

Callahan et al., 1979 

U.S. EPA, 1986b 

U.S. EPA, 1986b 

U.S. EPA, 1986b 

U.S. EPA, 1980 

c-35 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Bamett, J.R., and H.W. Dorough. 1974. Metabolism of Chlordane in Rats. J. Agric. Food Chem. 

22:612-619. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards. EPA-440/4-79-029a. 

Ellington , J.J., F.E. Stancil, Jr., W.D. Payne, and C. Trusty. 1987. Measurement of Hydrolysis 

Rate Constants for Evaluation of Hazardous Waste Land Disposal: Volume 2: Data on 54 

Chemicals. U.S. Environmental Protection Agency, Athens, GA. EPA/600/3-871019. 

Hartley, D., and Kidd, eds. 1987. Agrochemicals Handbook. Royal Society of Chemistry: 

Nottingham, England. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans. Vol. 20. IARC, Lyon, France. 

IRIS. 1989. Chlordane. Integrated Risk Information System. U.S. Environmental Protection 

Agency, Washington, DC. Last updated Feb. 10, 1988. 

Ouellette, R.P., and J.A. Ring. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co.. New York. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Chlordane. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Criteria and Standards Division. EPA-440/5- 

8-027. 

U.S. EPA. 1984. Health Effects Assessment for Chlordane. Office of Research and Development, 

Cincinnati, OH. EPA-540/l-86-023. 

U.S. EPA. 1986a. Pesticide Fact Sheet #109, Chlordane. 

U.S. EPA. 1986b. Superfund Public Health Evaluation Manual. U.S. Enviromental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

C-36 
Williams, GM., and S. Numoto. 1984. Promotion of Mouse Liver Neoplasmas by the Organochlorine Pesticides Chlordane and Heptachlor in Comparison to Dichlorodiphenyltrichloroethane. Carcinogenesis 5: 1689- 1696. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck and Co., Rahway, NJ. 

c-37 
CHLORDANE, HEPTACHLOR, OXYCHLORDANE , AND RELATED COMPOUNDS 

OBSERVATIONS AND EFFECTS ON PISCIVOROUS WILDLIFE 

There are several components in technical grade chlordane. Active ingredients include chlordane, 

cis-chlordane, trans-chlordane, trans-nonachlor, and heptachlor (Stickel et al., 1979). The metabolic 

products of chlordane are oxychlordane, chlordane isomers, glucuronides, and heptachlor (Newell 

et al., 1987). 

Technical grade heptachlor contains heptachlor, trans-chlordane, and cis-chlordane (Stickel et al., 

1979). Heptachlor metabolizes to heptachlor epoxide {U.S. EPA, 1980, as cited in Newell). 

Stickel et al. (1979) investigated the lethal levels of chlordane and the metabolites oxychlordane 

and heptachlor epoxide in several bird species. The lethal level of heptachlor epoxide in the brains 

of heptachlor-fed birds was 8 ppm wet weight. In oxychlordane-fed birds, the lethal level of 

oxychlordane was 5 ppm wet weight. However, chlordane compounds exhibit an additive effect. 

For birds that were fed chlordane, Stickel et al. (1979) found that the lethal levels of heptachlor 

epoxide and oxychlordane in the brain were only about 28% of the concentrations listed above. 

Chlordane components and metabolites have been detected in several fish-eating bird species. Two 

hundred twenty eggs were randomly collected from black-crowned night-herons in the intermountain western United States between 1978 and 1980. Oxychlordane was detected in 35% of the eggs. 

Over 27% had heptachlor epoxide residues. Cis-chlordane was detected in 16%. Trans-nonachlor 

was found in 25%. and cis-nonachlor was present in 6% of the eggs (Henny et al., 1984). 

Ohlendorf et al. (198 1) collected individuals of various species of herons nationwide and analyzed 

them for organochlorines. Most of the birds were found either dead or moribund. The highest 

concentration of heptachlor epoxide (1.9 ppm), oxychlordane (0.87 ppm), and trans-nonachlor (1.1 

ppm in the brain) were found in a great blue heron that apparently died from die&in. 

Residues of these contaminants were also detected in a high percentage of dead or dying ospreys 

collected from the eastern United States from 1975 to 1985 (Wiemeyer et al. 1987). Cis-chlordane 

was detected in 52% of the ospreys. Trans-nonachlor was detected in 45%. Concentrations of 

oxychlordane and cis-nonachlor were found in 35% of the birds, while 13% had detectable levels 

of heptachlor epoxide. 

The State of New York proposed piscivorous wildlife dietary criteria for chlordane (0.5 ppm), and 

for heptachlor epoxide (0.2 ppm) (Newell et al., 1987). These general criteria were established 

based on existing studies with factors of uncertainty taken into account. 

The effects of chlordane, oxychlordane, and heptachlor epoxide on piscivorous wildlife are 

summarized in the following table: 

C-38 
Effects of Chlordane* Concentrations on Piscivorous Wildlife 

Animal 

Piscivorous 

Wildlife 0.5 ppm (diet) 

0.37 ppm (diet) 

Birds 

Piscivorous 

Wildlife 

8 ppm (brain) 

0.2 ppm (diet) 

0.21 ppm (diet) 

Birds 5 ppm (brain) 

Thlordane, heptachlor epoxick and oxychlorclane 

Estimated 

NOEL 

cancer risk 

of lo-2 

Newell et al., 1987 

Newell et al., 1987 

death Stickel et al., 1979 

Estimated 

NOEL 

cancer risk 

of 1O-2 

Newell et al., 1987 

Newell et al.. 1987 

death Stickel et al., 1979 

REFERENCES 

Henny, C.J., L.J. Blus, A.J. Krynitsky, and CM. Bunck. 1984. Current Impact of DDE on 

Black-Crowned Night-Herons in the Intermountain West. J. Wildl. Manage. 48( 1) l- 13. 

Khasawinah, A.M. 1982. Metabolism of ChlordaneIHeptachlor in Animals. Prepared for the 

Velsicol Chemical Corp., Chicago (unpubl.) (as cited in Newell et al., 1987). 

Newell, A.J., D.W. Johnson, and LX. Allen. 1987. Niagara River Biota Contamination Project: 

Fish Flesh Criteria for Piscivorous Wildlife. Tech. Rep. 87-3. NY Dept. Environ. Consent., Div. 

Fish Wildl., Bureau Environ. Protection. 

Ohlendorf, H.M., D.M. Swineford, and L.N. Locke. 1981. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4) 125-135. 

c-39 
Stickel, L.F., W.H. Stickel, R.D. McArthur, and D.L. Hughes. 1979. Chlordane in Birds: A Study 

of Lethal Residues and Loss Rates. In: Toxicology and Occupational Medicine, organizer W.B. 

Deichman, ElsevierINorth Holland, New York, NY. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Heptachlor. U.S. Environmental Protection 

Agency, Washington, DC. EPA 440/5-80-052. 

Wiemeyer, S. N., S. K. Schmeling, and A. Anderson. 1987. Environmental Pollutant and Necropsy 

Data for Ospreys from the Eastern United States, 19751982. J. Wildl. Diseases 23(2) 279-291. 

c-40 
CHLORPYRIFOS 

CAS No.: 2921-88-2 

CAS Preferred Nomenclature: 

Phosphorothioic acid, O,O-diethyl 

o-(3.56trichloro-2-pyridinyl) ester 

Empirical Formula: CgHt 1Cl3NO3PS 

Synonyms and Common Names: 

- Dursban - Eradex 

- Lorsban - Pyrinex 

- Brodan 

REGULATORY STATUS 

C,H, ,Cl,NO,PS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of fish): 

None established at present 

l EPA Ambient Water Quality Criteria . 

(for protection of aquatic organisms) 

(U.S. EPA, 1986): 

Freshwater Saltwater 

Acute, pg/L 0.083 0.041 

Chronic, pg/L 0.041 0.0056 

l EPA Drinking Water Standard Maxi- . 

mum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

EPA Drinking Water Health Advisories: 

None established at present 

EPA Tolerance Levels (40 CFR 

185.1000): 

mint oil = 10 ppm 

citrus oil = 25 ppm 

other listed commodities = 0.05 to 5 

PPm 

Food and Drug Administration Action 

Level for Fish: 

None established at present 

. Current labeling states that it is not to be applied directly to water bodies (U.S. EPA, 

1986). 

9 Meat or dairy animals are not allowed to graze in treated orchards. 

l Treated seeds are not to be used for human consumption, as a feed for livestock or 

poultry, or for grams to be used in making oils. 

C-41 
SOURCES OF CHLORPYRIFOS 

Total Chlorpyrifos Produced: 

. In 1982 about 3,500 tons were used as an insecticide (Green et al., 1987). 

9 Developed during the 1960s by Dow Chemical (Midland, Michigan) to replace the more 

persistent organochlorine pesticides (e.g., DDT)(SRI, 1986; U.S. EPA, 1986). 

uses of Chlorpyrifos: 

l Chlorpyrifos is an organophosphate insecticide developed in the 1960s to replace the 

environmentally persistent organochlorine pesticides (e.g., DDT). 

l It has been used for a broad range of insecticidal applications, including mosquitoes, 

flies, household pests, and aquatic larvae. 

l Primarily, it is used to control soil and folk insect pests on cotton, peanuts, and sorghum 

(Worthing, 1983; U.S. EPA, 1986). 

l Chlorpyrifos is also used to control root-infesting and boring insects on a variety of fruits 

(e.g., citrus crops, apples, bananas, peaches, grapes, nectarines), nuts (e.g., almonds, 

walnuts), vegetables (e.g., beans, broccoli, brussel sprouts, cauliflower, soybeans, 

cabbage, peas) and field crops (e.g., alfalfa and com)(U.S. EPA, 1984). 

l As a household insecticide it has been used to control ants, cockroaches, fleas, and 

mosquitoes (Worming, 1983). 

l Chlorpyrifos is registered for use in controlling subsurface termites in California (U.S. 

EPA, 1983). 

l It is also used to control ticks on cattle and sheep (Thomson, 1985). 

None identified. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based r$on its ph~sical/chemical properties, chlorpyrifos has a low volatility (H = 

6.7x10 atm l m /mol), and a moderate potential for bioaccumulation (BCF=470). 

Chlorpyrifos is predicted to have an intermediate volatilization rate from surface soil 

(P/S& = 6.9x 10”’ mm Hg . Umg corresponding to an estimated volatilization half-life 

of 23 days) (Lyman et al., 1982). 

c-42 
l Chlorpyrifos is hydrophobic (i.e., has an affinity for organic soils), rapidly sorbs to 

suspended organics and sediments in aquatic systems &w=128,800), and remains 

stable for long periods of time (U.S. EPA, 1986). 

l McCall (1986) reported intermediate soil/water partition coefficients (KS) of 50.66, and 

100 for chlorpyrifos adsorbed to a loam soil (organic carbon 0.68 percent), a sandy loam 

soil (organic carbon 1.1 percent), and a silt loam soil (organic carbon 2.0 percent), 

respectively. In soil column studies, using 30-cm columns, approximately 5 percent of 

the chlorpyrifos applied leached below the top 5 cm of loam soil, but less than 1 percent 

leached below the top 5 cm of sandy loam and silt loam soils leached with 20 in. of water 

at a rate of 1 ml/hr. 

l Murphy and Lutenske (1986) reported a high steady state BCF of 1.4~10~ for chlorpyrifos in rainbow trout. 

Persistence: 

l The hydrolysis half-life for chlorpyrifos in buffered, distilled water at 25OC was found 

to be 22.8.35.3, and 62.7 days at pH 8.1.6.9, and 4.7, respectively; the rate was enhanced 

16-fold in canal and pond water at 25°C (Verschueren, 1983). McCall (1986) reported 

relatively long to intermediate hydrolysis half-lives (25OC) for chlorpyrifos of 72.8 days 

at pH 5, 72.1 days at pH 7, and 15.8 days at pH 9. Hydrolysis products are 3,5,6- 

trichloro-2-pyridinol and O-ethyl O-(3,5,6-trichloro-2-pyridyl) phosphorothioate. 

Macalady and Wolfe (1985) observed hydrolysis half-lives ranging from 12 to 68 days 

in pond and river water. 

l Photolysis of chlorpyrifos can occur as evidenced by the following experimental data. 

Fontaine and Teeter (1987) reported a relatively short half-life of 2.6 days for chlorpyrifos in air exposed to artificial light with a comparable but less intense irradiation 

spectrum to that of sunlight. Yackovich and Miller (1984) reported relatively short 50 

percent dissipation times of 3 to 6 days for chlorpyrifos on loam soi irradiated with >290 

nm artificial light compared to a 50 percent dissipation time of 12 days on loam soil 

incubated in the dark. 

l Bidlack (1979) reported intermediate to relatively long 50 percent dissipation times of 

11 to 141 days (averaging 63 days) for chlorpyrifos incubated in 7 different soils under 

aerobic conditions. McCall (1985a) reported a 50 percent dissipation time of 7 to 10 

days for chlorpyrifos incubated in a sandy loam soil under aerobic conditions. Bidlack 

(1979) reported 50 percent dissipation times of 15 and 58 days for chlorpyrifos incubated 

under anaerobic conditions in a loam soil and in a clay soil, respectively. 

c-43 
HEALTH EFFECTS 

Carcinogenicity : 

l Studies with rats, mice and dogs demonstrated no carcinogenicity (U.S. EPA, 1983). 

Mutagenic Activity: 

l Bacterial mutagenicity tests were negative (U.S. EPA, 1983). 

Reproductive Effects: 

l No teratogenic or fetotoxic effects 

Other Toxicologiad Effects: 

in mice or rats IRIS, 1989). 

l Chlorpyrifos, in a manner similar to other organophosphate pesticides, interferes with 

the nerve-muscle relationship by inhibiting the enzyme cholinesterase. Without 

cholinesterase, the neurotransmitter acetylcholine accumulates at nerve-muscle junctions and interferes with muscle coordination (Green et al., 1986; U.S. EPA, 1986). 

l Acute (high-dose, short-term) poisoning can produce a variety of symptoms including 

weakness, blurred vision, nausea, diarrhea, wheezing, tremors, psychosis, convulsions, 

paralysis, coma, and death (Klaassen et al., 1986; U.S. EPA, 1983, 1986). 

l It is rapidly detoxified in rats and dogs (Worthing, 1983). 

Toxicological Effects Indices: 

l Reference Dose (RfD): 3 x 10m3 mg/kg/day (IRIS, 1989). 

+ TWA-TLV (time-weighted average, threshold limit value) for occupational skin exposure: 0.2 mg/m3 (ACGIH, 1986). 

l Oral LD5o: rats, 82-245 mgkg (U.S. EPA, 1983). 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25OC (atm . m /moI): 

Log (Octanol-Water Partition 

Coefficient), log hw: 

Soil Adsorption Coefficient, K&mL/g): 

Fish Bioconcentration 

Factor, BCF: 

351 

solid, white 

granules 

42-43.5 

N/A 

1.398 @ 43.5”C 

(liquid) 

N/A 

2 (25°C) 

1.87~10-~ (25°C) 

6.7~10-~ 

U.S. EPA, 1983 

Farm Chemicals 

Handbook, 1987 

Hartley & Kidd, 1983 

Verschueren, 198 3 

Hartley & Kidd, 1983 

McCall et al., 1983 

McCall et al., 1983 

5.11 Leo, 1983 

13,600 Kenaga, 1980 

470 McCall et al., 1983; 

450 (exptl.) Kenaga, 1980 

c-45 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Bidlack. H.D. 1979. Degradation of Chlorpyrifos in Soil Under Aerobic, Aerobic/Anaerobic, and 

Anaerobic Conditions. Dow Chemical Co. Asc. #256041. 

Farm Chemicals Handbook. 1987. Meister Publishing Co., Willoughby, OH. 

Fontaine, D.D., and D. Teeter. 1987. Photodegradation of Chlorpyrifos in the Vapor Phase. Report 

#GH-C- 19 11. Dow Chemical Co. and ABC Laboratories. 

Green, M.B., G.S. Hartley, and T.F. West. 1987. Chemicals for Crop Improvement and Pest 

Management. 3rd ed. Pergarnon Press, Oxford, England. 

Hartley, D. and H. Kidd, eds. 1983. The Agrochemicals Handbook. The Royal Society of 

Chemistry, Nottingham, England. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Kenaga, E.E. 1980. Correlation of Bioconcenttation Factors of Chemicals in Aquatic and Terrestrial Organisms With Their Physical and Chemical Properties. Environ. Sci. Technol. 14:553- 

556. 

Klaassen C.D., M.D. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology. The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Leo, A.J. 1983. Log P Parameter Database, Issue #24 (dated Dec. 16, 1983). Obtained from the 

Medchem Project, Pomona College, Claremont, CA. 

Lyman, W.J., W.F. Reehl. and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co. 

Macalady, D.L., and N.L. Wolfe. 1985. Effects of Sediments Sorption and Abiotic Hydrolysis. 1. 

Organophosphorothionate Esters. J. Agric. Food Chem. 33(2):167-173. 

McCall, P.J. 198%. Column Leaching and Sorption Studies with Chlorpyrifos. Report GH-C1977. Dow Chemical Co. Act. No. 260794. 

McCall, P.J. 1985b. Chlorpyrifos Aged Column Leaching. Report GH-C-1778. Dow Chemical 

co. 

McCall, P.J. 1986. Hydrolysis of Chlorpyrifos in Dilute Aqueous Solution. Report GH-C-1791. 
McCall, P.R., et al., 1983. Estimation of Environmental Partitioning or Organic Chemicals in Model 

Ecosystems. Residue Reviews. 85:23 l-244. 

Murphy, P.G., and N.E. Lutenske. 1986. Bioconcentration of Chlorpyrifos in Rainbow Trout. 

Project #ES-928. Dow Chemical Co. Act. No. 400564-01. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers, Stanford Research 

Institute, Menlo Park, CA. 

Thomson, W.T. 1985. Agricultural Chemicals. Book I - Insecticide. 1985 revision. 

U.S. EPA. 1983. Analysis of the Risks and Benefits of Seven Chemicals Used for Subterranean 

Termite Control. U.S. Environmental Protection Agency. EPA-54019-83-005. 

U.S. EPA. 1984. Registration Standard for Chlorpyrifos. U.S. Environmental Protection Agency, 

Office of Pesticides. Washington, DC. 

U.S. EPA. 1986. Ambient Water Quality Criteria for Chlorpyrifos. U.S. Environmental Protection 

Agency, Washington, DC. EPA-440/5-86-005. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A world compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

Yackovich, P.R., and J.H. Miller. 1984. Photodegradation of Chlorpyrifos on Commerce Soil 

Surface. Dow Chemical Co. 

c-47 
c-48 
&-DDE 

CAS No.: 72-55-9 

CAS Preferred Nomenclature: 

Benzene, 1, I’-(dichloroethenylidene) 

bis (4-chloroEmpirical Formula: C t&I8C 14 

Synonyms and Common Names: 

- 4,4’-DDE 

- p,pF128M&Dichlorodiphenyl dichloroethylene 

- 1.1 -Dichloro-2,2-bis (p-chlorophenyl) - ethylene 

REGULATORY STATUS 

standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of fish) for a lo4 combined (DDT and DDE) cancer risk 

(U.S. EPA, 1980): 

0.024 rig/L 

EPA Drinking Water Health Advisories: 

None established at present 

l EPA Ambient Water Quality Criteria . Food and Drug Administration Action 

(for protection of aquatic organisms) Level for Fish, combined (DDT, TDE 

DDT, TDE and DDE combined (U.S. and DDE) (55 FIX 14361): 

EPA, 1980): 5* PPm 

Acute, pg/L 1.1 Es-F - 

Chronic,M gg/L 1.0x 10m3 1:0x 1o-3 

l EPA Drinking Water Standard Maxi- . 

mum Contaminant Level: 

None established at present 

* 

Food and Drug Administration Action 

Levels for Other Foods: 

0.05 to 3* ppm 

FDA Action Levels are for use in interstate commerce 

Use: Not produced commercially. 
SOURCES OF DDE 

Total DDE Produced: 

l DDE is a metabolic breakdown product of the insecticide DDT. DDT was first 

synthesized in 1874 and was used as an insecticide starting in 1939. By 1961, 1,200 

formulations were available for use on 334 crops. Peak production was 180 million 

pounds in 1963 (McEwen and Stephenson, 1979). 

l DDE was initially synthesized by German researchers during World War II. Production 

data are not available, but presently the only production may be for use as a laboratory 

standard (McEwen and Stephenson, 1979). 

Uses of DDE: 

l Unlike its parent compound, DDE has no insecticidal properties (McEwen and Stephenson, 1979). 

l Military use only (Verschueren, 1983). 

Other Sources: 

l DDT is no longer used in the U.S. It was a widely-used insecticide on a variety of crops 

and was also used for the control of insect-borne diseases (e.g., mosquitoes carrying 

malaria). DDT was banned because it was shown to be carcinogenic and also more than 

150 species of insects developed resistance to it. DDE is formed by the degradation of 

DDT by loss of one molecule of hydrochloric acid. DDE further degrades to DDA by 

loss of two more molecules of HCl (Farm Chemicals Handbook, 1985). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, p,p’-DDE is moderately volatile (H = 6.8~10’~ 

atm l m3/mole), very strongly sorbed to soil (hw = 1.0~10-~), and has a high potential 

for bioaccumulation (BCF was determined by experiment to be 1.8~10~). 

Persistence: 

. Direct photolysis of p,p’-DDE in water has been reported in laboratory experiments by 

Zepp et al. (1976,1977) and in aquatic environments by Singmaster (1975). A quantum 

yield of 0.3 was measured by Zepp et al. at a wavelength of 313 nm. This results in 

estimated haIf-lives at 4.0’ latitude of 0.9 days in summer to 6.1 days in winter. 

c-50 
+ p,p’-DDE is the hydrolysis breakdown product of DDT. DDE, itself, was found to be 

stable with respect of hydrolysis (half-life of more than 120 years at pH 5 and 27°C). 

l DDE is biodegraded very slowly, if at all, in aquatic environments (Callahan et al., 1979). 

HEALTH EFFECTS 

Carcinogenidty: 

Liver tumors (hepatocellular carcinomas) observed in mice, but not in rats. IARC 

Classification - 2b. (IARC, 1973; Sax, 1984; HSDB, 1988). 

The U.S. EPA has classified DDE as a probable human carcinogen (B2) and is presently 

reviewing experimental data in order to determine a cancer potency factor (PHRED, 

1988). 

Mutagenic Activity: 

l Not mutagenic in bacterial assays, but weakly mutagenic in mouse lymphocytes and 

cytogenetic analysis in rats (Sax, 1984; HSDB, 1988). 

Reproductive Effects: 

l No data located on teratogenicity of DDE, but did not adversely affect lactation or 

neonatal growth at maternal daily doses of 10 mgkg (HSDB, 1988). 

Other Toxicological Effects: 

l Causes liver damage in rats (Sax, 1984). 

Toxicological Effects Indkes: 

l Cancer Potency Factor (CPF): 3.4~10” (mg/kg/day)-’ (IRIS, 1989). 

+ Oral LD5o: rat, 880-1240 mgkg (Sax, 1984). 

C-51 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0: 

Boiling Point (“0 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25°C (sun. m3/mo1): 

Log (Octanol- Water Partition 

Coefficient), log I&W: 

Soil Adsorption Coefficient, Kr>c(mUg): 

Fish Bioconcentration 

Factor, BCF: 

3 18.0 

solid 

88-90 

N/A 

N/A 

N/A 

0.04 (2OOC) 

6.5x 1O-6 (20°C) 

6.8x1o-5 PHRED. 1988 

7.00 

4.4x lo6 

1.8~10~ (expel.) 

53,600 (talc) 

Callahan et al., 1979 

Callahan et al., 1979 

Callahan et al.. 1979 

PHRED. 1983; 

Mabey et al., 1982 

PHRED, 1988: 

Mabey et al., 1982 

Verschueren, 1983; 

PHRED, 1988; 

Lyman et al., 1982 

c-52 
Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore. B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol 1. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards. EPA-440/4-79-029a. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

HSDB. 1988. Hazardous Substances Data Base Computer Printout: p,p’-DDE. Retrieved May 

16, 1988. National Library of Medicine, Bethesda, MD. 

IARC (International Agency for Research on Cancer). 1973. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 5. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington. DC. 

Lyman, W.J., ed. 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill, New 

York. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. Mill, T.W. Chou, J. Gates, J.W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440/4-8 1-O 14. 

McEwen, F.L., and G.R. Stephenson. 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, Inc., New York. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold Co., 

New York. 

Singmaster, J.A., III. 1975. Environmental Behavior of Hydrophobic Pollutants in Aqueous 

Solutions. Ph.D. thesis, University of California, Davis, CA. University of Microfilms, Ann Arbor, 

MI, Order No. 76- 14,237. (D&s. Abstr. Int. B 1976,36( 12, Pt. 1):6206-6207. 

U.S. EPA. 1980. Ambient Water Quality Criteria for DDT. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals.1 2nd ed. Van 

Nostrand Reinhold, New York. 

c-53 
Zepp. R.G.. N.L. Wolfe, J.A. Gordon, and R.C. Fincher. 1976. Light-Lnduced Transformations of 

Methoxychlor in Aquatic Systems. J. Agric. Food Chem. 24(4):727-733. 

Zepp, R.G., N.L. Wolfe, L.V. Azarraga, R.H. Coz, and C.W. Pape. 1977. Photochemical Transformation of the DDT and Methoxychlor Degradation Products, DDE and DMDE, by sunlight. 

Arch. Environ. Contam. Toxicol. 6:305-3 14. 

c-54 
DDE 

OBSERVATIONS AND EFFECTS ON PISCNOROUS WILDLIFE 

The use of the insecticide DDT was severely restricted in the United States in 1972. However, the 

long-lived DDT and its metabolite, DDE, are still present in the tissue and eggs of many fish-eating 

birds. 

The concentration of DDE residue in avian eggs is negatively correlated with reproductive success. 

A study of black-crowned night herons from 1978 to 1980, determined that residues greater than 

1.0 ppm reduce eggshell thickness, and levels greater than 8.0 ppm reduce the percentage of 

successful nests and clutch size and increase the percentage of cracked eggs (Henny et al., 1984). 

Almost 11 percent of eggs collected from night herons in San Francisco Bay in 1982 had 

concentrations of DDE above 8.0 pmm (Ohlendorfet al., 1988). 

For the sensitive brown pelican, a concentration greater than 0.5 ppm in eggs was estimated to cause 

eggshell thinning (Blus, 1972; Blus et al., 1971). From these data, the EPA in 1976 estimated a 

NOEL for the eggs of the brown pelican at 2.0 ppm, with a corresponding dietary NOEL of 0.2 ppm 

(Newell et al., 1987). More recently, the State of New York has also proposed a fish flesh criterion 

of 0.2 ppm DDE to protect all piscivorous wildlife (Newell et al., 1987). 

DDE residues in eggs at concentrations high enough to affect reproductive success were observed 

in herring gull eggs from the Great Lakes between 1974 and 1978 (mean of 21 ppm for a Lake 

Ontario colony in 1974) (Weseloh et aI., 1979). In Maine, differences in DDE concentrations 

observed between the common eider, herring gull, and black-backed gulI were attributed to 

differences in feeding habits (Szaro et al., 1979). The highest concentrations (mean of 8.66 ppm) 

were detected in the eggs of black-backed gulls, which are piscivorous and have also been observed 

to eat carrion of marine mammals. The common eider, with the lowest concentrations (mean of 

0.23 ppm), feeds primarily on marine invertebrates. 

DDE has also been detected in high concentrations (2.9 ppm) in eggs from the American crocodile 

in the Florida Everglades (Hall et al., 1979). 

In birds, the lethal effect of DDE in the brain is estimated to be about 250 ppm (as cited in Ohlendorf 

et al., 1981). Although DDE is often present in the brains of piscivorous birds, it is seldom found 

at levels considered lethal. 

Dead or moribund bald eagles were collected nationwide from 1971 to 1974 and analyzed for 

organochlorine residues. Of the 101 specimens analyzed, DDE was detected in 97 percent of the 

brains. However, only one death could possibly be attributed to DDE (230 ppm) (Barbehenn and 

Reichel, 198 1). 

In 1969 and 1973 in southern Ontario, ring-billed guls found dead of no apparent disease were 

analyzed for organochlorines. Most had DDE residues in the brain, although a lethal level was 

detected in only one specimen (Stickel et al., 1984). 

C-55 
Of 12 adult black-crowned night herons found dead in 1980 and 1981 in Nevada, all had DDE 

residues in the brain. Only one dead immature heron collected did not have a detectable DDE 

residue in the brain (Henny et al., 1984). 

The effects of DDE on piscivorous wildlife are summarized in the following table: 

Effects of DDE Concentrations on Piscivorous Wildlife 

Animal 

Birds 

Brown 

Pelican 

Brown 

Pelican 

Brown 

Pelican 

Black-crowned 

Night-heron 

Piscivorous 

Wildlife 

Source 

250 ppm (brain) death Ohlendorf, 198 1 

9.5 ppm (egg) eggshell 

thinning 

Blus, 1972; 

Blus et al., 1971 

9.0 ppm (egg) eggshell U.S. EPA, 1976 

ti.2 ppm (diet) eggshell 

thinning 

U.S. EPA, 1976 

1 .O ppm (egg) eggshell 

thinning 

Henny et al., 1984 

8.0 ppm (egg) reduced 

clutch size 

reduced percentage 

of successful 

nests 

0.2 ppm (diet) 

0.226 ppm 

(diet) 

increased percentage 

of cracked 

e&Y 

estimated 

NOEL 

cancer risk 

of lo’* 

Henny et al., 1984 

Newell et al., 1987 

Newell et al., 1987 

C-54 
REFERENCES 

Barbehenn, K-R., and W.L. Reichel. 1981. Organochlorine Concentrations in Bald Eagles: 

Brain/Body Lipid Relations and Hazard Evaluation. J. Toxicol. Environ. Health. 8:325-330. 

Blus, L. 1972. Further Analysis of the Logarithmic Relationship of DDE Residues to Nest Success. 

Nature 240: 164. (.As cited in Newell et al., 1987). 

Blus, L.J., R. Heath, C. Gish, A. Belisle, and R. Prouty. 1971. Eggshell Thinning in the Brown 

Pelican: Implication of DDE. Bioscience 21: 1213-1215. (As cited in Newell et al., 1987). 

Hall, R. J., T. E. Kaiser, W. B. Robertson, Jr., and P.C. Patty. 1979. Organochlorine Residues in 

Eggs of the Endangered American Crocodile oocodu acutw. Bull. Environ. Contam. Toxicoi. 

23:87-90. 

Henny, C. J., L. J. Blus, A. J. Krynitsky, and C. M. Bunck. 1984. Current Impact of DDE on 

Black-Crowned Night-Herons in the Jntermountain West. J. Wildl. Manage. 48( 1): 1- 13. 

Newell, A. J., D.W. Johnson, and L.K. Allen. 1987. Niagara River Biota Contamination Project: 

Fish Flesh Criteria for Piscivorous WildIife. Tech. Rep. 87-3. NY Dept. Environ. Conserv., Div. 

Fish Wildl., Bureau Environ. Protection. 

Ohlendorf, H.M., T.in. Custer, R.W. Lowe, M. Rigney, and E. Cromartie. 1988. Organochlorines 

and Mercury in Eggs of Coastal Terns and Herons in California, USA. Colon. Waterbirds 

1 l( 1):85-94. 

Ohlendorf, K.M., D.M. Swineford, and L.N. Locke. 1981. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4) 125-135. 

Stickel, U.K., L.F. Stickel, R.A. Dyrland and D.L.Hughes. 1984. Aroclor 1254 Residues in Birds: 

Lethal Levels and Loss Rates. Arch. Environ. Contam. Toxicol. 13:7-13. 

Szaro, R. C., N. C. Coon, and E. Kolbe. 1979. Pesticide and PCB of Common Eider, Herring Gull 

and Great Biack-Backed GulJ Eggs. Bull. Environm. Contam. Toxicol. 22:394-399. 

U.S. EPA. 1976. Quality Criteria for Water. U.S. Environmental Protection Agency, Washington, 

DC. EPA 440/g-76-023. (As cited in Newell et al., 1987). 

Weseloh, D.V., P. Mineau, and D.J. Hallett. 1979. Organochlorine Contaminants and Trends in 

Reproduction in Great Lakes Herring Gulls, 1974-1978. Trans. N. Am. Wildl. Nat. Resour. Conf. 

44:543-557. 

c-57 
C-58 
DICOFOL 

CAS No.: 115-32-2 

CAS Preferred Nomenclature: 

Benzenemethanol, 4-chloro-.alpha. 

-(J-chlorophenyi)-.alpha.- 

(trichtoromethyl)- 

Empirical Formula: C 14H9Cl50 

Synonyms and Common Names: 

- Kelthane - Carbax 

- Mitigan - CPCA 

- Acarin - Decofol 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Adconsumption of fuh): visories: 

None established at present None established at present 

l EPA Ambient Water Quality Criteria l EPA Tolerance Levels for Food (21 

(for protection of aquatic organisms): CFR 193.80; 40 CFR 185.410): 

None established at present dried tea = 45 ppm 

hops = 30 ppm 

cottonseed = 0.1 ppm 

other foods = 5-10 ppm 

l EPA Drinking Water Standard Maxi- * Food and Drug Administration Action 

mum Contaminant Level: Level for Fish: 

None established at present None established at present 

Use Restrictions and Bans: 

l Effective December 3 1,1988, all uses to be cancelled unless registered formulas contain 

less than 0.1% DDT and related contaminants (5 1 FR 19508). 

c-59 
SOURCES OF DICOFOL 

Total Dicofol Produced: 

l Dicofol is a pesticide structurally similar to DDT which was introduced in 1957. 

Technical-grade dicofol is a brown viscous oil. 

l Recent use in the U.S. is 2 to 3 million pounds per year (Holder, 1986). Dicofol is 

produced by Rohm and Haas, Inc. and Makhteshim-Agan, Inc. (51 FR 19509). 

Uses of Dicofol: 

l Used primarily (60%) to control mites on cotton and citrus. Other major uses include 

the control of mites on apples ( 10%) and on ornamental plants and turf ( 10%) (5 1 FR 

19515). 

9 Another 20% is used for the control of mites on a variety of other agricultural products 

inciuding: 

- pears, apricots and cherries (51 FR 195 15; Farm Chemicals Handbook, 1985) 

- seed crop soil treatment 

- vegetables (e.g., beans and corn) 

- shade trees (U.S. EPA, 1986). 

-: None found. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, dicofol is predicted to be essentially nonvolatile in water (H = 3.5x 1 O-’ atm l m3/mol) and from soil surfaces (P/S& = 4.8x 1 O-l4 

mm Hg l Umg). It is very strongly sorbed to soil and sediment (I& 3 1,148,000), 

and has a high potential for bioaccumulation (BCF = 5.5~10~) (Lyman et al., 1982). 

l Fisher (1975) reported that dicofol and its aerobic soil breakdown products were 

relatively immobile in a column experiment using sandy loam soil. Approximately 93 % 

of radioactivity applied as “C-dicofol and >99% of the total radioactivity accounted 

for remained in the upper 2 inches of a sandy loam soil column after 30 days of aerobic 

aging followed by 44 days of leaching with water at a rate of 0.5 in/day. 

l Tillman (1986) reported a maximum non-steady-state, whole-body BCF of 1.0 x lo4 

and an estimated steady-state whole-body BCF >2.5 x lo4 for bluegill sunfish exposed 

to 0.006 ppm dicofol for 28 days. 

C-60 
Persistence: 

l Dicofol can hydrolyze with the rate increasing as pH increases. For example, Warren 

(1986) reported hydrolysis half-lives for dicofol (at 25°C) of 85 days at pH 5, 64 hours 

at pH 7, and 26 minutes at pH 9. The half-life for dicofol hydrolysis in distilled water 

at pH 8.2 was found to be 1 hour; in filtered river water at pH 7.5. roughly 90% 

conversion of dicofol to 4,4’-dichlorobenzophenone occurred in 24 hours, though 

dicofol recovery was poor (Walsh and Hites, 1979). 

l The photolysis half-life for dicofol was found to be 144 hours in one study using thin 

films (TDB, 1985). However, studies using water and soil solutions reported longer 

half-lives. For example, Carpenter (1986a) reported a relatively long photodegradative 

half-life of ~37 days for dicofol in water exposed to artificial light with wavelengths > 

290 nm. Carpenter (1986b) reported an intermediate photodegradative half-life between 

21 and 30 days for dicofol adsorbed to a silt loam soil when exposed to these same 

conditions. Dicofol appears to be poorly metabolized by microbes in aerobic soil 

systems (Walsh and Hites, 1979). It has been found to undergo degradation in anaerobic 

sewage sludge, however (Verschueren, 1983). 

HEALTH EFFECTS 

Carcinogeuicity: 

l Technical-grade dicofol (containing an undetermined level of DDT) induced hepatocellular (liver) carcinomas in male mice. Resuits were negative in female mice as well as 

in rats (NC], 1978). 

l Dicofol is classified by the U.S. EPA as a possible human carcinogen (Class C) with 

only limited animal evidence supporting the classification (Holder, 1986). 

l Because it is structurally related to DDT and there is a large data base supporting the 

carcinogenicity of DDT, it has been suggested that difocol be classified somewhere 

between C and B2 (as a probable human carcinogen). Further study is necessary to 

determine the conect classification (Holder. 1986). 

Mutagenic Activity: 

l Additional studies need to be done to determine whether dicofol causes mutagenic 

effects (Holder, 1986). 

+ Negative results were reported for induction of chromosomal aberrations in Chinese 

hamster lung cells and for bacterial tests (IARC, 1983). 

l Positive results were noted in a micronucleus test with rat bone marrow cells (IARC, 

1983). 

C-61 
Reproductive Effects: 

. In a multi-generation mouse study there were no effects on reproduction or fetal 

development (IARC, 1983). 

l With rats, dicofol influenced only early (pre-implantation) embryo development (IARC, 

1983). 

Other Toxicological Effects: 

l Although no symptoms of toxicity were demonstrated in dogs fed 300 ppm for one year, 

two of the four test animals died before completion of the experiment (Clayton and 

Clayton, 198 1). 

l Report of possible suppression of adrenal function (Clayton and Clayton, 1981). 

ToxicologicaI Effects Indices: 

l Estimated cancer potency factor (CPF): = 0.44 (mg/kg/day)-1 (Holder, 1986). 

l The U.S. EPA Carcinogen Assessment Group recommends the use of a CPF of 0.34 

(mg/kg/day)-’ for any combination of dicofol, DDT, DDE, and DDD (Holder, 1986). 

l Occupational exposure to DDT should be limited to 1 mg/m3 (ACGIH, 1986). 

l Oral LDso: rats, between 575 and 1,000 mg/kg (McEwen and Stephenson, 1979; 

Worthing, 1983; Matsumura, 1985). 

c-62 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular weight: 

Physical State @ 2O*C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H 

@ 25°C (atm . m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log I&: 

Soil Adsorption Coefficient, Koc (mL/g): 

Fish Bioconcentration Factor, BCF: 

370.5 

Colorless solid; 

technical grade, 

brown viscous oil 

78.5-79.5 

180 @ 0.098mm Hg 

technical grade, 

1.45 @ 25*C 

N/A 

0.8 (20’0 

5.8x 1O-9 (talc.) 

3.5x1o’9 (talc.) 

6.06 (talc.) 

1.5x 105 (talc.) 

5.5x104 (talc.) 

1 .0x104 to >2.5x104 (est.) 

Sax, 1984 

Kirk-Othmer, 1984; 

Matsumura, 1985 

Hartley & Kidd, 1983 

Hartley & Kidd, 1983 

Hartley & Kidd, 1983 

Verschueren, 1983 

Lyman et al.. 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Tillman, 1986 

c-63 
REFERENCES 

ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Carpenter, M. 1986a. Aqueous Photolysis of “C-p,p’-dicofol (Kelthane). Prepared by Analytical 

Bio-Chemistry Laboratories for Rohm and Haas. TR No. 310-86-58. 

Carpenter, M. 1986b. Photodegradation of 14C-p,p’-dicofol on the Surface of Soil. Prepared by 

Analytical Bio-Chemistry Laboratories for Rohm and Haas. TR No. 310-86-58. 

Clayton, G.D., and F.E. Clayton, eds. 1981-82. Patty’s Industrial Hygiene and Toxicology. 3rd 

rev. ed., Vol. 2A. 2B, 2C, Toxicology. John Wiley and Sons, New York. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Fisher. J.D. 1975. Laboratory Leaching Study With Soil-aged Kelthane. Rohm and Haas Co. Tech. 

Report No. 3423-75-50. 

Hartley, D., and H. Kidd, eds. 1983. The Agrochemicals Handbook. The Royal Society of 

Chemistry, Nottingham, England. 

Holder, J.W. 1986. The Assessment of the Carcinogenicity of Dicofol (Kelthane), DDT, DDE and 

DDD (TDE). U.S. Environmental Protection Agency, Carcinogen Assessment Group. EPA/600/6- 

86/00 1. 

IARC (International Agency for Research on Cancer). 1983. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 30. IARC, Lyon, France. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1984. 3rd. ed. John Wiiey and Sons, Inc., 

New York. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book, Co., New York. 

Matsumura, F. 1985. Toxicology of Insecticides. Plenum Press, New York. 

McEwen, F.L., and G.R. Stephenson. 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, Inc., New York. 

NC1 (National Cancer Institute). 1978. Bioassay of Dicofol for Possible Carcinogenicity. NC1 

Carcinogenesis Tee hnical Report Series, No. 90. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhotd Co., 

New York. 

C-64 
Tillman. A.M. 1986. The Bioconcentration, Elimination, and Metabolism of 14CDicofol by 

Bluegill Sunfish (LeDomis. Rohm and Haas Co. Report No. 3 10-86-17. 

Toxicology Data Bank (TDB) Database. 1985- 1986. Available through the National Library of 

Medicine’s MEDLARS system, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1983. Guidance for the Reregistration of Pesticide Products Containing Dicofol as the 

Active Ingredient. 540-RS-83-003. 

U.S. EPA. 1985. Suspended, Cancelled, and Restricted Pesticides. U.S. Environmental Protection 

Agency, Office of Pesticides and Toxic Substances, Washington, DC. 

U.S. EPA. 1986. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York. 

Walsh, P.R. and R.A. Hi&. 1979. Dicofol Solubility and Hydrolysis in Water. Bull. Environ. 

Contam. Toxicol. 22:305-3 11. 

Warren, J. 1986. Hydrolysis of 14C-p,p’-dicofol (Kelthane). Prepared by Analytical BioChemistry Laboratories for Rohm and Haas. Report No. 310-86-41. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 
c-66 
DELDRIN 

CAS No.: 60-57- 1 

CAS Preferred Nomenclature: 

2,7:3,6-Dimethanonaphth(2,3b)oxirene, 

3,4,5,6,9,9-hexachloro-la,2,2a,3,6,6a,7,7,7aoctahydro-,(la ,2 p,2 or,3p ,6p ,6acx ,7p ,7a 

Empirical Formula: C t2H8C 160 

Synonyms and Common Names: 

- Dieldrex - 1110x01 

- HEOD - octalox 

REGULATORY STATUS 

Standards and Ctiterla: 

l EPA Water Quality Criteria (for human 

consumption of fish) for a 10e6 cancer 

risk (50 FR 793 18): 

0.076 mg/L 

l 

l EPA Ambient Water Quality Criteria . 

(for protection of aquatic organisms) 

(U.S. EPA, 1980): 

Freshwater Saltwater 

Acute, kg/L 2.5 0.71 

chronic, pg/L 0.0019 0.0019 

l EPA Drinking Water Standard Maxi- . 

mum Contaminant Level: 

None established at present 

* 

Cl 

0 

Cl 

H Cl 

EPA Drinking Water Health Advisories (U.S. EPA, 1988; ATSDR, 

1987): 

M (10 kg): 

1 -day, 1 O-day, longer-term 

exposures = 0.5 @L 

ii&U Ukg): 

longer-term exposure = 2 PgL 

Food and Drug Administration Action 

Level for Fish, total aldrin and dieldrin 

(55 FR 14361): 

0.3* ppm 

Food and Drug Administration Action 

Levels for Other Foods (55 FR 14361): 

0.02 - 0.3* ppm 

FDA Action Levels are for use in 

interstate commerce 

c-47 
Use Restrictions and Bans: 

l Suspension of uses on food products in 1974 (ATSDR, 1987). 

l All uses banned in 1985 except for subsurface termite control, dipping of nonfood roots 

and tops, and moth proofing in a closed system by manufacturing processes (U.S. EPA, 

1985). These uses have been voluntarily cancelled by industry (ATSDR, 1987). 

SOURCES OF DIELDRIN 

Total Dieldrin Produced: 

l In 1970 about 670,000 pounds were used. Dieldrin is no longer produced in the U.S. 

Until 1985, products containing dieldrin were imported from Europe. None have been 

imported since then. 

Uses of Dieldrin: 

l Dieldrin is an organochlorine pesticide that was widely used from 1950 to 1974 for 

controlling soil-dwelling insects, especially termites, on cotton, corn, and citrus crops. 

l Uses prior to 1974 included the following (Worthing, 1983): 

- Control of locusts 

- Control of tropical disease carriers (e.g., mosquitoes) 

- Wood preservative 

- Termite control for electrical cables and buildings 

- Moth proofing woolen clothes and carpets. 

Other Sources: 

l Breakdown product (by oxidation) of the pesticide aldrin (Verschueren, 1983) 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, dieldrin has a low volatility (H = 2~10’~ 

atm l m3/mol), sorbs readily to soil organic matter (Kow = 20,890), and has a high 

potential for bioaccumulation (BCF = 4,670). 

C-68 
Persistence: 

l Dieldrin can undergo hydrolysis under neutral pH conditions (Kn = 7.5x 10-6/mole/hr). 

but the half-life is long (10.5 years) (Ellington, et al., 1986). Direct photolysis ofdieldrin 

can also occur; the half life is about 2 months (Callahan, et al., 1979). 

l Dieldrin can be biotransformed very slowly by soil microbes to an epoxide that is more 

toxic to some insects than the parent compound. Further degradation results in the 

ketone-aldrin, an aldehyde and alcohols (Merrill et al., 1982). Under aerobic conditions, 

dieldrin can be degraded to 6,7-trans-dihydroxydihydroaldrin (Kirk-Othmer, 1978). 

HEALTH EFFECTS 

Carcinogeuicity: 

l Dieldrin has caused liver carcinoma in feeding studies (oral administration) with five 

strains of male and female mice (50 FR 10080). The EPA has classified dieldrin as a 

B2, probable human carcinogen, IARC classification 2b. (IARC, 1982; PHRED, 1988): 

Mutagenic Activity: 

l Mutagenic in human lung cells in culture. Interferes with metabolic cooperation in 

cultured cells (i.e., it promotes mutagenic activity). Negative in mouse dominant lethal 

test, Salmonella. yeast and Drosow (fruit flies). Inconclusive data on chromosome 

damage to mouse bone marrow cells (IARC, 1982). 

Reproductive Effects: 

l In hamsters, high doses of dieldrin exposure resulted in fetal deaths, congenital defects 

and retarded growth (Proctor and Hughes, 1978). 

l Decreased fertility in rats and mice; increased postnatal mortality in rats (ATSDR, 1987). 

Other Toxicological Effects: 

l Identified as a neurotoxin (Clayton and Clayton, 1981). The acute affects can include: 

headache, dizziness, hyperexcitability, tremors, convulsions, depression and death 

(ATSDR, 1987). 

l Chronic effects: damage to liver in rats, dogs, and hamsters, also evidence of suppressed 

immune systems (Gosselin et al., 1984). 

l Low levels decreased learning capabilities in monkeys (50 FR 10080). 

C-69 
Todcolo@cal Effects Indices: 

l Cancer potency factor (CPF): 16 (mg/kg/day)“ (U.S. EPA, 1987a). 

l Reference Dose (Rfl>): 5~10.~ mg/kg/day (U.S. EPA, 1987b). 

l TLV-TWA (time-weighted average, threshold limit value) for occupational skin exposure: 0.25 mg/m’ (ACGIH, 1986). 

l LD50 in humans, approximately 5 mg/kg (ATSDR, 1987). 

l Oral LD~o: rats, 46 mgkg (Sax, 1984). 

l Tolerance levels for agricultural commodities: 0 to 0.1 ppm (ATSDR, 1987). 

c-70 
PHYSICAWCHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25OC (atm . m3/mol): 

Hydrolysis, &I, UmolIhr 

380.9 

solid; buff to light 

tan flakes; mild odor 

175-176 

N/A 

1.75 

N/A 

0.186 (2OOC) 

3.1x10” 

2x 1 o-7 (2OOC) 

7.5x10” 

Windholz, 1983 

Worthing, 1983 

Callahan et al., 1979 

Verschueren, 1983 

Callahan et al., 1979 

Callahan et al., 1979 

U.S. EPA, 1986b 

Ellington et al., 

1986 

Log (Octanol-Water Partition 

Coefficient), log I&W: 

Soil Adsorption Coefficient, 

KocWJg): 

Fish Bioconcentration Factor, BCF: 

4.32 Leo, 1983 

1700 Mabey et al., 1982 

4670 U.S. EPA, 1980 

c-71 
REFERENCES 

ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for Aldrin./Dieldrin. ATSDR, U.S. Public Health Service. 

Callahan, M.A., M.W. Slimak, NW. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. Office of Water Planning and Standards, 

U.S. Environmental Protection Agency, Washington, DC. EPA-440/4-79-029a. 

Clayton, G.D., and F.E. Clayton, eds. 1981-82. Patty’s Industrial Hygiene and Toxicology. 3rd 

rev. ed.. Vol. 2A, 2B, 2C. Toxicology. John Wiley and Sons, Inc., New York. 

Ellington, J.J., F.E. Stancil, Jr. and W.D. Payne. 1986. Measurement of Hydrolysis Rate Constants 

for Evaluation of Hazardous Waste Land Disposal. Vol. I. U.S. Environmental Protection Agency, 

Athens, GA. EPA Report No. EPA/600/3-861043. 

Goss&t, R.E., R.P. Smith, H.C. Hodge, and J.E. Braddock. 1984. Clinical Toxicology of 

Commercial Products. 5th ed. The Williams and Wilkins Co., Baltimore. 

IARC (International Agency for Research on Cancer). 1982. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Suppl. 4. IARC, Lyon, France. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1978. 3rd Ed. John Wiley and Sons, Inc., 

New York. 

Leo, A.J. 1983. Log P Parameter Database, Pomona College, Claremont, CA. 

Mabey, W .R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. Mill, T.W. Chou. J. Gates, J.W. Partridge, 

H. Jaber. and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440/4-8 l-014, 

Merrill, L.G., B.C. Mahilum, and S.H. Mohiuddin. 1982. Organic Compounds in Soils: Sorption, 

Degradation and Persistence. Ann Arbor Science Publishers, Inc., Ann Arbor, MI. p. 187-238. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

Proctor, NH., and J.P. Hughes. 1978. Chemical Hazards of the Workpface. Lippincott Company, 

Philadelphia. 

C-72 
Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold Co.. 

New York. 

Sittig. M., ed. 1980. Pesticide Manufacturing and Toxic Materials Control Encyclopedia. Noyes 

Data Corp., Park Ridge, NJ. 

Toxicology Data Bank (TDB) Database. 1985- 1986. Available through the National Library of 

Medicine’s MEDLARS system, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1976. Quality Criteria for Water. U.S. Environmental Protection Agency, Office of 

Water and Hazardous Materials, Washington, DC. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Aldrin/Dieldrin. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA 440/5-80-019. 

U.S. EPA. 1985. Suspended, Cancelled, and Restricted Pesticides. U.S. Environmental Protection 

Agency, Office of Pesticides and Toxic Substances, Washington. DC. 

U.S. EPA. 1986a. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

U.S. EPA. 1986b. Super-fund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

U.S. EPA. 1987a. Carcinogenicity Assessment of Aldrin and Dieldrin. U.S. Environmental 

Protection Agency, Carcinogen Assessment Group, Washington, DC. EPA/600/6-87/006. 

U.S. EPA. 1987b. Draft RCRA Facility Investigation (RFI) Guidance. U.S. Environmental 

Protection Agency, Office of Solid Waste, Washington, DC. EPA-530/SW-87-001. 

U.S. EPA. 1988. Dieldrin - Health Advisory. U.S. Environmental Protection Agency, Office of 

Drinking Water, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold Co., New York. 

Windholz, M. ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 

Merck and Co., Rahway, NJ. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-73 
DIELDRIN 

OBSERVATIONS AND EFFECTS ON PISCJYOROUS WILDLIFE 

The concentration of dieldrin in the brain determined to cause death in several bird species appears 

to be quite low. The average level that put the animal at risk of death is between 5 and 9 ppm 

(Ohlendorf et al. 1981 and Stickel et al. 1972). A concentration of 6.8 ppm was determined to be 

the average level lethal to birds from several laboratory studies (Heinz and Johnson, 1981). 

However, levels as low as 1 ppm in the brain may trigger irreversible starvation in sensitive 

individuals (Heinz and Johnson, 1981). During starvation, mobilization of low concentrations of 

dieldrin from body fats to the brain may cause death, after concentrating to a lethal level (Newell 

et al., 1987). 

Dieldrin is commonly found in the brain, tissues, and eggs of fish-eating birds that also have residues 

of organochlorines such as DDE and PCBs. Die&in was the apparent cause of death for several 

ring-billed gulls in southern Ontario in 1969 and 1973. Stickel et ai. (1984) analyzed 54 gulls that 

had died of no apparent disease. Of these birds, eight specimens had dieldrin levels in the brain 

greater than 5 ppm. The cause of death in many of the other gulls was most likely PCB 

contamination (Stickel et al., 1984). 

From 197 1 to 198 1.10 1 dead or dying bald eagles were collected and analyzed for organochlorines. 

Based on the data provided, four eagles had died from lethal concentrations of dieldrin (concentrations near 5 ppm in the brain) (Barbehenn and Reichel, 1981). 

In a nationwide survey of 72 species of heron found dead or moribund between 1966 and 1973.10 

specimens had greater than 5 ppm in the brain and had possibly died of die&n poisoning. Eight 

others had concentrations of dieldrin greater than 2.0 ppm in the brain (Ohlendorf et al., 198 1). 

Based on a number of studies in the literature, the State of New York proposed a dietary fish flesh 

criterion of 0.12 ppm to protect piscivorous wildlife (Newell et al., 1987). 

The effects of die&in on piscivorous wildlife am summarized in the following table: 

c-74 
Effects of Dieldrin Concentrations on Piscivorous Wildlife 

Animal 

Birds 

Birds 

Birds (sensitive 

individuals) 

Piscivorous 

Wildlife 

cone5 ppm (brain) death Stickel et al., 

1972 

6.8 ppm death Heinz and 

Johnson, 1987 

1.0 ppm (brain) irreversible 

starvation 

Heinz and 

Johnson, 1987 

0.12 ppm (diet) 

0.022 ppm (diet) 

estimated NOEL 

cancer risk of 

lO’2 

Newell et al. 

1987, 

Newell et al., 

1987 

REFERENCES 

Barbehenn, K.R., and L. Reichel. 198 1. Organochlorine Concentrations in Bald Eagles: 

Brain/Body Lipid Relations and Hazard Evaluation, 3. Toxicol. Environ. Health 8:325-330. 

Heinz, G. and R. Johnson. 1981. Diagnostic Brain Residues of Dieldrin: Some New Insights. 

Avian and Mammalian Wildlife Toxicology: Second Conference, ASTM STP 757, D. Lamb and 

G. Kenaga, eds., American Society of Testing and Materials, pp. 72-92. (As cited in Newell et al., 

1987) 

Newell, A.J., D.W. Johnson, and L.K. Allen. 1987. Niagara River Biota Contamination Project: 

Fish Flesh Criteria for Piscivorous Wildlife. Tech. Rep. 87-3. NY Dept. Environ. Conserv., Div. 

Fish inildl., Bureau Environ. Protection. 

Ohlendorf, K.M., D.M. Swineford, and L.N. Locke. 198 1. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4):125-135. 

Stickel, W.H., L.F. Stickel, R.A. Dyrland and D.L. Hughes. 1984. Aroclor 1254 Residues in Birds: 

Lethal Levels and Loss Rates, Arch. Environ. Contam. Toxicol. 13:7- 13. 

Stickel, W.H., L.F. Stickel and J. Spann. 1972. Tissue Residues of Dieldrin in Relation to Mortality 

in Birds and Mammals. In Chemical Fallout: Current Research on Persistent Pesticides, ed., M.W. 

Miller and G.G. Berg. Charles C. Thomas publisher, Springfield, USA. 

c-75 
C-76 
DIPHENYL DISULFIDE 

CAS No.: 882-33-7 

CAS Preferred Nomenclature: 

Disulfide, diphenyl 

Empirical Formula: C 12H toS2 

C H S 

Synonyms and Common Names: 

- Phenyl disulfide 

12 10 2 

REGULATORY STATUS 

4 No use restrictions or regulatory standards. 

SOURCES OF DIPHENYL DISULFIDE 

Total Diphenyl Disulfide Produced: 

l Manufactured by Parish Chemical Co., less than 23,000 pounds of diphenyl disulfide 

were produced in 1982 (Perwak et al., 1983; SRI, 1986). 

Uses of Diphenyl Disulfide: 

l Diphenyl disulfide is used primarily as a flavoring agent in nonalcoholic beverages, ice 

cream, candy, gelatin, and pudding (Perwak et al., 1983). 

l Small amounts are used in the pharmaceutical industry and as a vulcanizing agent in the 

manufacture of rubber (Perwak et al., 1983). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on measured properties and structure-activity relationships, diphenyl disulfide 

can volatilize at a low rate (H = 7.6~10’~ atm l m3/mole) and has a moderately strong 

tendency to sorb to soil (I&&5,700). 

c-77 
Persistence: 

l Little information is available on transformation processes in the environment. 

Hydrolysis and biodegradation are not expected to occur at environmentally significant 

rates (Perw* et al., 1983). 

HEALTH EFFECTS 

Carcinogenicity: 

l The U.S. EPA has not evaluated the potential carcinogenicity of diphenyl disulfide. 

Other Toxicologkal Effects: 

. There are no reports of adverse health effects caused by diphenyl disulfide in either 

animals or humans. 

Toxicological Effects Idims: 

l Intraperitoneal LDso: mice, 100 mg/kg (Tatken and Lewis, 1983). 

C-78 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, P&I: 

Water Solubiiity, S (mg/L): 

VaporPresure, P (mm Hg): 

Henry’s Law Constant, H @ 25 OC 

(atm l m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log F&: 

Soil Absorption Coefficient, K&mug): 

Fish Bioconcentration Factor, BCF: 

218.3 

solid 

61-62 

310 

1.353 

N/A 

5.1 

i.4xlO~ 

7.6x10d Lyman, et al., 1982 

4.41 Leo, 1983 

7900 Lyman, et ai., 1982 

1200 (talc.) Lyman, et al., 1982 

Weast, 1986 

Weast, 1986 

Weast, 1986 

Weast 1986 

Lyman, et al., 1982 

Lyman, et al., 1982 

c-79 
Leo. A.J. 1983. Log P Parameter Database. Medchem Project, Pomona College, Claremont, CA. 

Lyman, W.J.. W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Co. 

Perwak. 1.. E. Cole, S. Coons, N. Green, W. Lyman, M. Miller, J.H. Ong, and K. Scow. 1983. 

Evaluation of Waterborne Exposure Pathways to Paragraph 4(c) Pollutants. U.S. EPA Draft Report. 

EPA Contract 68-O l-5949. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Tatken, R.L. and R.J. Lewis, eds. 1983. Registry of Toxic Effects of Chemical Substances 

(RTECS). 198 l-82 ed. 

Weast, R.C., ed. 1986. CRC Handbook of Chemistry and Physics. 67th ed. CRC Press, Boca 

Raton, FL. 

C-80 
ENDRIN 

CAS No.: 72-20-8 

CAS Preferred Nomenclature: 

2,7,3,6-Dimethanonaphth(2.3b)oxirene. 

3,4,5,6,9,9-hexachloro-la, 

2,2a,3,6,6a,7,7aoctahydroEmpirical Formula: C 12HcbO 

Synonyms and Common Names: 

- Endrex - Insecticide 269 

- Endriocol - Mendrin 

- Hexadrin - Oktanex 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of water and fish) 

(PHRED, 1988): 

1 ML 

l EPA Ambient Water Quality Criteria . 

(for protection of aquatic organisms) 

(U.S. EPA, 1980): 

Freshwater SaItwater 

Acute, pg/L 0.18 0.0023 

Chronic, pg/L 0.037 0.0023 

* 

EPA Drinking Water Health Advisories (U.S. EPA, 1989): 

w( 10 kg): 

l-day exposure = 20 pg/L 

lo-day exposure = 20 ug/L 

longer-term exposure = 3 pg/L 

adult(70 kg): 

longer-term exposure = 10 pg/L 

lifetime exposure = 2 PgiL 

Food and Drug Administration Action 

Level for Fish (FDA, 1986 and 52 FP 

18025): 

0.3* ppm 

Action Level for Other Foods: 

0.02 to 0.3* ppm 

FDA Action Levels are for use in interstate commerce 

l EPA Drinking Water Standard Maximum Contaminant Level: (40 CFR 

141.12): 

0.0002 mg/L 

C-81 
Use Restrictions and Bans: 

l Endrin is an organochlorine compound originally registered as a pesticide in 195 1. It 

was used to control a wide variety of pests until its long-term persistence in soils and 

high levels of mammalian toxicity were recognized. 

l In 1964, the high level of endrin persistence in soils led to cancellation of its use on 

tobacco (Sittig, 1980; U.S. EPA, 1980). 

. By 1979, specified uses on cotton, small grains, apple orchards, sugarcane, and omamentals were also restricted (44 PR 43632). 

l In 1984, the sole remaining producer of endrin voluntarily requested cancellation of 

registration of all emit-in products. This action effectively ended its use in the U.S. (U.S. 

EPA, 1984). 

SOURCES OF ENDRIN 

Total Endrin Produced: 

l Endrin was fust used in the U.S. in 1951. By 1971, approximately 1 million pounds of 

endrin were produced by Velsicol (Ouellette and King, 1977). 

l Endrin production had decreased to 400,000 pounds by 1978 (U.S. EPA, 1978). 

Uses of Endrin: 

l Emit-in is a broad spectrum pesticide and has been used to control many pests, including 

termites, mice and army worms. 

l Prior to 1979, the main domestic use of endrin was for the control of cotton bollworms 

(an insect larva) which attack cotton crops in the southeastern and Mississippi delta 

States (U.S. EPA, 1980). 

l Registered uses of endrin included foliar treatment for citrus, potatoes, barley, oats, rye, 

wheat, cotton, apple orchards, sugarcane, and various flowers and bark treatment for ash 

and hackberry trees (U.S. EPA, 1986). 

l En&in has also been used to control pest populations of birds and rodents (U.S. EPA, 

1980). 

Other Sources: 

l Isodrin may be metabolically converted to e&in (Matsumura, 1985). 

l Endrin is also found in the pesticide dieldrin in small quantities (Verschueren, 1983). 

C-82 
FATE IN ENVIRONMENT 

Partitionine: 

9 Based on its physical/chemical properties, endrin is strongly sorbed to organic matter 

(KCW =219,000) and volatilizes slowly from water (H = 4x lo-’ atm . m3/mol). It 

volatilizes from soils even slower with an estimated half-life of 34 days (p/S& = 

4.7x10-l’ mm Hg* Umg). Bioaccumulation is an important fate process; bioconcentration factors are moderately high to very high, ranging from 6.8~10~ to 1.3~10~ in 

microcosm experiments (Callahan et al., 1979; Lyman et al., 1982). 

Persistence: 

l Endrin is very resistant to hydrolysis (half-life over 4 years). Photolysis of endrin in 

hexane has been documented. No data concerning the photolysis rate of endxin in the 

aqueous environment were found. A half-life of about 7 days was observed when endrin 

was applied to a sandy loam soil and exposed to sunlight (Shell Chemical Co., 1975). 

l End.& can undergo biotransformation. Guenzi (1974) reported a biodegradation loss 

rate of 4-58 per year over 14 years. 

HEALTH EFFECTS 

Cardnogenidty: 

l No evidence of endrin carcinogenicity has been reported (U.S. EPA, 1980). Treon et 

al. (1955) reported that the incidence of cancers in rats fed endrin for 2 years was no 

greater than that in control rats. 

l A National Cancer Institute bioassay determined no carcinogenic effects in rats or mice 

(NCI, 1979). 

l The U.S. EPA has classified endrin as a Class D carcinogen (inadequate evidence of 

carcinogenicity in animals). 

Mutagenic Activity: 

l Conflicting results have been reported for e&in mutagenicity. Dikshith and Dana 

(1972) reported chromosomal aberrations and cellular degeneration in rat testes. However, negative results for endrin have been recorded with the mouse dominant lethal test 

(TDB, 1984). 

C-83 
Reproductive Effects: 

l Pregnant ratsand mice fed endrin showed reduced fetal survival rates (Noduet al., 1972). 

Endrin-exposed mouse fetuses had a higher incidence of club feet. 

l Endrin produced embryocidal and teratogenic effects in pregnant hamsters. Single doses 

of endrin (5 mgkg) resulted in increased fetal death, congenital abnormalities (i.e., eye 

deformities, cleft palate, and fused ribs), and growth retardation. Lower doses (1.5 to 5 

mg/kg) did not cause similar effects (Ottolenghi et al., 1974; Chemoff et al., 1979). 

Other Toxicologkal Effects: 

l Regardless of the method of exposure, endrin, like the related compounds aldrin and 

die&in. is highly toxic to humans (Matsumura. 1985). In one animal study endrin was 

shown to be five times as toxic as dieldrin (U.S. EPA, 1980). 

l Primarily, the central nervous system is affected with acute (short-term, high-dose) 

poisoning by endrin. A range of symptoms can be caused, including dizziness, nausea, 

confusion, hyperexcitability, generalized tremors or twitching, and convulsions. Death 

from respiratory failure may also occur (U.S. EPA, 1980; Sax, 1984). 

l In rats and dogs chronic (long-term, low-dose) exposure to endrin has led to poor survival 

rates and degenerative changes in the liver, kidneys, and brain (U.S. EPA, 1980). 

l Chronic human exposure to endrin (e.g., in the production of the pesticide) was not 

shown to cause adverse health effects (Jager, 1970). 

Toxicological Effects Indices: 

. Reference Dose (RfD): 3~10~ mg/kg/day (U.S. EPA, 1989). 

l TWA-TLV (time-weighted average, threshold limit value) for occupational skin exposure: 0.1 mg/m3 (ACGM, 1986). 

l Oral LD50: rats, 3-43 mg/kg; rabbits, 7-10 mgkg; monkeys, 3 mgkg (U.S. EPA, 1980; 

Sax, 1984; Matsumura, 1985). 

C-84 
PHYSICAL/CHEMICAL PROPERTIES 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

380.9 

white crystalline 

solid; technical 

grade, light tan 

powder 

Decomposition 

above200"C 

Windholz, 1983 

Matsumura, 1985 

U.S. EPA, 1980 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L,): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H @ 

25OC (arm l m3/moie): 

Log (Octanol-Water 

Partition Coefficient), log I&: 

N/A 

1.7 @ 2o”c 

N/A 

0.25 (25OC) 

2x10" (25OC) 

4x10-’ 

3.54 

U.S. EPA, 1980 

Callahan et al., 1979 

Callahan et al., 1979 

Mabey et al., 1982 

Leo, 1983 

Soil Adsorption Coefficient, I& (mug): 1.7xlOj PHRED, 1988 

Fish Bioconcentration 

Factor. BCF: 6.8x102 to 

1 .3x104 

Verschueren et al., 

1983; Callahan et al., 

(expW 1979 

1480 PI-RED, 1988 

3970 U.S. EPA, 1980 

C-85 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Callahan, M.A., M.W. Shimak, N.W. Gabel, I.P. May,C.F. Flowler, J.R. Freed, P. Jennings, R.L. 

Durice, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould, 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. 1. Office of Planning and Standards, U.S. 

Environmental Protection Agency. EPA-4401479-029a. 

Chemoff, N. et al., 1979. Perinatal Toxicity of Endrin in Rodents. I. Fetotoxic Effects of Prenatal 

Exposure in Hamsters. Submitted to Toxicol. Appl. Pharmacol. and the U.S. Environmental 

Protection Agency (Manuscript). 

Emerson, T.E. et al., 1964. Cardiovascular Effects of the Insecticide Endrin Can. Jour. Physiol. 

Pharmacol. 4214 1. 

FDA. 1986. NSSP Manual, Part 1, Appendix C. U.S. Food and Drug Administration, Washington, 

DC. 

Guenzi, W.D., ed. 1974. Pesticides in Soil and Water. Soil Science Society of America, Inc. 

Madison, WI. 

Jager, K.W. 1970. Aldrin, Dieldrin, Endrin and Telodrin: An Epidemiological and Toxicological 

Study of Long-Term Occupational Exposure. Elsevier Publ. Co., Amsterdam, The Netherlands. 

Leo, A.J. 1983. Log P Parameter Database, Issue #24 (dated Dec. 16, 1983). Obtained from the 

Medchem Project, Pomona College, Claremont, CA. 

Lyman, W.J., W.F. Reehl and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw Hill Book Co. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. Mill, T.W. Chou, J. Gates, J.W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440/4-8 1-O 14. 

Matsumura, F. 1985. Toxicology of Insecticides. Plenum Press, New York. 

NC1 (National Cancer Institute). 1979. Bioassay of Endxin for Possible Carcinogenic&y. DHEW 

Pub. No. (NIH) 79-812. U.S. Department of Health, Education and Welfare, Bethesda, MD. 

Nodu et al. 1972. Influence of Pesticides on Embryos. On the Influence of Organochloric 

Pesticides. Oyo Yakuri. 6:673. (Jap.) 

C-86 
Ottolenghi, A.D. et al., 1974. Teratogenic Effects of Aldrin, Dieldrin, and Endrin in Hamsters and 

Mice. Teratology 9: 11. 

Ouellette, R.P.. and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co., New York. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response; Washington, DC. 

Reins, D.S., et al. 1966. Effect of Endrin on Venous Return and Catecholamine Release in the 

Dog. Can. Jour. Physiol. Pharmacol. 4459. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold Co., 

New York. 

Shell Chemical Company. 1975. Photodegradation of Endrin on Soil. Experimental Data submitted to the U.S. Environmental Protection Agency. 

Sittig, M., ed. 1980. Pesticide Manufacturing and Toxic Materials Control Encyclopedia. Noyes 

Data Corp., Park Ridge, NJ. 

Toxicology Data Bank (TDB) Database, 1985-86. Available through the National Laboratory of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

Treon, J.F., et al. 1955. Toxicity of Endrin for Laboratory Animals. Agric. Food Chem. 3:842. 

U.S. EPA. 1978. Endrin-Position Document 2/3. U.S. Environmental Protection Agency, Office 

of Pesticide Programs, Special Pesticide Review Division, Washington, DC. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Endrin. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Washington, DC. EPA-440/5-80-047. 

U.S. EPA. 1984. Jntemal Office of Pesticide Programs memorandum from G. La Rocca to B. 

Bumam et ai., August 16, 1984. 

U.S. EPA. 1986. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

U.S. EPA. 1989. Health Effects Assessment Summary Tables (HEAST). U.S. Environmental 

Protection Agency; Environmental Criteria and Assessment Office, Cincinnati, OH. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold Co., New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck Co., Inc., Rahway, NJ. 

C-87 
ENDRIN 

OBSERVATIONS AND EFFECTS ON PISCIVOROUS WILDLIFE 

Endrin is lethal to birds at very low concentrations. In the brain, concentrations of only 0.8 ppm or 

more result in death. Levels between 0.6 ppm and 0.8 ppm are hazardous may result in death (Stickel 

et al., 1979). 

During 1975 and 1976, 12 of 15 dead white pelicans collected from refuges in northern California 

had lethal levels of endrin in the brain (0.74 to 2.7 ppm). Stickel et al. (1979) blamed these deaths 

on the presence of endrin in the agricultural return flows entering the refuges. 

White pelicans were also found dead with high levels of endrin near the Teton Dam disaster of 1976. 

On the Gulf Coast of Louisiana, both white and brown pelicans were found dead with endrin present 

in the brain (Stickel et al., 1979). 

Ohlendorf et al., (1981) recorded lethal levels of endrin in the brain of one heron from Minnesota 

in 1972, and one from Wisconsin in 1978. Bald eagles with lethal levels of endrin were found in 

Iowa in 1977 and in Minnesota in 1976 (Stickel et al., 1979). 

The endrin concentration in eggs appears to affect hatching success. For the brown pelican, Blus et 

al. (1979) estimated that concentrations of greater than 0.5 ppm in the eggs caused reproductive 

impairment (as cited in Newell et al., 1987). Pelican eggs from Louisiana during 1972 to 1974 

commonly contained 0.5 ppm endrin (Stickel et al., 1979). 

Based on data from several laboratory studies, the State of New York proposed a dietary fish flesh 

criterion of 0.025 ppm endrin to protect piscivorous wildlife (Newell et al., 1987). 

The effects of endrin on piscivorous wildlife are summarized in the following table: 

C-88 
Effects of Endrin Concentrations on Piscivorous Wildlife 

Animal 

Bird 0.6 - 0.8 ppm 

(brain) 

Bird 0.8 ppm (brain) 

Brown Pelican 0.5 ppm (egg) 

Piscivorous 

Wildlife 

0.025 ppm (diet) 

hazardous 

death 

reproductive 

impairment 

estimated NOEL 

REFERENCES 

Stickel et al., 

1979 

Stickel et al., 

1979 

Blus et al.. 1979 

Newell et al., 

1987 

Blus, L.J., R. Heath, C. Gish, A. Belisle, and R. Prouty. 1979. Eggshell Thinning in the Brown 

Pelican: Implication of DDE. Bioscience 21: 1213-1215. (as cited in Newell et al., 1987) 

Newell, A. J., D.W. Johnson, and L.K. Allen. 1987. Niagara River Biota Contamination Project: 

Fish Flesh Criteria for Piscivorous Wildlife. Tech. Rep. 87-3. NY Dept. Environ. Conserv., Div. 

Fish Wildl., Bureau Environ. Protection. 

Ohlendorf, KM., D.M. Swineford, and L.N. Locke. 198 1. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4) 125135. 

Stickel, H., L. Reichel, and D.L. Hughes. 1979. Endrin in Birds: Lethal Residues and Secondary 

Poisoning, Toxicology and Occupational Medicine, organizer in. B. Deichman, Elsevier/North-Holland, New York. 

C-89 
c-90 
HEPTACHLOR 

CAS No.: 76-44-8 

CAS Preferred Nomenclature: 

4,7-Methano- 1 H-indene 

1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydroEmpirical Formula: C 1oHsC17 

Synonyms and Common Names: 

- Velsicol 104 - Heptagran 

- Rhodiachlor - Heptalube 

- Heptox - Drinox H-34 

E33 14 - Gold Crest H-60 

REGULATORY STATUS 

a 

H Cl 

H Cl 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l 

consumption of fish) for a 1Oa cancer 

EPA Drinking Water Health Advisories 

(IRIS, 1989): 

risk (IRIS, 1989): cbilp (10 kg): 

0.00029 pg/L l-day and lOday exposures = 10 pg 

longer-term exposure = 5 PgL 

aplllt (70 kg): 

longer-term exposure = 17.5 jtgL 

+ EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish (heptachlor + heptachlor 

ganisms)(lRIS, 1988): epoxide)(55 FR 14362): 

0.03* ppm 

Acute, pg/L 5.2x10-1 

Chronic, jtg/L 3.8~10‘~ 

. EPA Drinking Water Standard (50 FR l FDA Action Levels for Other Foods (55 

46936; IRIS, 1989): FR 14362): 

Proposed Maximum Contaminant 0.01 to 0.02* ppm 

Level = 0.0004 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0 mg/L 

z 

+ FDA Action Levels are for use in 

interstate commerce 

c-9z 
Use Restrictions and Bans: 

. All uses except subsurface ground insertion for termite control and dipping of roots or 

tops of nonfood plants banned by 1983 (43 FR 12372). 

SOURCES OF HEPTACHLOR 

Total Heptachlor Produced: 

l In 197 1,6 million pounds were produced by Velsicol Chemical Co. (Ouellette and Ring, 

1977). 

. By 1983, most uses had been cancelled (Rafats and MacLean, 1986). 

. Heptachlor is no longer sold in the U.S. as of August 1987, but remaining stock can be 

used in some States by commercial exterminators for termite control (ATSDR, 1987). 

Uses of Heptachlor: 

. Production of heptachlor as a registered insecticide began in 1952. It was widely used 

to control fii ants in southern States (Rafats and MacLean, 1986) and to control soil 

insects on corn and other crops (U.S. EPA, 1980). 

. Use of registered products (e.g., soil treatment for pineapples and sugarcane) allowed 

only by certified applicators (U.S. EPA, 1986b). No uses are allowed in Minnesota, 

Massachusetts, and New York (ATSDR, 1987). 

Other Sources: 

l Contaminant of the pesticide chlordane (Callahan, a A., 1979). 

FATE IN ENVIRONMENT 

Partitioning: 

. Based on its physical/chemical properties, heptachlor is moderately volatile (H = 

1.48~10~~ atm l m3/mo1), is strongly sorbed to sediment (Kw = 186,000). and has a 

high potential for bioaccumulation (BCF = 1.57x 104. 

Persistence: 

. Heptachlor can persist in aquatic systems once it sorbs onto sediment. 

l Heptachlor in the water column can undergo hydrolysis and photolysis and can be 

oxidized to heptachlor epoxide. Heptachlor is hydrolyzed to 1-hydroxychlordene; the 

c-92 
half-life is 1 to 3 days (Callahan et al., 1979). Specific near-surface rate constants for 

photolysis were not found, although photoisomerization is thought to occur 

(Verschueren, 1983). 

l Heptachlor can be biotransformed to heptachlor epoxide or chlordane, but at a slower 

rate in aquatic systems than abiotic hydrolysis (Callahan et al., 1979). 

HEALTH EFFECTS 

Carcinogenic@: 

. Exposure to heptachlor induced liver tumors in two strains of mice, but tests using rats 

did not result in any tumors (IRIS, 1989). The EPA classification is B2, a probable 

human carcinogen, based on tumors in mice and the fact that related chemicals cause 

liver cancers (U.S. EPA, 1986b). 

Mutagenic Activity: 

l Mutagenic effects were not observed in tests using bacteria, I&Q@&, or mammalian 

liver cells. Increased chromosomal aberrations were found in tests using mouse bone 

marrow cells (IARC, 1979; U.S. EPA, 1980; IRIS, 1987). 

Reproductive Effects: 

l Exposure to heptachlor has been associated with stillbirths in humans. 

l In animals, observed effects include decreased fertility and decreased survival of 

newborns in rats and liver damage in dogs (U.S. EPA, 1980). 

Other Toxicological Effects: 

. Acute (short-term, low-dose) exposure of humans can cause blood disorders, including 

anemia and leukemia, and central nervous system damage (e.g., hyperexcitability, 

depression, and convulsions) (U.S. EPA, 1980,1986b; IARC, 1979). 

l Hepatotoxicity, renal and adrenotoxicity, and blood disorders have been reported from 

chronic, (long-term, low-dose) exposure to heptachlor in animals. 

Toxicological Effects Indices: 

l Cancer Potency Factor (CPF): 4.5 (mg/kg/day)-’ (IRIS, 1989). 

l Reference Dose (RID): 5 x lOA mg/kg/day (U.S. EPA, 1987a; IRIS, 1989). 

. TWA-TLV (time-weighted average, threshold limit value), for occupational skin exposure: 0.5 mg/m3 (ACGIH, 1986). 

c-93 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor pressure, P (mm Hg): 

Hydrolysis, I&I l/lx 

Henry’s Law Constant H 8 

25°C (atm l m3/mol): 

Log (Gctanol- Water Partition 

Coefficient), log i&: 

Soil Adsorption Coefficient, Koc (mL/g): 

Fish Bioconcentration Factor, BCF: 

373.3 Windholz, 1983 

solid 

95-96 (pure) 

46-74 (technical grade) 

135-145OC at 

l-l.5 mm Hg 

1.57-1.59 

at 9°C 

1.65- 1.67 

at 25OC 

N/A 

0.056-o. 18 

at 25OC 

3~10~ at 25OC 

0.03 at 30°C 

1.48~10‘~ 

5.27 

4.4 

1 .2x10d 

1.1x103 to 

2. 1x104 

11,200 

Hartley and Kidd, 1987 

U.S. EPA, 1986c 

U.S. EPA, 1986c 

U.S. EPA, 1986c 

Cahhan et al., 1979 

Verschueren, 1983 

Callahan et al., 1979 

Mills et al., 1985 

Leo, 1983 

Mabey et al., 1982 

Mabey et al., 1982 

Verschueren, 1983 

U.S. EPA, 1980 

C-94 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGM, Cincinnati, OH. 

ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for 2,3,7,8-Tetrachlorodibenzo-p-Dioxin, ATSDR, U.S. Public Health Service, Oak Ridge National Laboratory, Oak Ridge, TN. 

Callahan, M. A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029a. 

Hartley, D., and H. Kidd, eds. 1987. Agrochemicals Handbook. Royal Society of Chemistry. 

Nottingham, England. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1987. Integrated Risk Information System Database. U.S. EPA, Washington, DC. 

IRIS. 1988. Integrated Risk Information System Database. U.S. EPA, Washington, DC. 

IRIS. 1989. Integrated Risk Information System Database. U.S. EPA, Washington, DC. 

Leo, A.J. 1983. Log P Parameter Database. Pomona College, Claremont, CA. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson. T. Mill, T.W. Chou, J. Gates, I. W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440-4-81-014. 

Mills, W.B., D.B. Porcella, M.J. Ungs, S.A. Gherini, K.V. Summers, L. Mok, G.L. Rupp, G.L. 

Bowie, and D.A. Haith. 1985. Water Quality Assessment: A Screening Procedure for Toxic and 

Conventional Pollutants in Surface and Groundwater. U.S. Environmental Protection Agency, 

Athens, Georgia. EPA 600/6-85/002a. 

Ouellette, R.P., and J.A. Ring. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co., New York. 

Rafats, J., and J. MacLean. 1986. Heptachlor Contamination, Special Reference Brief. National 

Agricultural Library, BeltsvilIe, MD. NAL SRB 86-02. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

c-95 
U.S. EPA. 1980. Ambient Water Quality Criteria for Heptachlor. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Criteria and Standards Division. EPA 

440/5-80-052. 

U.S. EPA. 1985. Suspended, Cancelled, and Restricted Pesticides. U.S. Environmental Protection 

Agency, Office of Pesticides and Toxic Substances, Washington, DC. 

U.S. EPA. 1986a. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

U.S. EPA. 1986b. Superfund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Emergency and Remedial Response, Washington, DC. EPA-540/l-86/060. 

U.S. EPA. 1986c. Pesticide Fact Sheet Number 107.1: Heptachlor. U.S. Environmental Protection Agency, Office of Pesticide Programs, Washington, DC. EPA-540/FS-87-202. PB-87- 

233748. 

U.S. EPA. 1987a. Draft. RCRA Facility Investigation (RFJ) Guidance. US. Environmental 

Protection Agency, Office of Solid Waste, Washington, DC. OSWER Directive 9502,00-6C. 

U.S. EPA. 1987b. Health Advisory for Hepuchlor and Heptachlor Epoxide. U.S. Environmental 

Protection Agency, Office of Drinking Water, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York.. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck Co., Inc., Rahway, NJ. 

C-96 
HEPTACHLOR EPOXDE 

CAS No.: 1024-57-3 

CAS Preferred Nomenclature: 

2,5-Methano-2H-indeno( 1-2-b)oxirene, 

2,3,4,5,6,7,8-heptachloro-la,lb,5,5a,6,6ahexahydroEmpirical Formula: C 1oHsC1-10 

Synonyms and Common Names: 

- 1,4,5,6,7,8,8-Heptachloro-2,3-epoxy2,3,3a,4,7,7a-hexahydro-4,7-methanoindene, 

- Epoxy heptachlor 

- Velsicol53-CS-17 

REGULATORY STATUS 

Standards and Criteria: 

Cl 

Cl Cl H 

l EPA Water Quality Criteria (for human 9 

consumption of fish) for a lo4 cancer 

EPA Drinking Water Health Advisories 

(IRIS, 1989): 

risk (IRIS, 1989): child: WW 

0.00029 pg/L long-term exposure = 0.13 l-@/L 

iuhli: WW 

long-term exposure = 0.5 pg/L 

. EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish (heptachlor + heptachlor 

ganisms)(IRIS, 1989): epoxide)(55 FR 14362): 

F!i%v%F 

0.03* ppm 

Acute, l.tg/L . 

Chronic, pg/L 3.8~10~~ 3:6x 1O’3 

+ EPA Drinking Water Standard (50 FR . FDR Action Levels for Other Foods: 

46936): 0.01 to 0.02 ppm* 

Proposed Maximum Contaminant 

Level = 0.0002 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0 mg/L 

* FDA Action Levels are for use in interstate commerce 

c-97 
Use Restrictions and Bans: 

. Restrictions on heptachlor, the parent compound, were instituted in 1978. Heptachlor 

is no longer sold in the U.S. as of August 1987, but remaining stock can be used in some 

States by commercial exterminators for termite control. No uses are allowed in Minnesota, Massachusetts, and New York (ATSDR, 1987). 

SOURCES OF HEPTACHLOR EPOXIDE 

’ Not produced as a separate chemical. 

l Heptachlor epoxide is a metabolic breakdown product of heptachlor that can be produced 

in microorganisms, plants, and animals (including humans). 

l It is a contaminant of heptachlor and chlordane. 

a Most uses of heptachlor have been banned. However, heptachlor epoxide can still be 

found in the environment. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, heptachlor epoxide is somewhat volatile (H 

= 4.4x10-4 atm l m3/mol), sorbs to organic matter to a moderate extent (&w = 500). 

and can be bioaccumulated (BCF values range from 850 to 4,500 based on experimental 

data). 

Persistence: 

0 Heptachlor epoxide is resistant to biotransformation. Its estimated half-life in soils is 

several years (U.S. EPA, 1987a). 

l Heptachlor epoxide is not susceptible to hydrolysis, oxidation, or photolysis. (Mabey 

et al., 1982; Eichelberger and Lichtenberg, 1971). 

HEALTH EFFECTS 

Cardnogenidty: 

l Exposure to heptachlor epoxide caused an increased incidence of liver carcinomas in 

rats and mice and hepatomas in female rats (IRIS, 1989). It is classified as a probable 

human carcinogen (B2) by the U.S. EPA (1986). 

C-98 
. Some increased lung and bladder cancers occurred in pesticide manufacturing plant 

workers, but it is difficult to associate occurrences with quantitative doses of a specific 

chemical (ATSDR, 1987). 

l No evidence of mutagenic activity was observed using mouse dominant lethal test, Ames 

test, or tests with fruit flies (IRIS, 1989). 

duct&&f&& . . 

l When animals were fed heptachlor epoxide there was decreased fertility and decreased 

fetal survival noted in rat and mouse studies extending for two to three generations. 

(Cerey and Ruttkay-Nedecka, 1971; Ruttkay-Nedecka, et al., 1972; Green, 1970). 

. Higher heptachlor epoxide levels were found in one group of women with premature 

delivery (Wasserman, et al., 1982) and in stillborn infants (Curley, et al., 1969). Data 

are not considered adequate to define a direct relationship between exposure and 

reproductive effects (ATSDR, 1987). 

l Acute (short-term, highdose) exposure in humans can cause central nervous system effects 

(e.g., irritability, dizziness, muscle tremors, and convulsions) (U.S. EPA, 1986). 

l In animals, liver, kidney, and blood disorders can occur. The oral LDso values for 

heptachlor epoxide range from 46.5 to 60 mg/kg. (U.S. EPA, 1980; IARC, 1979; IRIS, 

1988). 

l Cancer Potency Factor (CPF): 9.1 (mg/kg/day)-’ (IRIS, 1989) 

. Reference Dose (RfD): 1.3 x 10m5 mg/kg/day (IRIS, 1989) 

c-99 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 389.3 Windholz, 1983 

Physical State @ 20°C: solid 

Melting Point (“0 157-160 Callahan et al., 1979 

Boiling Point (“C): N/A 

Density/Specific Gravity: N/A 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 0.350 (25OC) Mabey et al., 1982 

Vapor pressure, P (mm Hg): 3x10+ (25OC) Mabey et al., 1982 

(value for 

heptachlor) 

Henry’s Law Constant, H 8 

25OC (atm l m3/mol): 4.4x10A Mabey et al., 1982 

Log (Octanol-Water Partition 

Coefficient), log ROW: 2.70 Mabey et al., 1982 

Soil Adsorption Coefficient, I& (mffg): 2.2~10~ Mabey et al., 1982 

Fish Bioconcentration Factor, 

BCF (for fish): l.44x104 (cak.) Lyman et al., 1982 

2900 pinfish Zaroogian et al., 

4500 minnow 1985 

1700 mussel 

850 oyster 

11,280 U.S. EPA, 1980 

c-100 
ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for 2,3,7,8-Tetrachlorodihenzo-p-Dioxin. U.S. Public Health Service, Oak Ridge National 

Laboratory, Oak Ridge, TN. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mahey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029a. 

Cerey, K., and J. Ruttkay-Nedecka. 197 1. The Influence of Heptachlor on Rat Fertility and Growth. 

Z. Versuchstierkd. 13:243-244. 

Curley, A., M.F. Copeland, and R.D. Kimbrough. 1969. Chlorinated Hydrocarbon Insecticides in 

Organs of Stillborn and Blood of Newborn Babies. Arch. Environ. Health 19:628-632. 

Eichelberger, J.W., and J.J. Lichtenberg. 1971. Persistence of Pesticides in River Water. Environ. 

Sci. Technol. 5:541-544. 

Green, V.A. 1970. Effects of Pesticides on Rat and Chick Embryo. In: Trace Subst. Environ. 

Health 3, Proc. Univ. MO. 3rd Annual. Conf., Meeting Date 1969 (D. Hemphill, ed.). 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1988. Integrated Risk Information System Database. U.S. Environmental Protection Agency, Washington, DC. 

IRIS. 1989. Integrated Risk Information System Database. U.S. Environmental Protection Agency, Washington, DC. 

Lyman, W.J., W.F. Reehe, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods - Environment. McGraw-Hill, New York. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. Mill, T.W. Chou, J. Gates, I.W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440- 4-81-014. 

Ruttkay-Nedecka, J., K. Cerey, and L. Rosival. 1972. Evaluation of the Chronic Toxic Effect of 

Heptachlor. Kongr. Chem. Pol’nohospod. 2:C27. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Heptachlor. U.S. Environmental Protection 

Agency, Office of Water Regulations and Standards, Criteria and Standards Division. EPA 

440/5-80-052. 
U.S. EPA. 1985. Drinking Water Criteria Document for Heptachlor. Heptachlor Epoxide and 

Chlordane. U.S. Environmental Protection Agency, Washington, DC. EPA 600/X-84- 197- 1. 

U.S. EPA. 1986. Superfund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Emergency and Remedial Response, Washington. DC. EPA-540/l-86/060. 

U.S. EPA. 1987. Draft. RCRA Facility Investigation (RFI) Guidance. U.S. Environmental 

Protection Agency, Office of Solid Waste. OSWER Directive 9502.00-6C. 

U.S. EPA. 1987b. Heptachlor and Heptachlor Epoxide Health Advisory. U.S. Environmental 

Protection Agency, Office of Drinking Water. 

Windholz, M., ed., 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck Co., Inc., Rahway, NJ. 

Zaroogian, G.E., J.F. Heltshe, and M. Johnson. 1985. Estimation of bioconcentration in marine 

species using structure-activity models. Environ. Toxicol. Chem. 4:3-12. 

c-102 
HEXACHLOROBENZENE 

CAS No.: 118-74-l 

CAS Preferred Nomenclature: 

Benzene, hexachloroEmpirical Formula: C&l6 

Synonyms and Common Names: 

- HCB - Amadin 

- NoBunt - Co-op Hexa 

- Perchlorobenzene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of fish) for a lOa cancer 

risk (US. EPA, 1987): 

0.74 rig/L 

l EPA Ambient Water Quality Criteria 

(for protection of aquatic organisms) 

None established at present 

l EPA Drinking Water Standard Maximum Contaminant L3fel: 

None established at present 

Use Restrictions and Bans: 

Cl 

Cl 

Cl 5 

Cl 

G 

Cl 

Cl 

c&J 

+ EPA Drinking Water Health Advisories 

(U.S. EPA, 1987): 

u (10 kg): 

1 -day, lo-day and long- term 

exposure = 0.05 mg/L 

iid& (70 kg): 

long-term exposure = 0.2 mg/L 

. Food and Drug Administration Action 

Level for Fish: 

None established at present 

l Food and Drug Administration Action 

Level for Meat and Poultry (Morris and 

Cabral, 1986): 

0.5 ppm* 

l FDA Action Levels are for use in interstate commerce 

l In 1984 registration of hexachlorobenzene as a pesticide was voluntariIy cancelled 

(Morris and Cabral, 1986). 

c-103 
SOURCES OF HEXACHLOROBENZENE 

Total Hexachlorobenzene Produced: 

l Production in the U.S. of HCB as a pesticide was about 3.2 million pounds in 1975 

(Blackwood and Sipes, 1979). Commercial production in the U.S. was discontinued in 

1976 (U.S. EPA, 1984). Since 1981 no HCB has been imported (Menzie, 1986). 

l HCB is formed, however, as a by-product of the production of other chlorinated 

compounds. Major sources include carbon teuachloride, tetrachloroethene, and 

trichloroethene. HCB is also an impurity in some pesticides (e.g., pentachloronitrobenzene, chlorothalonil, dacthal, picloran) and in pentachlorophenol. 

Uses of Hexachlorobenzene: 

l Primary agricultural use prior to 1985 was as a fungicide to protect seeds of grain crops, 

particularly wheat (Devine, 1982; Pelletier, 1985) 

l In the early 1970’s, small amounts of HCB were used for a variety of industrial purposes: 

- fungicide in paper products (Verschueren, 1983) 

- pyrotechnic materials (Quinlivan et al., 1975) 

- synthetic rubber production for tires (Mumma and Lawless, 1975) 

- reported use as fluxing agent in aluminum production (Quinlivan et al., 1975) 

- reported use in graphite electrode production (Mumma and Lawless, 1975). 

Other Sources: 

l Incineration of municipal waste and chlorination treatment of industrial process water 

and wastewater. 

l Breakdown product of the biotransformation of lindane (Morris and Cabral, 1986). 

l Emissions to air and water from landfills containing pesticides and industrial wastes 

(Brooks and Hunt, 1984). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical 

f 

roperties, hexachlorobenzene can volatilize but not 

readily (H = 6.8~10~ atm l m /mol). An experimentally-determined volatilization 

half-life was 41 hours in l-meter-deep water (Korte and Greim, 1981). HCB sorbs 

c-104 
strongly to soils or sediments containing organic matter WOW = 457,000). HCB can 

bioaccumulate, although the potential differs substantially among aquatic species (BCF 

= 7,800 to 22,000). 

Persistence: 

. Hexachlorobenzene is widespread and persistent in aquatic systems. Recent experiments by Mill and Haag (1986) confirmed that photolysis is slow with a half-life of about 

90 days. Earlier experiments had suggested that natural organics (e.g., humic acids) 

might increase photolysis, but Mill and Haag found no such effect. Because of its 

chemical structure, HCB does not undergo hydrolysis at temperatures normally found 

in the environment. Experiments to determine biotransformation rates of HCB found 

negligible degradation (Tabak et al., 1981; Callahan et al., 1979). 

HEALTH EFFECTS 

Carcinogenicity: 

l Hexachtorobenzene causes liver tumors in rats, mice, and hamsters (IARC, 1979; U.S. 

EPA, 1984). Tumors have also been induced in kidneys of rats and in adrenal and thyroid 

glands of hamsters (U.S. EPA, 1984). EPA classification B2: Probable human carcinogen (IARC Class 2b) (PHRED, 19888). 

Mutagenic Activity: 

l Hexachlorobenzene was not mutagenic in bacterial or mammalian cell assays, but was 

mutagenic in yeast (U.S. EPA, 1984). The Ames test was also negative (Morris and 

Cabral, 1986). 

Reproductive Effects: 

l HCB is teratogenic in mice and rats (IARC, 1979) and fetotoxic in rats and quail. 

. An increase in mortality of breast-fed babies whose mothers have been chronically 

exposed to HCB has also been reported (IARC, 1979). 

Other Toxicological Effects: 

l Chronic (long-term, low-dose) human exposure to HCB can cause porphyria with the 

following symptoms: skin lesions, excessive pigmentation, excessive hair production 

or hair loss, light sensitivity, and neurologic damage (U.S. EPA, 1984, 1987). Effects 

on animals include liver and kidney lesions in rats; immunosuppression in mice, rats and 

dogs; neurologic damage in mice; and changes in ovaries of female mice (U.S. EPA, 

1987; Morris and Cabral, 1984). One test using rats showed no effects on the first 

generation at dosages of 0.32-40 ppm, but the second generation had liver and 

C-105 
parathyroid gland problems. Oral LDso values range from 1,700 mgkg in cars to 10,000 

mgkg in rats (U.S. EPA, 1987). 

Toxkologkal Effects Indices: 

l Cancer potency factor (CPF): 1.7 (mg/kg/day)-’ (U.S. EPA, 1986; PHRED, 1988). 

l Reference Dose (IUD): 0.0008 mg/kg/day (IRIS, 1989). 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 2O*C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/P): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant H @ 

25*C (atm l m3/mol): 

284.8 

solid 

231 

323-326 

2.044 (23OC) 

N/A 

6x 10-3 (25OC) 

0.11 (24OC) 

1.089x 1O’5 (20°C) 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Cahhan et al., 1979 

Verschueren, 1983 

Callahan et al., 1979 

6.8xlO”(calc) Lyman et al., 1982 

Log (Octanol-Water Partition 

Coefficient), log Kow: 

Soil Adsorption Coefficient, 

Koc (mU$: 

Fish Bioconcentration 

Factor, BCF: 

5.66 

39OO(cak) 

Leo, 1983 

Lyman et al., 1982 

7800 rainbow trout 

22,000 fathead 

minnow 

8,690 

U.S. EPA, 1987 

U.S. EPA, 1987 

U.S. EPA, 1980 

c-107 
REFERENCES 

Blackwood and Sipes. 1979. Status Assessment of Toxic Chemicals: Hexachlorobenzene. U.S. 

Environmental Protection Agency, Office of Research and Development, Washington, DC. EPA600/2-79-2 1 Og. 

Brooks, G.W., and G.E. Hunt. 1984. Source Assessment for Hexachlorobenzene. EPA Contract 

No. 68-02-3818. Research Triangle Park, NC. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol II. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029b. 

Devine, K. 1982. Preliminary Quantitative Usage Analysis of Hexachlorobenzene. U.S. Environmental Protection Agency, Office of Pesticides Programs, Washington, DC. 

ICF Incorporated. 1985. Draft Superfund Public Health Evaluation Manual. U.S. Environmental 

Protection Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA 

Contract #68-O l-7090. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1988. Integrated Risk Information Service. Office of Emergency and Remedial Response, 

U.S. Environmental Protection Agency, Washington, DC. 

IRIS. 1989. Integrated Risk Information Service. Office of Emergency and Remedial Response, 

U.S. Environmental Protection Agency, Washington, DC. 

Korte, F. and H. Greim. 1981. Feasibility of Test Guidelines and Evidence of Base-set Testing 

according to the Chemicals Legislation. Environmental Research Plan of the Ministry of the 

Interior, Research Report No: 10704006/l. Federal Environmental Agency, West Berlin, Germany. 

Leo, A.J. 1983. Log P Parameter Database, Pomona College, Claremont, CA. 

Lyman, W.J., ed. 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill, New 

York. 

Menzie, C.M. 1986. Hexachlorobenzene: Uses and Occurrence. pp. 13-22. In: Morris, CR. and 

J.R.P. Cabral, ed. Hexachlorobenzene: Proceedings of an International Symposium. IARC. 

Scientific Publications No.77. 

C-108 
Mill, T., and W. Haag. 1986. The Environmental Fate of Hexachlorobenzene. p.61-66. In 

Hexachlorobenzene: Proceedings of an International Symposium, ed. C.R. Morris and J.R.P. Cabral. 

IARC Scientific Publications, No.77 

Morris, C.R., and J.R.P. Cabral, eds. 1986. Hexachlorobenzene: Proceedings of an International 

Symposium. IARC Scientific Publication No.77. Lyon, France. 

Mumma, C.E., and E.W. Lawiess. 1975. Survey of Industrial Processing Data, Task I - 

hexachlorobenzene, pollution from chlorocarbon processes. U.S. Environmental Protection Agency, Washington, DC. EPA-560/3-75-003. 

Pelletier, E.N. 1985. Fungicidal Uses of HCB and Other Fungicides Possibly Containing HCB. 

Memo from E.N. Pelletier to P. Tobin, February 11.1985. U.S. Environmental Protection Agency, 

Office of Pesticides Programs, Washington, DC. 

PHRED. 1988. Public Health Risk Evaluation Database. Office of Emergency and Remedial 

Response. U.S. Environmental Protection Agency, Washington, DC. 

Quinlivan, SM., M. Ghasseni, and M. Shanty. 1975. Survey of Methods Used to Control Water 

Containing Hexachlorobenzene. U.S. Environmental Protection Agency, Washington, DC. NTIS 

PB 25305. 

Tabak, H.H., S.A. Quave, C.I. Mashni, and E.F. Barth. 1981. Biodegradability Studies with 

Organic Priority Pollutant Compounds. Jour. Water Pollution Control Federation 53(10):1503- 

1518 

Toxicology Data Bank (TDB) Database. 1985- 1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1984. Health Effects Assessment for Hexachlorobenzene. U.S. Environmental Protection Agency, Washington, DC. EPA 540/l/86-017. 

U.S. EPA. 1986. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

U.S. EPA. 1987. Health Advisory for Hexachlorobenzene. U.S. Environmental Protection 

Agency, Office of Drinking Water, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

C-109 
C-110 
0bHEXACHLOROCYCLOHEXANE 

(alpha=BHC) 

CAS No.: 3 19-84-6 

CAS Preferred Nomenclature: 

Cyclohexane, 1,2,3,4,5,6-hexachloro- 

(l.alpha., 2.alpha., 3.heta.. 4.beta., 

S.betas, 6heta.)- 

Empirical Formula: C&I&b 

Synonyms and Common Names: 

- a-Hexachlorocyclohexane - a-Benzenehexachloride 

- a-BHC - a-Hexachloran 

- a-HCH - a-Lindane 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 9 

consumption of fish) for a 10e6 cancer 

EPA Drinking Water Health Advisories: 

w(lO kg): 

risk (IRIS, 1989): 

3.1 x lo’* &?J/L 

l-day, lo-day and long-term 

exposures = 50 pg/L 

uhli (70 kg): 

long-term exposure = 20 PLgn, 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish: 

ganisms)(IRIS, 1989): None established at present 

Freshwater Saltwater 

Acw CL@ 100 0.34 

Chronic, kg/L - - 

Above are LECs (Lowest Effect Concentration) 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

C-III 
Use Restrictions and Bans: 

. In 1977, EPA cancelled inclusion of a-hexachlorocyclohexane in technical grade 

lindane (EPA, 1985). 

. Uses of all but y-hexachlorocyclohexane (lindane) were cancelled by 1978 (41 FR 

46031; 43 FR 31432). 

SOURCES OF a-HEXACHLOROCYCLOHEXANE 

Total a-Hexachlorocyclohexane Produced: 

. a-Hexachlorocyclohexane is no longer produced in the United States. 

Uses of a-Hexachlorocyclohexane: 

l Hexachlorocyclohexane occurs in eight forms. Technical grade lindane is an off-white 

to brown powder that, prior to 1977, contained a-hexachlorocyclohexane. 

l Technical-grade lindane was used to control cockroaches, flies, aphids, grain weevils, 

and beetles (Kirk-Othmer, 1982). 

Other Sources: 

l May be selective degradation product of other hexachlorocyclohexane isomers. 

(Matsumura. 1985). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on the physical/chemical properties of a-hexachlorocyclohexane, sorption to 

sediment is moderate(Kow = 8,000). and the potential for bioaccumulation is low (BCF 

= 130). Based on its similarity to the y isomer, volatilization is estimated to be low. 

l Experiments by Tsukano (1973) reported Freundlich isotherms for the 

hexachlorocyclohexane isomers on two soils with organic carbon contents of 1.9% and 

5.2%. The values were l/n =0.71 to 0.83 and K = 30 to 120 for the second soil. 

Persistence: 

l Hydrolysis, photolysis, and oxidation are not thought to be important fate-determining 

processes in the environment. One experiment showed no change due to hydrolysis at 

a pH of 7.3 to 8 after 2 years (Callahan et al., 1979). No other studies under acidic or 

more alkaline conditions were found. 

c-112 
. Biotransformation has been observed in laboratory experiments conducted using 

soil/water mixtures under anaerobic conditions (Tsukano, 1973). 

HEALTH EFFECTS 

Carcinogenicity: 

l Inadequate data exist to determine whether a-hexachlorocyclohexane is a human 

carcinogen. Exposure to a-hexachlorocyclohexane caused increased incidences of liver 

tumors in mice and rats. a-Hexachlorocyclohexane is classified by EPA as a probable 

(B2) human carcinogen. IARC (1979) states that hexachlorocyclohexane cannot be 

classified (class d) because of limited data. 

Mutagenic Activity: 

. a-Hexachlorocyclohexane (tested individually and mixed with j%hexachlorocyclohexane) was determined to be nonmutagenic in bacteria, yeast, and Drosopl& 

(IARC, 1979). 

-Effects: No data found. 

None found. 

Toticoiogical Effects Indices: 

l Cancer potency factor (CPF): 6.3 (mg/kg/day)-1 (IBIS, 1989). 

c-113 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility. S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25°C (atm l m3/mol): 

Log (Octanol- Water Partition 

Coefficient), log &JW: 

291 

solid 

157-158 

N/A 

N/A 

N/A 

1.63 

2.5x1o-5 

Callahan et al., 1979 

Gunther, 197 1 

Brooks, 1974 

Cak&u~ et al., 1979 

N/A 

3.90 Mabey et al., 1982 

Soil Adsorption Coefficient, K&mug): 3800 Mabey et al., 1982 

Fish Bioconcentration Factor, BCF: 130 OWRS, U.S. EPA, 1980 
Brooks, G.T. 1974. Chlorinated Insecticides: Volume I: Technology and Applications. CRC 

Press, Cleveland, OH. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, and B. Maestri. 1979. Water Related Environmental Fate of 129 Priority 

Pollutants. U.S. Environmental Protection Agency, Washington, DC. EPA-440/4-79-029a. 

Gunther, F.A. 197 1. Halogen Derivatives of Aliphatic Hydrocarbons. Residue Review. 36:34-77. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information Service. U.S. Environmental Protection Agency, Office 

of Emergency and Remedial Response, Washington, DC. 

Kirk-Gthmer. 1982. Encyclopedia of Chemical Technology. 3rd. ed. John Wiley and Sons, Inc., 

New York. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. MiIl, T.W. Chou, J. Gates, T. W. Partridge, 

H. Jaber, D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. SRI 

International. EPA 440/4-8 1-O 14. 

Matsumura, F. 1985. Toxicology of Insecticides. 1982. 3rd ed. John Wiley and Sons, Inc., New 

York. 

OWRS, U.S. EPA. 1980. Ambient Water Quality Criteria Documents for -Hexachlorocyclohexane. 

Tsukano, Y. 1973. Factors Affecting Disappearance of BHC Isomers from Field Rice Soil. JARQ. 

7(2):93-97. 

U.S. EPA. 1985. Guidance for the Registration of Pesticide Products Containing Lindane as the 

Active Ingredient. U.S. Environmental Protection Agency, Office of Pesticide Programs, 

Washington, DC. EPA 54O/RS-86- 12 1. 

U.S. EPA. 1987. Draft RCRA Facility Investigation (RFI) Guidance. U.S. Environmental Protection Agency, Office of Solid Waste, Washington, DC. EPA-530/SW-87-001. 

C-115 

ISOPROPALIN 

CAS No.: 33820-53-o 

CAS Preferred Nomenclature: 

Benzenamine, 4-( 1-methylethyl)-2,6- 

dinitro-N,N-dipropylNO2 

KH,&CH 

-0 

/ \ N [(CH14CH,12 

- 

Empirical Formula: C t5H23N304 

Synonyms and Common Names: 

- Paarlan 

- 2,6-Dinitro-N,N-dipropylcumidene 

- El-179 

REGULATORY STATUS 

Standards and Criteria: 

9 EPA Water Quality Criteria (for human 

consumption of fish): 

None established at present 

l EPA Drinking Water Health Advisories: 

None established at present 

l EPA Ambient Water Quality Criteria l EPA Tolerance Levels for peppers and 

(for protection of aquatic organisms): tomatoes (40 CFR 180.3 13): 

None established at present 0.05 ppm 

(Proposed to be revoked in May 1990) 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

l Food and Drug Administration Action 

Level for Fish: 

None established at present 

Use Restrictions and Bans: 

. Isopropalin may be used only as a pre-emergent herbicide on tobacco fields that are not 

rotated with food or feed crops. 

SOURCES OF ISOPROPALIN 

Total Jsopropalin Produced: 

0 Isopropalin is produced by Eli Lilly and Co. No production data are available (SRI, 

1986). 

c-117 
l One report states that other dinitroaniline herbicides are used more widely than 

isopropalin. This would make isopropalin production in the U.S. less than 4,000 tons 

per year (Green et al., 1987). 

Uses of Isopropalin 

. Isopropalin is a dinitroaniline compound used as a herbicide to control grasses and 

broadleaf weeds in the vegetable crops of peppers and tomatoes (Ouellette and King, 

1977; Worthing, 1983; Farm Chemicals Handbook, 1985). 

l The only currently registered use for isopropalin is as a preemergent spray for controlling 

weeds in tobacco crops (Worthing, 1983; IRIS, 1989). 

None found. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based upon its physical/chemical properties, isopro?aIin is predicted to volatilize 

relatively rapidly from water (H=l.5 x lOA atm l m /mol) and at a slower rate from 

surface soil (P/S& = 4.4 x 10” mm Hg* Umg corresponding to an estimated 

volatilization half-life of 3.6 days). 

l It adsorbs relatively strongly to soils and sediments (estimated = 8.5 x 104 and has 

a high potential for bioaccumulation (estimated BCF = 2.5 x 10 

l Isopropalin has a low potential for leaching from soils. Holzer and Sieck ( 1972) reported 

that isopropalin and its associated breakdown products, which formed during 30 days 

of aerobic incubation, were relatively immobile in a sandy loam soil. Approximately 

99% of the radio-labeled compound initially applied as 14C-isopropalin remained in the 

top 2 inches of a 12-inch sandy loam column after 45 days of elution with 0.5 inch 

water/day. 

l Sleight (1972) reported maximum isopropalin concentrations of 25-40 mg/kg in the 

edible tissues of bluegill sunfish during 42 days of exposure to 0.025 mgL. The 

tissue- to-water concentration ratios correspond to non-steady-state BCF values of 1 .O x 

103.to 1.6 x 103. 

Persistence: 

l Saunders and Smith (1983) reported that at 24OC, isopropalin did not undergo any 

detectable hydroiysis over a 42-day period at pH values of 57, and 9. 

l Saunders and Smith (1983) reported ashort photodegradative half-life of 1.5 hours for 

isopropalin in a pH 7 buffered aqueous solution exposed to artificial light with a similar 

irradiation spectrum to that of sunlight. 

C-l 18 
. Biodegradation of isopropalin in soil occurs. The specific processes include dealkylation, reduction of nitro groups to amino groups. Twelve different breakdown products, 

representing at most 4% of the parent compound, were identified (Golab and Althaus, 

1975). Golab (1983) reported relatively long 50% dissipation times of approximately 

6 months for 2 ppm isopropalin incubated at 23°C in a sandy loam, a loam, and a clay 

loam soil under aerobic conditions. Golab and Sassic (1983) reported that the degradation of isopropalin in a loam soil was more rapid under anaerobic conditions (45% 

dissipated within 60 days) than under aerobic conditions. 

ISOPROPALIN OBSERVED IN THE ENVIRONMENT 

l No data available. 

HEALTH EFFECTS 

Cardnogenicity: 

. The carcinogenic potential of isopropalin has not been evaluated by the U.S. EPA (IRIS, 

1989). No experimental data have been found for carcinogenic&y tests with isopropahn. 

. v: No data found. 

Reproductive Effects: 

l The U.S. EPA states that better studies on the reproductive effects of ispropalin need to 

be conducted. In one rat study with isopropalin, the only effects noted were reduced 

weights and reduced food consumption in exposed mothers (IBIS, 1989). 

Other Toxicologkal Effects: 

l Acute human toxicity due to short-term, high-dose exposure to isopropalin is considered 

to be insignificant (Sittig, 1985). 

l Isopropalin at high doses (~2000 mg/kg) caused eye and skin irritation in rabbits 

(Worthing, 1983). 

l No fatalities were observed in chickens, dogs, mallard ducks, or rabbits fed isopropalin 

at 2000 mg/kg or quail fed a dosage of 1000 mg/kg (Worthing, 1983). 

l Subchronic (go-day feeding) exposure of rats caused a reduction in the number of red 

blood cells and alterations in organ weights at the highest dose (288 mg/kg/day). 

l EPA does not require that chronic (long-term, low-dose) exposure tests be conducted 

because of isopropalin’s use on tobacco. EPA recognizes that the use of tobacco 

products is detrimental to the consumer and that the use of tobacco is voluntary. It may 

be possible then to avoid exposure to isopropalin residues (IRIS, 1989). 

c-119 
Toxicological Effects Indices: 

. Reference Dose (RfD): 1.5 x 10e2 mg/kg/day (IRIS, 1989). 

. Oral LD5orat.s and mice: >5000 mgkg (Dreisbach, 1980; Sittig, 1985; Worthing. 1983). 

. LC=,o (96 hour): fathead minnow, >O. 1 mgk; goldfish, >o. 15 mg/L. 

c-120 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (OC): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

309.4 Wonhing, 1893 

red-orange Worthing. 1983 

liquid 

N/A 

390 (talc.) Lyman et al., 1982 

N/A 

N/A 

0.08 Weed Science Society, 

1983 

3x 10-5(25.60C) Weed Science Society, 

1983 

Henry’s Law Constant, H @ 

25°C (atm l m3/mol) 1.5x lo-4 (cak.) Lyman et al., 1982 

Log (Gctanol-Water 

Partition Coefficient). log Kow: 5.74 (talc.) Lyman et al., 1982 

Soil Adsorption Coefficient, I& (mug): 8.5x lo4 (talc.) Lyman et al., 1982 

Fish Bioconcentration Factor, BCF: 2.5~10~ (cak.) Lyman et al., 1982 

c-121 
Dreisbach, R.H. 1980. Handbook of Poisoning: Prevention, Diagnosis and Treatment. Lange 

Medical Publications, Los Altos, CA. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Golab, T. 1983. 14C-Isopropalin Aerobic Soil Degradation Study. Eli Lilly and Co. ABC-0154. 

Golab, T., and W.A. Ahhaus. 1975. Transformation of Isopropalin in Soil and Plants. Weed 

Science 23: 165. 

Golab. T., and K.A. Sassic. 1983. (14C) Isopropalin Anaerobic Soil Degradation Study. Eli Lilly 

and Co. ABC-0155. 

Green, M.B., G.S. Hartley, and T.F. West. 1987. Chemicals for CropImprovement and Pest 

Management. 3rd ed. Pergamon Press, Oxford, England. 

Holzer, F.J., and R.F. Sieck. 1972. EL-179 Leaching Study on Degradation Products. Eli Lilly 

Co. and Purdue University. CDL: 12628 1 -C; MRID #00002474. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Lyman, W.G., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Ouellette, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill BookCo., 

New York. 

Saunders, D.G., and SK. Smith 1983. Photodegradation of Isopropalin in Aqueous Solution. Eli 

Li.lIy and Co. 1 -EWD-83-02. 

Sittig, M., ed. 1985. Pesticide Manufacturing and Toxic Materials Control Encyclopedia. Noyes 

Data Corp., Park Ridge, NJ. 

Sleight, R.H. 1972. Research Report: Accumulation and Persistence of 14C-EL-179 Residues of 

Bluegill (Lepomis macrochirus) Continually Exposed to the ChemicaI in Water. Eli Lilly and Co. 

CDL: 12628 1 -D; MRID #00002475. 

Smith, SK., and D.G. Saunders. 1983. Hydrolysis of the Herbicide Isopropalin in Aqueous Buffer 

Solution. EliLiIly and Co. l-EWD-82-33. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

c-122 
Weed Science Society of America. 1983. Herbicide Handbook. 5th ed. Weed Science Society of 

America, Champaign, IL. 

Worthing, CR., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

C-123 
C-124 
(Y-HEXACHLOROCYCLOHEXANE) 

CAS No.: 58-89-9 

CAS Preferred Nomenclature: 

Cyclohexane, 1,2,3,4,5,6-hexachloro-, 

Empirical Formula: C&I&l6 

Synonyms and Common Names: 

- y-Benzene hexachloride 

- y-BHC 

- y-HCH 

- y-Hexachlorobenzene 

-y-Hexachlorocyclohexane 

-Gammexane 

-Jacutin 

-Lindex 

REGULATORY STATUS 

Standards and Criteria: 

. EPA Water Quality Criteria (for human . EPA Drinking Water Health Advisories 

consumption of fish) (IBIS, 1989): 

6.25 x 1O-2 pg/L 

(PHRED, 1988) 

s;hilQ (10 kg): 

1 -day and 1 O-day exposure = 1200 pgk 

longer-term exposure = 33 pg/L 

adult(70 kg): 

longer-term exposure = 0.12 l-lg/L 

lifetime exposure = 0.2 l.@L 

. EPA Ambient Water Quality Criteria . Food and Drug Administration Action 

(for protection of aquatic or Level for Fish: 

ganisms)(IRIS, 1989): None established at present 

Acute, l.t.g/L 2.0 

Chronic, pg/L 8.0x10-* 1 

c-125 
l EPA Drinking Water Standard 

(IRIS. 1989): 

Current Maximum Contaminant 

Level = 0.004 mg/L 

Proposed Maximum Contaminant 

Level = 0.0002 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0.0002 mg/L 

. Food and Drug Administraiton Action Level for Other Foods (55 FR 

14362) 

0.1 to 0.5 ppm* 

l FDA Action Levels are for use in interstate commerce 

l In 1977, EPA banned inclusion of a-and p-hexachlorocyclohexane in technical grade 

lindane. 

l Use in smoke fumigation devices for indoor domestic purposes banned in 1985 (48 FR 

485 12,50 FR 5424). 

l Use of lindane in dog dips for the control of pests (other than mites) permitted only for 

veterinary use (U.S. EPA, 1985). 

. Application permitted only under direct supervision of a certified applicator. Protective 

clothing required (U.S. EPA, 1985). 

SOURCES OF LINDANE 

Total Lindane Produced: 

l First synthesized in 1825, lindane’s insecticidal properties were discovered in 1942 

(Hayes, 1982). 

l In 197 1, one million pounds were produced by Occidental Petroleum Corporation 

(Guellette and King, 1977). 

l Technical lindane (a mixture of several isomers of hexachlorocyclohexane) is no longer 

produced in the United States, but is imported from France, Germany, Spain, Japan, and 

China (U.S. EPA, 1985). It is an off-white to brown powder with a persistent, musty 

odor (Hayes, 1982). 

Uses of Lindane: 

. Lindane is registered for use as an insecticidekaracide on a variety of fruit and vegetable 

crops, ornament&, tobacco, forestry, domestic outdoor and indoor uses by homeowners, 

commercial warehouses or feed storage areas, farm animal premises, and wooden 

structures (U.S. EPA, 1985). 

C-i26 
. Lindane is primarily used on phytophagous and soil-inhabiting insects, public health 

pests, and animal ectoparasites (Farm Chemicals Handbook, 1987). 

l In 1982, approximately 48%. 20%. and 19% of the lindane use in the U.S. was for seed 

treatment, livestock, and hardwood lumber, respectively. 

Other: Component of other hexachlorocyclohexanes. 

FATE OF LINDANE IN THE ENVIRONMENT 

Partitioning: 

l Based upon its physical/chemical properties, lindane is predicted to volatilize relatively 

slowly from water (H = 4.9 x 10” atm l m3/mol). volatilize at an intermediate rate from 

soil surfaces (P/S& = 3.3 x 10-lomm Hg l Umg. corresponding to an estimated 

voiatiiization half-life of 18 days), and have intermediate adsorption to soils and 

sediments (& = 3.8 x 103) (Lyman et al., 1982). 

. Kay and Elrick (1967) reported intermediate soil/water partition coefficients (Kp) of 23, 

20, and 17 for lindane adsorbed to a sandy loam (organic carbon content (oc) of 3.2%), 

loam (oc = 3.6%), and loamy sand (oc = 2.9%) soil, respectively. The corresponding 

Koc values are 720,560, and 590, respectively. Foschi et al. (1970) reported that lindane 

is moderately susceptible to leaching from a low organic soil. After elution with 35 

inches of water, 80%, 19%. and 1% of the total lindane recovered from a 60 cm sandy 

clay loam (oc = 1.5%) column were recovered in the 0 to 5 cm, 5 to 20 cm, and 20 to 

40 cm segments, respectively. No lindane was detected in the 40 to 60 cm segment or 

in the leachate. 

l Forbis (1986) reported maximum BCFs of 780 (edible tissue) and 1,400 (whole body) 

for bluegill sunfish exposed to 0.54 ppb lindane over a 28-day period. 

Persistence: 

l Based upon the hydrolysis rate constants measured by Ellington et al. (1986). lindane 

has an intermediate hydrolysis half-life of 14 days at pH 9, and relatively long hydrolysis 

half-lives of 210 days at pH 7 and 240 days at pH 5. 

l ADL (1986) reported a relatively long photodegradative half-life of 48 days for lindane 

in water. 

l Biotransformation is favored in biologically rich, anaerobic environments. Half-lives 

range from several days to over a year (Callahan et al., 1979). Under some conditions, 

lindane degrades to g-pentachlorocyclohexane (Kirk-Othmer, 1978). 

C-127 
HEALTH EFFECTS 

Carcinogenicity : 

. Evidence to determine whether g-hexachlorocyclohexane is a humah carcinogen is 

limited. The technical grade of lindane (containing approximately 65% a-hexachlorocyclohexane) has been shown to cause liver cancer in four strains of mice. Experiments 

performed on rats were negative (Ito et al., 1975, Fitzhugh et al., 1950). 

l The carcinogenicity data for lindane is presently under review by the U.S. EPA (IRIS, 

1989). However, on the basis of mouse carcinogenicity, EPA has previously rated 

lindane as a B2 carcinogen (IRIS, 1989). 

Mutagenic Activity: 

. Predominantly negative results have been obtained in mutagenicity testing of lindane. 

Tsoneva-Maneva er al. (197 1) reported lindane-induced alterations in mitotic activity of 

Chinese hamster cells. Chromosomal breaks and gaps in Chinese hamster cells have 

also been attributed to lindane exposure (Ishidata and Odashima, 1971). Mutagenic 

effects were not observed in tests using bacteria (Buselmaier et al., 1972; Schubert, 

1969). 

Reproductive Effects: 

l Lindane has been shown to cause disturbed estrous cycles, decreases in fetal survival, 

and reduced numbers of Iive births in rats; delayed sexual maturation in female rats 

(Shtenberg and Mamefkulien, 1976); and increases in stillbirths in dogs (Litterst and 

Miller, 1975). 

Other Toxicological Effects: 

l Acute lindane poisoning affects the nervous system, causing restlessness, tremors, 

unsteady gait, heavy breathing, and convulsions. Violent convulsions are rapid in onset 

and generally followed by death or recovery within 24 hours. The probable human oraI 

lethal dose is 50-500 mg/Icg (IUaassen et al., 1986). 

l Rats fed diets containing lindane developed mild toxicity-related changes primarily in 

the kidneys and liver. 

Toxicological Effects Indices: 

l Cancer Potency Factor (CPF): 1.33 (mg/kg/d)-’ WIRED. 1988) 

C-128 
l Technical Grade CPF: 1.8 (mg/kg/d)~’ (MS, 1989) 

. Reference Dose (IUD): 3~10~ mg/kg/d (IRIS, 1989) 

. TWA-TLV (time-weighted average-threshoid limit value) for occupational Skin exposure: 0.5 mg/m3 (ACGIH, 1986) 

c-129 
PHYSICAWCHEMICAL PROPERTIES FOR LINDANE 

Value Reference 

Molecular Weight (g/mole): 290.85 

Physical State @ 20°C: colorless solid 

Melting Point (“C): 112.9 

Boiling Point (“C): 323.4 

Specific Gravity: 1.87 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 7.52 0.4 @' 25OC 

Vapor Pressure, P (mm Hg): 9.4x10-Q 20°C 

Hydrolysis, K&r-‘), 

Kb (l/Mm 

1.20.2xlO~ 

198 

Henry’s Law Constant, 

H @ 25*C (atnt l m3/mol): 4.9x10" 

Log (Octanol-Water Partition 

Coefficient), log K.o~: 

Soil Adsorption Coefficient, K&ml/g): 

Fish Bioconcentration Factor, BCF: 

3.72 

3.8 x lo3 

780 edible tissue, 

1400 whole body for 

bluegill sunfish 

130 

Windholtz, 1983 

IRIS, 1989 

Callahan et al., 1979 

IRIS, 1989; Weast, 1979 

Verschueren, 1983 

Callahan et al., 1979 

IRIS, 1989; Windholz, 

1983 

Ellington et al., 1987 

Mills et al., 1985 

IRIS, 1989 

Lyman et al.. 1982 

Forbis, 1986 

c-130 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Arthur D. Little (ADL), Inc. 1986. The Installation Restoration Program Toxicology Guide, 

Vol. 2. 

Buselmaier, W., G. Rohrbom, and P. Propping. 1972. Mutagenicity, Investigations with Pesticides 

in the Host Predicted Assay and Dominant Lethal Test in Mice. Biol. Zbl. 91:3 1 l-325. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.P. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, and B. Margin. 1979. Water Related Environmental Fate of 129 Priority 

Pollutants. U.S. Environmental Protection Agency, Washington, DC. EPA 440/4-79-029A. 

Ellington, J. J., F.E. Stancil, Jr., W.D. Payne, and C. Trusty. 1987. Measurement of Hydrolysis 

Rate Constants for Evaluation of Hazardous Waste Land Disposal. Vol. 2. Data on 54 Chemicals. 

U.S. Environmental Protection Agency, Athens, GA. 

Farm Chemicals Handbook. 1987. Meister Publishing Co., Willoughby, OH. 

Fitzhugh, O.G., A.A. Nelson, and J.P. Frawley. 1950. The Chronic Toxicities of Technical Benzene 

Hexachloride and Its Alpha, Beta, and Gamma Isomers. I. Pharmacol. Exp Therap. 100:59-66. 

Forbis, A.D. 1986. Uptake, Deouration, and Bioconcentration of 14C-Lindane by Bluegill Sunfish 

(m. Analytical Bio-Chemistry Laboratories. Act. No. 400561-02. 

Foschi, S., A. Cesari, et al. 1970. Investigation into Degradation and Vertical Movement of 

Agricultural Chemicals in Soil. Not& Mal. Pliante 82(37). 

Hayes, W.J., Jr. 1982. Pesticides Studied in Man. Waverly Press, Inc. Baltimore, MD. 

IRIS. 1989. Integrated Risk Information Service. U.S. Environmental Protection Agency, 

Washington, DC. 

Ito, N., H. Nagaski, and H. Ade. 1975. Development of Hepatocellular Carcinomas in Rats Treated 

with Benzene Hexachloride. J. Natl. Cancer Inst. 54:801-805. 

Kay, B.D., and D.E. Elrick. 1967. Adsorption and Movement of Lindane in Soils. Soil Sci. 

104(5):314-322. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

c-131 
Kirk-Othmer Encyclopedia of Chemical Technology. 1975. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Klaassen, C.D., M.O. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology: The Basic 

Science of Poisons. 3rd ed. MacMillan Publishing Co., New York. 

Litters& C.L., and E. Miller. 1975. Distribution of Lindane in Basins of Control and Phenobarbitol 

Pretreated Dogs at the Onset of Lindane Induced Convulsions. Bull. Environ. Contam. Toxicol. 

13:619. 

Lyman, W.J., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Mills, W.B., D.B. Porcella, M.J. Ungs. S.A. Gherini, K.V. Summers, L. Mok, G.L. Rupp, G.L. 

Bowie, and D.A. Haith. 1985. Water Quality Assessment: A Screening Procedure for Toxic and 

Conventional PolIutants in Surface and Ground Water. U.S. Environmental Protection Agency, 

Athens, GA. EPA 600/6-85/002a. 

Ouellene, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book Co., 

New York. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

Schubert, A. 1969. Investigations on the Induction of Respiration Deficient Yeast Mutants by 

Chemical Herbicides. Z. Allg. Mikrobiol. (Gier.) 9:77. 

Shtenberg, A.I., and C. Mametkulian. 1976, The Effect of Gamma-Isomer of 

Hexachlorocyclohexane (HCHH) on the State of Sexual Glands in Rats. Vap. Pitan (Rus). 4162. 

U.S. EPA. 1985. Guidance for the Registration of Pesticide Products Containing Lindane as the 

Active Ingredient. U.S. Environmental Protection Agency, Office of Pesticide Programs, 

Washington, DC. EPA 54O/RS-86-121. 

U.S. EPA. 1986. Superfund Public Health Evaluation Manual. US. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

U.S. EPA. 1987. Draft of RCRA Facility Investigation (RFI) Guidance. U.S. Environmental 

Protection Agency, Office of Solid Waste, Washington, DC. EPA 53O/SW-87-001. 

U.S. EPA. 1988. Treatabability Manual I. Treatability Data. U.S. Environmental Protection 

Agency, Washington, DC. EPA 600/2-82-OOlA. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. Van Nostrand 

Reinhold, New York. 

C-132 
Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals. Drugs, and Bioiogicals. Merck and Co., Rahway, NJ. 

c-133 
c-134 
MERCURY 

CAS No.: 7439-97-6 

CAS Preferred Nomenclature: Mercury 

Formula: Hg, can occur in elemental and 

inorganic and organic {methyl) forms 

Synonyms and Common Names: Quicksilver 

REGULATORY STATUS 

Ll H BEa 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories 

consumption of fish) (45 FR 793 18) {for inorganic mercury) (IRIS, 1989) 

(IRIS, 1989): adult(70 kg): 

0.153 pg/L long-term and lifetime exposure 

=2lw 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish (40 FR 45663): 

ganisms)(IRIS, 1989): 1 PPm* 

Freshwater Saltwater 

Acute, pg/L 2.4 2.1 

chronic, pg/L 1.2x10-* 2,5x10-* 

+ FDA Action Levels are for use in interstate commerce 

l EPA Drinking Water Standard (for inorganic mercury) (40 CFR 141.11): 

Current Maximum Contaminant 

Level = 0.002 mg/L 

Proposed Maximum Contaminant 

Level = 0.002 mg/L 

Proposed Maximum Contaminant 

LevelGod=0.002 mg/L 

c-135 
Use Restrictions and Bans: 

. All uses as a bactericide or fungicide banned after August 1978 except the following (41 

FR 16497,41 FR 26743,41 FR 36068): 

- treatment of textiles for outdoor use 

- control of brown mold on new lumber 

- in-can preservative in water-based paints 

- for exterior use. 

SOURCES OF MERCURY 

Natural Sources: 

l Mercury occurs in nature (about 3x10-% of earth’s crust) mostly in combination with 

sulfur to fotm more than 25 different minerals. Commercially, the most important 

mineral is cinnabar (HgS), from which elemental mercury (Hg) is extracted (USDI, 

1985). Mercury can occur as elemental Hg, as well as inorganic and organic (organomercurial) forms. It forms complexes with organic ligands, chlorides, and sulfur compounds. 

. Degassing contributes an estimated 25,000 to 150,000 tons per year to the atmosphere, 

compared to about 5,000 tons per year from fossil fuel burning (Klaassen et al.. 1986). 

Total Mercurv Produced: 

l 1.6 million pounds (USDI, 1986). 

Industrial Uses of Mercurv: 

l Electrical applications including the production of mercury cell batteries, mercury vapor 

lamps, thermostats, cathode tubes, and switches. 

l Catalyst in the production of urethane polymers for use in plastics. 

. Cathode in the electrolytic production of chlorine and caustic soda (U.S. EPA, 1987). 

Uses of Mercury In Homes and Businesses: 

. Batteries for small electronic devices such as calculators, hearing aids, and cameras 

9 Thermometers and barometers 

. Amalgamated with silver and tin to form tooth fillings. 

C-136 
Uses as Fungicide/E!actericide (Limited; see Regulatory Status): 

. A fungicide in some exterior water-based paints 

. Formerly as a fungicide in paper products and for the protection of seed grain from 

mildew 

. As a preservative in laboratories. 

FATE IN ENVIRONMENT 

Partitioning: 

b The fate of mercury depends on its speciation, pH, redox conditions, and presence of 

complexing ions including organic ligands, chloride, and sulfhydryl groups (-SH). 

Mercury exists in the 0 (metallic), 1+ (mercurous) and 2+ tmercine) forms. The +1 

species can hydrolyze to form Hg(OH)2 . The 2+ species can hydrolyze to form the 

species Hg(OH>+, Hg(OH)2, and Hg(OH)3 (Rubin, 1976). 7’he relative amotms of each 

species are dependent on pH. 

9 Examples of Hg complexes include Hg(OH)2 under alkaline conditions and HgCl2 under 

acidic conditions. In alkaline sediments under moderately reducing conditions, dimethyl 

mercury, which is insoluble and highly volatile, can form. At neutral and lower pH 

values, monomethyl mercury can form. Under strongly reducing conditions (e.g., in the 

presence of hydrogen sulfide (H2S)), mercury can precipitate as HgS, which is insoluble 

(Nriagu, 1979). 

Persistence: 

l Mercury is readily sorbed to soil organic matter, clays, and hydrous metal oxides with 

the exception of some organic chloride-Hg complexes, e.g. CH3HgCl. Methylmercuric 

chloride has a KoW value of about 2.0 (Medeiros, 1980). Mercury is also bioaccumulated. BCF values for inorganic mercury range from 1,800 to 5,000. BCF values for 

organic mercury are higher (10,000 to 82,000). Most of the mercury in fish is present 

in the methyl form. 

l Mercury is biologically methylated and in limited amounts may be lost from soils by 

volatilization (Lyman et al., 1987). 

HEALTH EFFECTS 

Carcinogenicity : 

l Mercury has not been shown to cause cancer in humans. 

c-137 
. Rats have developed local tumors at the point of injection of metallic mercury (U.S. 

EPA, 1984). 

l The EPA designates mercury as a Group D chemical, not classified (U.S. EPA, 1984). 

,Mutagenic Activity: 

l Methyl mercury was shown to be a weak mutagen in experiments with fruit flies (U.S. 

EPA, 1981). Mercuric salts were not mutagenic in tests using nonmammalian cells, but 

results using mammalian cells were inconclusive. 

ReDrOduCtiVe Effects: 

l Both inorganic and organic forms of mercury are toxic to developing fetuses. The fetal 

nervous system is particularly sensitive, with mercury disrupting and delaying nerve cell 

development. Fetuses chronically exposed (low doses over long time periods) to organic 

mercury are born mentally retarded and exhibit cerebral palsy-like symptoms (Marsh, 

1987). 

Other Toxkological Effects: 

l Mercury toxicity in humans produces a number of different symptoms depending on 

whether the exposure is of a short-term, high-dose (acute) type or long-term, low-dose 

(chronic) type. Elemental mercury vapor produces an acute pneumonitis. Inorganic 

mercury salts can cause acute gastrointestinal distress and renal failure. (The lethal dose 

of mercuric chloride in humans is 1 to 4 g.) Both of these forms, as well as the organic 

mercurials, produce neurologic effects after chronic exposure to mercury. Eye and skin 

irritation can also occur (Sittig, 1985). 

+ Symptoms such as numbness of the extremities, tremors, spasms, personality and 

behavior changes, difficulty in walking, deafness, blindness, and death have been 

associated with the tong-term ingestion of mercury-contaminated fish. (U.S. EPA, 

1981). 

Toxkological Effects Indices: 

l RfD (Reference Dose): 0.002 mg/kg/day for inorganic mercury compounds and 0.0003 

mgAcg/day for alkyl (organic forms) or mixed alkyl-inorganic mercury (U.S. EPA, 

1986). 

l TWA-TLV (Time-weighted average, threshold limit value for occupational exposures): 

0.01 mg/m3 alkyl mercury for skin exposure and 0.05 mg/m3 for vapor exposure 

(ACGM, 1986). 

C-138 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0: 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p& 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant @ 25OC 

(atm l m3/mo1): 

Hydrolysis Rates: 

Log (Octanol-Water Partition 

Coefficient), log KOW: 

Partition Coefficient, Kp (mWg): 

{Inorganic Hg) 

Fish Bioconcentration Factor, 

BCF: 

200.6 

liquid 

-38.87 

356.72 

13.534 (25OC) 

N/A 

0.056 (25OC) 

2x10-3 (25OC) 

Hgo 6.97x1O-3 

(CH3)2Hg = 7.45~10~ 

Hg(OH)2 = 7.2x10-* 

l+ and 2+ forms 

hydrolyze, specific rate 

constants not found 

CH3HgCl = 0.3 

= 0.4 

1,000-1x106 l/kg 

1800-4994 

(inorganic) 

lO,OOO-8 1,670 

(organic) 

5,500 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Lindquist et al., 1984 

Lindquist et al., 1984 

Rubin, 1976 

Medeiros et al.,1980 

Halbach, 1985 

Gherini and 

Rajashenkar. 1975 

U.S. EPA, 1985 

U.S. EPA, 1985 

Olson et al., 1975 

U.S. EPA, 1980 

c-139 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Bloom, N. 1988. Determination of Methylmercury in Water at the Femtomolar (pg/L) Level 

Following Aqueous Phase Ethylation with Sodium Tetraethylborate. EPRI Project Report. Palo 

Alto. CA. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. II. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/79-029b. 

Gherini, S.A., and P. Rajashenkar, 1975. A Study of the Water Quality Impact of the Lmplementation of Air Quality Standards. U.S. Environmental Protection Agency, Washington, DC. Contract 

No. 68-O l-2243. 

Halbach, S. 1985. The Octanol Water Distribution of Mercury Compounds. Short Communication Arch. Toxicol. 57: 139-141. 

BUS. 1989. Integrated Risk Information System Database. U.S. Environmental Protection Agency, Washington, DC. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Klaassen, C.D., M.D. Amdur, and I. Doull, eds. 1986. Casarett and Doull’s Toxicology, The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Lindquist, O., A. Jemelov, K. Johansson, and H. Rodhe. 1984. Mercury in the Swedish Environment: Global and Local Sources. Report No. 91-7590-154-4. Prepared for the National Swedish 

Environment Board. 

Lyman, W.L., I. Bodek, W.F. Reehl, and D.H. Rosenblatt. 1987. Methods for Estimating 

Physicochemical Properties of Inorganic Chemicals of Environmental Concern. U.S. Army Medical Research and Development Command, Fort Detrick, MD. Contract No. DAMD 17-83-C-3274. 

Marsh, D.O. 1987. Dose-Response Relationships in Humans: Methyl Mercury Epidemics in Japan 

and Iraq. In: The Toxicity of Methyl Mercury. (C.U. Eccles and 2. Annau, eds). Johns Hopkins 

University Press, Baltimore, MD. 

Medeiros D., L. Cadwell, and R. Preston. 1980. A Possible Physiological Uptake Mechanism of 

Methylmercury by the Marine Bloodworm (Glvcera . Bull. Environm. Contam. 

Toxicol. 24: 97- 10 1. 

c-140 
Nriagu, J.O.. ed. 1979. The Biogeochemistry of Mercury in the Environment. ElsevieriNorth-Holland Biomedical Press, New York. 

Olson, G.F.. D.J. Mount, V.M. Snarski, and T.W. Thorslund. 1975. Mercury Residues in Fathead 

Minnows, PimDehales Rafinesque, Chronically Exposed to Methyl Mercury in Water. 

Bull. Environ. Contam. Toxicol. 14(2). 

Rubin, A.J., ed. 1976. Aqueous-Environmental Chemistry of Metals. Ann Arbor Science Publishers, Inc.. Arm Arbor, MI. 

Sittig, M. 1985. Handbook of Toxic and Hazardous Chemicals and Carcinogens. 2nd ed. Noyes 

Publications, Park Ridge, NJ. 

U.S. Department of the Interior (USDI), Bureau of Mines. 1985. Minerals Facts and Problems. 

1985 ed. Bulletin 675, U.S. Government Printing Office, Washington, DC. 

U.S. Department of the Interior (USDI), Bureau of Mines. 1986. Mineral Commodity Summaries 

1986. U. S. Government Printing Office, Washington, DC. Publication No. 1986-606-225. 

U.S. EPA. 1980. Ambient Water Quality Document U.S. Environmental Protection Agency, 

Washington, DC. EPA 440/5-80 Series. 

U.S. EPA. 1981. An Exposure and Risk Assessment for Mercury. US. Environmental Protection 

Agency, Office of Water Regulations and Standards, Washington, DC. EPA-44014-85-01 1. 

U.S. EPA. 1984. Health Effects Assessment for Mercury. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. EPA-540/l-86-042. 

U.S. EPA. 1985. Ambient Aquatic Life Water Quality Criteria for Mercury. U.S. Environmental 

Protection Agency, Office of Research and Development, Duluth, MN. PB85-22745. 

U.S. EPA. 1986. Superfund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

c-141 
OBSERVATIONS AND EFFECTS ON PISCIVOROUS WILDLIFE 

Mercury is toxic to mink at diet concentrations of 1 to 2 ppm (Wren, 1989). This finding is consistent 

with the lethal dose reported by the State of Wisconsin (WDHSS, 1988). 

The effects of mercury on piscivorous wildlife are summarized in the following table: 

Effects of Mercury Concentrations on Piscivorous Wildlife 

Animal 

Mink 1 .O mg/kg 

(diet) 

Death WDHSS, 1988 

Mink 1-2 ppm (diet) Death Wren, 1989 

River Otter >2.0 mg/kg 

(diet) 

Death WDHSS, 1988 

REFERENCES 

WDHSS (Wisconsin Department of Health and Social Services). 1988. Technical Support Document for Chapter MR 105 of the Wisconsin Administrative Code. Division of Health, Madison, 

WI. 

Wren, C.D. 1989. Personal communication. BAR. Environmental. Nicholas Beaver Park, RR% 

Guelph, Ontario. Canada. 

C-142 
METHOXYCHLOR 

CAS No.: 72-43-5 

CAS Preferred Nomenclature: 

Benzene,l,l’-(2,2,2-trichloroethytidene) 

bis (4-methoxy)- 

Empirical Formula: C1&I15Cl302 

Synonyms and Common Names: 

- Methoxy-DDT - Marlate 

- DMDT - Dianisyl trichloroethane 

- Maralate - Dimethoxy-DT 

- p,p’-Dimethoxydiphenyl - Metox 

- trichloroethane 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human . EPA Drinking Water Health Advisories 

consumption of water and fish)(U.S. (U.S. EPA, 1987; PHRED, 1988): 

EPA, 1987): chilp (10 kg): 

100 pg/L 1 day exposure = 6.0 mg/L 

10 day exposure = 2.0 mg/L 

long-term exposure = 0.5 mg/L 

adub (70 kg): 

long-term exposure = 2.0 mg/L 

lifetime exposure = 0.4 mg/L 

. EPA Ambient Water Quality Criteria . EPA Tolerance Levels for Food (40 

(for protection of aquatic organisms): CFR 180.120): 

- Saltwater l-14 ppm 

Acute, j~g/L - - 

chronic, pg/L 0.03 0.03 

c-143 
. EPA Drinking Water Standards (50 FR l Food and Drug Administration Action 

46936; IRIS, 1989): Level for Fish 

Current Maximum Contaminant None established at present 

Level = 0.1 mg/L 

Proposed Maximum Contaminant 

Level = 0.4 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0.4 mg/L 

Use Restrictions and Bans: 

m None found. 

SOURCES OF METHOXYCHLOR 

Total Methoxychlor Produced: 

l Methoxychlor is an organochlorine pesticide with a similar chemical structure to DDT. 

It was first introduced in 1945. 

. In 197 1.9.9 million pounds were produced by the companies Chemical Formulations, 

DuPont, and Prentiss (Ouellette and King, 1977). 

. By 1982, very little methoxychlor was being produced. Current data are unavailable, 

but the volume produced by the two listed producers, Drexel Chemical Company and 

Kincaid Enterprises, is likely to be small (SRI, 1986; Green et al., 1987). 

Uses of Methoxychlor: 

l Like DDT, methoxychlor is effective against a wide range of insects that affect fruits, 

vegetables, forage crops, and livestock (Hayes, 1982; McEwen and Stephenson, 1979). 

. Hundreds of products containing methoxychlor are registered for insect control in foliar 

treatment, dormant application, seed or soil treatment. and post-harvest application of 

many crops (U.S. EPA, 1986). 

+ Methoxychlor is used primarily to control houseflies, blackflies, and mosquitoes, in 

areas of human habitation including hotels, bakeries, meat processing plants, flour mills, 

and dairy barns (Worthing, 1983; U.S. EPA, 1986; McEwen and Stephenson, 1979). 

+ Mosquito control uses also include methoxychlor treatment of stagnant ponds, streams, 

and other aquatic recreation areas (U.S. EPA, 1986). 

l Methoxychlor is also used in mothproofing (U.S. EPA, 1986). 

w None found. 

C-i44 
Partitionine: 

l Based on its physicakhemical properties, methoxychlor is estimated to be volatile (H 

= 1.5~10-~ atm l m3/mole), strongly sorbed tosoil (&*47,900) and hasa high potential 

for bioaccumulation (BCF = 8,300). although some empirical datashow a more moderate 

potential for bioaccumulation. 

Persistence: 

l Methoxychlor is considered to be moderately biodegradable (Wolfe et al., 1977). 

l Methoxychlor is estimated to have a half-life for direct photolysis in water (in the central 

U.S.) of 4.5 months, and also undergoes indirect photolysis (Wolfe et al., 1977); 

photolysis half-lives of 2-5 hours have been observed in river water (TDB, 1985). The 

rate of hydrolysis has been found to be independent of pH under environmental 

conditions, with a half-life of about 1 year at 27OC (Wolfe et al., 1977). 

HEALTH EFFECTS 

Cardnogenicity: 

l The evidence for methoxychlor carcinogenicity is inconclusive, according to the EPA 

Carcinogen Assessment Group’s review of aNational Cancer Institute Bioassay (HSDB, 

1988). EPA has not yet classified its carcinogenic potential (PHRED, 1988). 

l No cancers were observed in four experiments with rats fed 1,000 mgkg or in one mouse 

feeding experiment (IARC, 1979). 

Mutagenic Activity: 

l Methoxychlor was found not to be mutagenic in bacterial and yeast cell assays as well 

as in a mouse dominant lethal test (IARC, 1979). 

l It was weakly positive in a mammalian cell transformation assay (HSDB, 1988). 

Reproductive Effects: 

l Adverse reproductive effects have been reported. In studies with rats consuming a 

dietary level of 1% methoxychlor has produced testicular atrophy, inhibition of spermatogenesis, and arrested folliculogenesis (IARC, 1979; HSDB, 1988). 
l Methoxychlor is also reported to be fetotoxic in rats, causing wavy ribs, but only at doses 

(100-400 mgkg) causing maternal toxicity. There is no evidence of any teratogenesis 

at lower doses (IARC, 1979; Hayes, 1982; HSDB, 1988). 

Other Toxicological Effects: 

l In man, acute, short-term, high doses, up to 2 mg/kg/day, have not been shown to cause 

any adverse effects. 

l Animals exposed to high doses of methoxychlor have exhibited a variety of symptoms. 

Dogs fed 2,000 or 4,000 mg/kg for 2 years developed nervousness, tremors and 

convulsions. Rats had similar central nervous system effects as well as severely retarded 

growth (Hayes, 1982; HSDB, 1988). Kidney injury and uterine and mammary enlargement were observed in pigs, while monkeys had liver and intestinal damage (IARC, 

1979; HSDB, 1988). 

Toxicological Effects Indkes: 

l Adjusted Reference Dose for drinking water: 1.7 mg/L (50 FR 46936). 

l TWA-TLV (time-weighted average, threshold limit value) for occupational exposure: 

10 mg/m3 (ACGIH, 1986). 

. Oral LD50: rat, 5-7 mgkg; mouse, 1.8 mgkg (IARC, 1979; HSDB, 1988). 

c-146 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 345.7 

Physical State @ 20°C: colorless crystals, solid 

Windholz, 1983 

Hayes, 1982 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

89 Worthing, 1983 

416 (talc.) 

1.41 (25OC) 

N/A 

1x10” 

1.3x106(200C) 

(talc.} 

Lyman et al., 1982 

Hartley & Kidd, 1983 

PHRED, 1988 

Lyman et al., 1982 

Henry’s Law Constant, 

H @ 25OC (atm l m3/mol): 1 .5x1o‘5 (talc.) Lyman et al., 1982 

Log (Gctanol-Water Partition 

Coefficient), log Kow: 4.68 PHRED, 1988 

Soil Adsorption Coefficient, K&nL/g): 8~10~ PHRED, 1988 

Fish Bioconcentration Factor, BCF: l.9x102-1.6x103 

(expd.) 

8300 

Kenaga, 1980 

PHRED, 1988 

c-147 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Green, M.B., G.S. Hartley, and T.F. West. 1987. Chemicals for Crop Improvement and Press 

Management. 3rd ed. Pergamon Press, Oxford, England. 

Hartley, D., and H. Kidd, eds. 1983. The Agrochemicals Handbook. The Royal Society of 

Chemistry, Nottingham, England. 

Hayes, W.J., Jr. 1982. Pesticides Studied in Man. Waverly Press, Inc., Baltimore, MD. 

HSDB. 1988. Hazardous Substances Data Base. Computer printout: Methoxychlor. Retrieved 

May 16.1988. National Library of Medicine, Bethesda, MD. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Kenaga, E.E. 1980. Correlation of Bioconcentration Factors of Chemicals in Aquatic and Terrestrial Organisms with Their Physical and Chemical Properties. Environ. Sci. Technol. 14:553- 

556. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Matsamura, F. 1985. Toxicology of Insecticides. 2nd ed. Plenum Press, New York. 

McEwen, F.L., and G.R. Stephenson, 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, New York. 

Ouellette, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co.. New York. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

C-148 
Toxicology Data Bank (TDB) Database. 1985 1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1986. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

US. EPA. 1987. Methoxychlor Health Advisory. U.S. Environmental Protection Agency, Office 

of Drinking Water, Washington, DC. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs and Biologicals. 

10th ed. Merck & Co., Rahway, NJ. 

Wolfe, N.L., R.G. Zepp, D.F. Paris, G.L. Baughman, and R.C. Hollis. 1977. Methoxychlor and 

DDT Degradation in Water: Rates and Products. Environ. Sci. Technol. 11: 1077- 108 1. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-149 
C-150 
MIREX 

CAS No.: 2385-85-5 Q 

CAS Preferred Nomenclature: 

1,3,4-Metheno- lH-cyclobuta(cd) a a 

pentalene,l,la,2,2,3,3a,4,5,5,5a,5b,6- 

Cl c’ Cl dodecachloro-octahydro- Cl 

Empirical Formula: C lOCll2 a fl 

Cl Cl 

a 

Synonyms and Common Names: C,*C’,2 

- Dechlorane - Perchloropentacyclodecane 

- Hexachlorocyclo- - Perchlorodi-homocubaane 

- pentadiene dime - Feniamicide 

- Paramex 

- Dodecachlorooctahydro- 1,3,4-metheno-2H-cycfobutal (cd) pentalene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories: 

consumption of fish): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish (43 FR 14736): 

ganisms)(IRIS, 1989): 0.10 ppm* 

Freshwater Saltwater 

Acute, @/L - - 

Chronic, pg/L 0.001 0.00 1 

* FDA Action Levels are for use in interstate commerce 

l EPA Drinking Water Standards Maxiurn Contaminant Level: 

None established at present 

Use Restrictions and Barn:: 

. All registered uses were cancelled as of 1977 (41 FR 56703). 

C-151 
l All existing stock was not to be sold. distributed, or used after June 30, 1978 (NAS, 

1978). 

SOURCES OF MIREX 

Total Mirex Produced: 

. 3.3 million pounds were produced by Hooker Chemicals and Plastics Co. between 1959 

and 1975 (Suta, 1977). Twenty-five percent was used as a pesticide and the remainder 

as a fire retardant. Commercial production stopped in 1978. 

Uses of Mirex: 

l Mirex was used primarily for the control of the imported fire ant in eight southeastern 

States from 1962 to 1975. Approximately 250,000 kg were used to treat 14 million acres 

(NAS, 1978; Kutz et al., 1985). Mirex was also used in Hawaii to control the pineapple 

mealy-bug (Suta, 1977). 

l Mirex was used as a fire retardant in plastics, rubber, paint, paper, and electrical products 

(Kutz et al., 1985; Windholz, 1983). 

Other: None identified. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, mirex is predicted to have a relatively low 

volatility from water (H = 2.2 x 10-5 atm l m3/mol at 25OC), a low volatility from surface 

soil (P/S Koc = 1.3 x lo-l2 mm Hg l Wmg, corresponding to an estimated volatilization 

half-life of ~30 years), a strong adsorption to soils and sediments (Kow = 199,500 and 

& = 2.4 x 107), and a high potential for bioaccumulation (BCF = 2.6 x lo3 - 4.1 x 104). 

Persistence: 

. Mirex is thermally and chemically very stable and resistant to biodegradation (Bell et 

al., 1978). There is some evidence that mirex can be biotransformed into chlordecane 

(Kepone) in soil (Klaassen et al., 1986). However, mirex applied at 1 lb/acre to a 

Mississippi soil was reported to have a 50% dissipation time of ~2.5 years (State of 

Mississippi, 1982 as cited by EPA, 1982). Mirex appears to be persistent in the aquatic 

environment as evidenced by no reported significant decreases in the concentration of 

mirex in a water/sediment system over a 130-day period (State of Mississippi, 1982 as 

cited by EPA, 1982). 

c-152 
+ Photolysis of mirex in water can occur, but at a slow rate (Verschueren, 1983). The rate 

determined experimentally using river water in sunlight was 0.004Uday (Smith et al., 

1978). 

HEALTH EFFECTS 

Carcinogenicity: 

l Hepatomas and liver-cell carcinomas were observed in mice and rats fed mirex in their 

diet, Mirex has been classified as a probable human carcinogen (2b) by IARC (1979). 

The carcinogenic data for mirex are presently under review by the U.S. EPA (IRIS, 

1989). 

l The results of one animal cancer study (Ulland et al., 1977) have been analyzed using a 

dose-response model not typically used by EPA. This one-hit model was used to derive 

a possible carcinogenic potency factor of 0.354 (mg/kg/day)-’ (U.S. EPA, 1982). 

Mutagenic Activity: 

. Negative in dominant lethal assay in mice (IARC, 1979). Not generally active in 

short-term tests (WHO, 1984). 

Reproductive Effects: 

0 Some studies have reported that mirex is fetotoxic (25 @kg) and teratogenic (causing 

cleft palate, heart defects, cataracts) to rats (6 mg/kg/day). Also, fewer and less viable 

offspring were born to mice fed 1.8 mg/kg for 3 months (WHO.1984; Klaassen et al., 

1986). Voles also had decreased pup survival when exposed to mirex in the diet (IRIS, 

1988). Further studies must be done to confirm these results (IRIS, 1988). 

Other Toxicological Effects: 

. Acute hepatotoxicity (liver toxicity) was noted in rats after oral administration of mirex 

(IARC, 1979). Liver hypertrophy observed in rats fed 1 mg/kg for 14 days WHO, 

1984). 

l 

Chickens exposed to mirex had depressed levels of certain types of antibodies (IgG and 

IgM) (IUaassen et al., 1986). 

Toxicological Effects Indices: 

l Cancer Potency Factor (CPF): 1.8 (mg/kg/day)-’ (HEAST, U.S. EPA, 1989). 

c-153 
. Reference Dose (RfD): 2 x low6 mg/kg/day (IRK 1989). 

. Oral LDso: rat, 740 mg/kg (IARC, 1979). 

c-154 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 545.6 Windholz. 1983 

Physical State @ 2OC: solid, snow- Verschueren, 1983 

white crystals 

Melting Point (“C): 485 (decomp.) Windholz, 1983 

Boiling Point (“C): N/A 

Density/Specific Gravity: N/A 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 0.2 (24OC) PHRED, 1988; 

Verschueren, 1983 

Vapor Pressure, P (mm Hg): 6~10-~ (25OC) TDB, 1985 

Henry’s Law Constant, 

H @ 25°C (atm l m3/mol): 2.2x 1o-5 Lyman et al, 1982 

Log (Gctanol-Water Partition 

Coefficient), log ROW: 5.3 Lyman et al., 1982 

Soil Adsorption Coefficient, I& (mL/g): 2.4x107 PHRED, 1988 

Fish Bioconcentration Factor, BCF: 2.6~10~~4.1~10~ Verschueren, 1983 

(apti. 1 

18,100 PHRED, 1988 
Bell, M.A., R.A. Ewing, G.A. Lutz, and E.G. Alley. 1978. Review of the Environmental Effects 

of Pollutants: I. Mirex and Kepone. (NTIS Abstract). EPA Health Effects Research Laboratory, 

Cincinnati, OH. EPA/600/i -78-O 13. NTIS PBSO- 125958. 

Green, M.B., G.S. Hartley, and T.F. West. 1987. Chemicals for Crop Improvement and Pest 

Management. 3rd ed. Pergamon Press, Oxford, England. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1988. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

KIaassen, C.D., M.D. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology, The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Kutz, F.W., S.C. Strassman, C.R. Stroup, J.C. Cat-m, C.C. Leininger, D.L. Watts, and C.M. 

Sparacino. 1985. The Human Body Burden of Mirex in the Southeastern United States. J. Toxicol. 

and Environ. Health, 15:385-394. 

Lyman, W.T., W.E. Reehl, D.E. Rosenblatt. 1982. Handbook of Chemical Estimation Methods. 

McGraw-Hill Book Co., New York. 

NAS (National Academy of Sciences). 1978. Kepone/Mitex/Hexachlorocyclopentadiene: An 

Environmental Assessment. National Academy of Sciences, National Research Council, 

Washington, DC. NTIS PB 280289. 

Ouellette, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co.. New York. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

State of Mississippi. 1982. Environmental Fate Studies in support of an emergency request for use 

of mirex on fire ants. 

Suta, B-E. 1977. Human Population Exposures to Mirex and Kepone. EPA-60011-78-045. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 
Ulland, B.M., N.P. Page, R.A. Squire, E.K. Weisburger, and R.L. Cyphor. 1977. A carcinogenicity 

assay of mirex in Charles River CD rats. J. Natl. Cancer inst. 58:133-140. 

U.S. EPA. 1982. Office of Pesticides Programs Reviews of Environmental Fate Studies submitted 

by the State of Mississippi in support of an emergency request for use of mirex on fii ants. 

U.S. EPA. 1989. Health Effects Assessment Summary Tables (HEAST). U.S. Environmental 

Protection Agency, Office of Solid Waste and Emergencies Response, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

WHO (World Health Organization). 1984. Mirex. Environmental Health Criteria 44: l-70. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A world compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-157 
MIREX 

OBSERVATIONS AND EFFECTS ON PISCl-VOROUS WILDLIFE 

EPA banned the use of mirex in 1978, in part because of its detrimental effects on fish and wildlife 

(Eisler. 1985). Eisler’s review provides a good summary of mirex hazards to nontarget species and 

concentrations found in wildlife. 

High concentrations of mirex in eggs were blamed for the low reproductive success of Lake Ontario 

herring gulls in the early 1970’s (Gilman et al., 1977,1978). In 1975, the reproductive success of 

herring gulls in Lake Ontario colonies was only one-tenth that of colonies on the other four Great 

Lakes (Gilman 1977, 1978). The mean concentration of mirex in eggs from one Lake Ontario 

Lake Ontario was the only Great Lake contaminated with mirex (Kaiser, 1978; NAS, 1978), and 

both Gilman et al. (1977, 1978) and Norstrom et al. (1980) suggested that a high percentage of the 

mirex in the eggs originated from Lake Ontario fish. 

Differences in feeding habits have been related to differences in mirex concentrations in eggs of 

three bird species in Maine: the common eider, herring gull, and black-backed gull (Szaro et al., 

1979). Eggs of the black-backed gull had levels of DDE and PCBs greater than those in the eggs 

of the herring gull, which, in turn, were higher than those in the eggs of the common eider. Mirex 

was detected only in the eggs of the black-backed gull (up to 0.26 ppm) (Szaro et al., 1979). Szaro 

et al. (1979) attributed the higher levels of contaminants in the blacked-back gull to its predatory 

and scavenging feeding habits. 

Based on a study of herring gulls and predation on alewives, Norstrom et al. (1978) estimated a 

bioaccumulation factor of 50 for mirex in gull eggs. 

Mirex residues have been detected in the brains and tissues of various piscivorous birds collected 

nationwide, such as bald eagles (Barbehenn and Reichel, 1981) and herons (Ohlendorf et al., 1981). 

However, in both studies, mirex concentrations were recorded at nonhazardous levels. 

Mirex has also been detected in eggs of the American crocodile (up to 0.02 ppm) (Hall et al., 1979). 

The State of New York proposed a fish flesh criterion for mirex at 0.33 ppm to protect piscivorous 

wildlife. This criterion was based on studies of rats (Gaines and Kimbrough, 1969), prairie voles 

and old field mice (Hyde, 1972), and mallards (Newell et al., 1987; Schafer et al., 1983). 

The effects of mirex on piscivorous wildlife are summarized in the following table: 

C-158 
Effects of Mirex Concentrations on Piscivorous WiIdiife 

Animal Concentration 

Piscivorous 

Wildlife 

0.33 ppm (diet) estimated Newell et al. 

NOEL 1987 

0.373 ppm (diet) cancer risk 

of lo-2 

Newell et al. 

1987 

REFERENCES 

Barbehenn. K.R., and in.L. Reichel. 198 1. Organochlorine Concentrations in Bald Eagles: 

Brain/Body Lipid Relations and Hazard Evaluation. J. Toxicol. Environ. Health 8:325-330. 

Eisler, R. 1985. Mirex Hazards to Fish, Wildlife and Invertebrates: A Synoptic Review. U.S. Fish 

Wildl. Serv. Biol. Rep. 85( 1.1). 

Gaines, T., and R. Kimbrough. 1969. The Oral Toxicity of Mirex in Adult and Suckling Rats. 

Toxicol. Appl. Pharmacol. 14:631-632. (As cited in Newell et a.l.,1987) 

Gilman, A.P., G.A. Fox, D.B. Peakall, S. M. Teeple, T.R. Carroll and G.T. Katmes. 1977. 

Reproductive Parameters and Egg Contaminant Levels of Great Lakes Herring Gulls. J. Wildl. 

Manage. 41:458-468. (As cited in Eisler, 1985) 

Gilman, A.P., D. J. Hallett, G.A. Fox, L.J. Allan, W.J. Learning, and D.B. Peakall. 1978. Effects 

of Injected Organochlorines on Naturally Incubated Herring Gull Eggs. J. Wildl. Manage. 42:484- 

493. (As cited in Eisler, 1985) 

Hall, R. J., T. E. Kaiser, in. B. Robertson, Jr., and PC. Patty. 1979. Organochlorine Residues in 

Eggs of the Endangered American Crocodile (Crocodvlusacutus). Bull. Environ. Contam. Toxicoi. 

23:87-90. 

Hyde, K. 1972. Studies of the Responses of Selected Wildlife Species to Mirex Bait Exposure. 

Ph.D. thesis, Louisiana State University, Baton Rouge. (As cited in Eisler, 1985) 

Kaiser, K.L.E. 1978. The Rise and Fall of Mirex. Environ. Sci. Technol. 12:520-528. (As cited 

in Eisler, 1985) 

NAS (National Academy of Science). 1978. Scientific and Technical Assessments of Environmental Pollutants. Kepone/Mirex/Hexachlorocyclopentadiene: An Environmental Assessment. 

National Academy of Science, Washington, DC. (As cited in Eisler, 1985) 

c-159 
Newell, A.J., D.W. Johnson, and L.K. Allen. 1987. Niagara River Biota Contamination Project: 

Fish Flesh Criteria for Piscivorous Wildlife. NY Dept. Environ. Conserv., Div. Fish Wildl.. Bureau 

Environ. Protection. Tech. Rep. 87-3. 

Norstrom, R.J., D.J. Hallett, and R.A. Bonstegard. 1978. Coho Salmon (m 

and Herring Gulls w arsentatus) as Indicators of Organochlorine Contamination in Lake 

Ontario. J. Fish. Re. Board Canada 35: 1401- 1400. (As cited in Eisler, 1985) 

Norstrom, R.J., D.J. Hallett, F.1. Onuska, and M.E. Comba. 1980. Mirex and Its Degradation 

Products in Great Lakes Herring Gulls. Environ. Sci. Technol. 14:860-866. (As cited in Eisler, 

1985) 

Ohlendorf, H.M., D.M. Swineford, and L.N. Locke. 1981. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4):125-135. 

Schafer, E., Jr., W. Bowles, and J. Hulbert. 1983. The Acute Oral Toxicity, Repellency and Hazard 

Potential of 998 Chemicals to One or More Species of Wild and Domestic Birds. Arch. Environ. 

Contam. Toxicol. 12:335-382. (As cited in Newell et al., 1987) 

Szaro, R.C., N.C. Coon, and E. Kolbe. 1979. Pesticide and PCB of Common Eider, Herring Gull 

and Great Black-Backed Gull Eggs. Bull. Environ. Contam. Toxicol. 22:394-399 

We&oh. D.V., P. Mineau, and D.J. Hallett. 1979. Organochlorine Contaminants and Trends in 

Reproduction in Great Lakes Herring Gulls, 1974-1978. Trans. N. Am. Wildl. Nat. Resour. Conf. 

44:543-557. 

C-160 
NITROFEN 

CAS No.: 1836-75-5 

CAS Preferred Nomenclature: 

Benzene,2,4-dichloro-2-(4-nitrrophenoxy)- 

Empirical Formula: C 1zH7C12NO2 

Synonyms and Common Names: 

- NIP 

- Nitrophen 

- F-W-925 

- TOK E-25 

- Nitrochlor 

- 2,4-Dichlorophenyl-.para.-nitrophenyl ether 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories: 

consumption of fish): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l EPA Tolerance Levels (50 FR 37850) 

(for protection of aquatic organisms): All tolerances revoked 9/l 8/85 

None established at present 

l EPA Drinking Water Standard Maxi- . Food and Drug Administration Action 

mum Contaminant Level: Level for Fish: 

None established at present None established at present 

Use Restrictions and Bans: 

l All uses of nitrofen, a selective herbicide, were cancelled voluntarily by 1984 (40 FR 

2151). 

SOURCES OF NITROFEN 

Total Ni trofen Produced: 

l Nitrofen is no longer produced or sold in the United States (Ouellette and King, 1977). 

C-161 
Uses of Nitrofen: 

l Prior to 1984, nitrofen was used as a selective herbicide to control weeds in various 

crops, including vegetables, cereal, grains, sugar beets, rice, and some ornamental plants 

(Worthing. 1983). 

er SourceS; None identified. 

NITROFEN OBSERVED IN THE ENVIRONMENT 

. No data available. 

FATE IN ENVIRONMENT 

Partitioning: 

+ Based on estimates of physical/chemical properties, nitrofen strongly sorbs to soil ( 9 w 

KJ39.000) and has a high potential for bioaccumulation (BCF estimated as 1.6x10 

Nitrofen volatiiizes at a low rate (H = 3. lx 10-6 atm l m3/mol). 

1. 

Per&term: 

l Nitrofen can biodegrade under both aerobic and anaerobic conditions. In one experiment, a 70% loss of nitrofen present in soil at a concentration of 10 ppm (incubated at 

30°C) occurred after 10 days, which represents a decay rate of O.l2/day. Nitrofen 

applied in a flooded paddy field (anaerobic conditions) had a half-life of 16 days (TDB, 

1986). Under these conditions, the nitro group (N@) is reduced to NH2 (Grover, 1988). 

. Nitrofen solutions and aqueous suspensions can undergo rapid photolysis (TDB, 1986). 

HEALTH EFFECTS 

Cardnogenidty: 

l The U.S. EPA has not classified the potential carcinogenicity of nitrofen. However, 

IARC (1983) considers that the available information is sufficient evidence to identify 

nitrofen as carcinogenic in experimental animals. 

. Mice fed nitrofen displayed a significant increase in the incidence of liver carcinomas 

(IARC, 1983). 

l Nitrofen administered in high doses to rats also resulted in various types of tumors at 

different anatomical sites (IARC, 1983). 

C-162 
MutaPe& Activitv: 

l Nitrofen was found to be mutagenic in mm. Negative results were 

obtained when nitrofen was tested in m subtilis and rat and mouse bone cells 

(IARC, 1983). 

Reproductive Effects: 

. In rats, nitrofen increased the incidence of stillbirths and reduced the survival rate of 

newborns (IAEX, 1983). Poor survival was due to heart, diaphragm, and kidney 

malformations, as well as lung immaturity (IARC, 1983; Klaassen et al., 1986). 

. Nitrofen produced similar birth defects in mouse fetuses (IARC, 1983). 

Other Toldcologikal Effects: 

. Increased liver weight, neurological symptoms, and respiratory distress generally occur 

after rats are exposed to nitrofen (IARC, 1983). 

Toxicological Effects Indices: 

. Oral LD5o: rats, 410-3580 mgkg (IARC, 1983). 

C-163 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“0: 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L) 

Vapor Pressure, P (mm Hg) 

Henry’s Law Constant, H @ 25°C 

(atm l m3/mol) 

Log (Octanol-Water Partition 

Coefficient), log Kow: 

Soil Adsorption Coefficient, 

&dmUg): 

Fish Bioconcentration Factor, BCF: 

284.1 

colorless 

crystals 

70-7 1 

180-190 @ 

0.25 mm Hg 

1.3 (liquid @ 

90°C) 

NIA 

0.7- 1.2 (22°C) 

8x10” (4OOC) 

3.1xlO-(j (talc.) 

5.53 (talc.) 

5.9x lo4 (talc.) 

1 .6x104 (talc.) 

Windholz, 1983 

Hartley and Kidd, 1983 

Hartley and Kidd, 1983 

Hartley and Kidd, 1983 

Hartley and Kidd, 1983 

Worthing, 1983 

Worthing, 1983 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

C-164 
Grover, R., ed. 1988. Environmental Chemistry of Herbicides. Vol. I, CRC Press, Inc., Boca 

Raton. FL. 

Hartley and Kidd, eds. 1983. Herbicide Handbook. 5th ed. Weed Science Society of America, 

Champaign, IL. 

IARC (International Agency for Research on Cancer). 1983. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 30. IARC, Lyon, France. 

IUaassen, C.D., M.O. Arndur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology: The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Ouellette, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co., New York. 

Toxicology Data Bank (TDB) Database. 19851986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologica.Is. 10th ed. Merck Co., Inc., Rahway, NJ. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

C-165 

NONACHLOR 

(cis- and trans- isomers) 

CAS No.: cis - 5 103-73- 1 

tram - 39765-80-5 

combined - 3734-49-4 

CAS Preferred Nomenclature: (combined) 

4,7-Methano- lH-indene, 

1,2,3,4,5,6,7,8,8-nonachloro-2,3,3a,4,7,7ahexahydroEmpirical Formula: C toH5C lg 

REGULATORY STATUS 

Standards and Criteria: 

cis-nonachbr 

Cl Cl \, 

Cl c’ 

A I Cl 

Cl Cl 

I-c H 

Cl Cl 

Vans-nonachlor 

. EPA Water Quality Criteria (for human . EPA Drinking Water Health Advisories: 

consumption of fish): None established at present 

None established at present 

. EPA Ambient Water Quality Criteria . Food and Drug Administration Action 

(for protection of aquatic organisms): Level for Fish: 

None established at present None established at present 

. EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

. None for nonachlor. However, trans-nonachlor is a minor (7-10s) constituent of 

technical-grade chlordane, a chlorinated hydrocarbon pesticide (McEwen and Stephenson, 1979; Takamiya, 1987). CNordane has been banned for all uses except for 

subsurface termites (see profile of chlordane for additional information). 
SOURCES OF NONACHLOR 

Total Nonachlor Produced: 

l Nonachlor is not intentionally produced for any commercial purposes. 

Uses of Nonachlor: 

. As an impurity in technical chlordane, nonachlor is distributed in the environment when 

chlordane is used to control soil-inhabiting insects (e.g., termites). 

Other !3ources: 

l An impurity in the technical grade of the pesticide heptachlor (Nash and Harris, 1973). 

FATE IN ENVIRONMENT 

Partitionhe: 

l Based on its estimated physical/chemical properties, nonachlor is nonvolatile (H = 

2x 10.’ atm l m3/mol), is strongly sorbed to soil (& 

for bioaccumulation (BCF = 2.2~10~). 

w = 457,000), and has a high potential 

Persistence: 

. Data on the persistence of cis- and trans-nonachlor are sparse, although their structural 

similarity to cis- and trans-chlordane (one chlorine atom replaces one hydrogen atom) 

suggests that they would behave similarly. NonacNor present as an impurity in 

heptachlor was found in soil test plots 16 years after the application of 112 kg/ha and 

224 kg/ha of technical heptachlor at concentrations of 2.3 and 5.2 ppm, respectively. 

Plots of the same type soil treated with technical chlordane, which contains roughly 7% 

nonachlor, also showed traces of nonachlor (co.03 ppm) after 16 years (Nash and Harris, 

1973). Assuming nonachlor behaves like chlordane, hydrolysis is not expected to be an 

important process although sensitized photolysis may occur. Biodegradation is expected 

to be very slow, although it may be important for ultimate degradation (Callahan et al., 

1979). 

. The immediate metabolic product of trans-nonachlor is trans-chlordane (Tashiro and 

Matsumura, 1978). 
HEALTH EFFECTS 

Carcinogenic@ 

4 No data found for nonachlor. 

0 Chlordane is a probable human carcinogen because it causes liver tumors in mice and 

rats (see chlordane profile). 

Mutagenic Activity: 

l No data found. 

Reproductive Effects: 

l No data found. 

Other Toxicological Effects: 

l Trans-nonachlor is reported to induce drug-metabolizing enzymes in the liver. Whether 

this is potentially related to any adverse health effects is not known (Campbell et al., 

1983). 

l Chlordane causes nerve, liver, kidney, and lung damage (see profile for chlordane). 

Toxicological Effects Indices: 

l LC50: mosquito larvae = 3.5~10“ ppm (Tashiro and Matsumura, 1977). 

. No health effects indices are available for nonachlor. The indices for chlordane are: 

- Cancer Potency Factor (CPF): I.3 (mgkglday).’ (IRIS, 1989) 

Concentration in 

1 in 10,000 3 PLgk 

1 in 100,000 0.3 pg/L 

I in l,OOO,OOO 0.03 j.tgL 

- Reference Dose (RfD): 6~10~~ (mgikg/day) (IRIS, 1989) 

- TWA-TLV (time-weighted average, threshold limit value) for occupational skin exposure: 0.5 mg/m3 (ACGIH, 1986; IRIS, 1988). 

C-169 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Sotubility, S (mg/L): 

Vapor Pressure, P {mm Hg): 

444.2 

solid 

148 (talc.) 

471 (talc.) 

N/A 

N/A 

0.06 (cak.) 

2xlo-8 (talc.) 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Henry’s Law Constant, 

H @ 25°C (atm l m3/mol): 2x10-’ (talc.) Lyman et al., 1982 

Log (Gctanol-Water Partition 

Coefficient), log &w: 5.66 (cab) Lyman et al., 1982 

Soil Adsorption Coefficient, I& (mug): 7.3~10~ (talc.) Lyman et al., 1982 

Fish Bioconcentration Factor, BCF: 2.2x104 (talc.) Lyman et al., 1982 

c-170 
REFERENCES 

ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Occupational Exposures to Chemicals. ACGIH, Cincinnati, OH. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Halt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-4401479-029a. 

Campbell, M.A., J. Gyorkos, B. Lee, K. Homonko, and S. Safe. 1983. The Effects of 22 

Organohalogen Pesticides as Inducers of the Hepatic Drug-Metabolizing Enzymes. (Abstract). 

Gen. Pharmacol. 14(4): 445-454. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency. 

Washington, DC. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

McEwen, F.L., and G.R. Stephenson. 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, New York. 

Nash, R.G., and W.G. Harris. 1973. CNorinated Hydrocarbon Insecticide Residues in Crops and 

Soil. J. Environ. Quality 2:269-273. 

Taguchi, S., and T. Yakushiji. 1988. Influence of Termite Treatment in the Home on the Chlordane 

Concentration in Human Milk. Arch. Environ. Contam. Toxicol. 17:65-71. 

Takamiya, K. 1987. Residual Levels of Plasma Oxychlordane and trams-Nonachlor in Pest Control 

Operators and Some Characteristics of These Accumulations. Bull. Environ. Contam. Toxicol. 39: 

750-755. 

Tashiro, S., and F. Matsumura. 1977. Metabolic Routes of cis- and trans-CNordane in Rats. J. 

Agric. Food Chem. 25(4):872-880. 

Tashiro, S. and F. Matsumura. 1978. Metabolism of trans-Nonachlor and Related CNordane 

Components in Rat and Man. (Abstract). Arch. Environ. Contam. Toxicol. 7:113-127. 

c-171 
C-172 
OCTACHLOROSTYRENE 

CAS No.: 29082-74-4 

CAS Preferred Nomenclature: 

Benzene, pentachloro 

(t.richloroethenyl)- 

Empirical Formula: CgCh3 

Molecular Weight: 379.7 I 53 %I 1 

REGULATORY STATUS 

l No use restrictions or regulatory standards. 

SOURCES OF TACHLOROSTYRENE 

Formation of Octachlorostyrene: 

l There is no intentional commercial production of octachlorostyrene. Octachlorostyrene 

is associated with wastes from the electrolytic production of chlorine prior to 1970 when 

graphite anodes and coal tar pitch binder were used. It is hypothesized that the 

chlorination of this binder material was a major source of octachlorostyrene as well as 

other chlorinated styrenes (Kaminsky and Hites, 1984). After 1970, metal anodes were 

used. 

l It is reported that octachiorostyrene is also formed when graphite anodes are used during 

the electrolytic production of magnesium from magnesium chloride (Tarkpea et al., 

1985). 

FATE IN ENVIRONMENT 

Partitioning: 

. Based on estimated physical/chemical properties using structure-activity relationships 

‘Lr man et al, 1982), octachlorostyrene is highly volatile (estimated H = 0.15 atm l 

m /mol) and strongly sorbs to organic matter (Kowr 87,100,OOO). Ithas a high potential 

for bioaccumulation (BCF = 4.2x 106). 

c-173 
l Octachlorostyrene is persistent in sediments (Kaminsky and Hites, 1984). Processes 

that can transform octachlorostyrene include hydrolysis, biodegradation, and photolysis. 

but at low rates. The estimated half-lives cited were >l,OOO days for hydrolysis and 

~100 days for biodegradation (Wise and Wrich, 1984). Information was found showing 

that octachlorostyrene can undergo photolysis in water/solvent mixtures exposed to 

wavelengths between 230 and 290 mm. The rate was slower at wavelengths greater than 

290 mm. (Hustert et al, 1984). 

HEALTH EFFECTS 

Cardnogenidty: 

l The potential carcinogenicity of octachlorostyrene has not been evaluated. 

Mutagenic Activity: 

9 Results were negative in bacterial mutagenicity tests (Tarkpea et al., 1985; Kaminskyu 

and Hites, 1984). 

Effects on Humans and Aninmls: 

. No reports of adverse health effects in humans or animals. 

c-174 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Water Solubility, (mg/L): 

Henry’s Law Constant, H@2S°C 

(atm l m3/mol): 

Log (Octanol - Water Partition 

Coefficient), log bw: 

Soil Adsorption Coefficient, k(mL/g): 

Fish Bioconcentration Factor, BCF: 

379.7 

Solid 

2x10-4(calc) 

O.l5(calc) 

7.94 (cak) 

4.4x 106(calc) 

33,000(calc) 

Lyman, et al ., 1982 

Lyman, et al ., 1982 

Lyman, et al ., 1982 

Lyman, et al ., 1982 

Lyman, et al ., 1982 

c-175 
Hustert, K.. D. Kotzias, and F. Korte. 1984. Beitrag Zum Verhalten von Octochlorostyrol bei 

UV-Bestrahlung. Chemospher. 13:845-848. 

Kaminsky, R., and R.A. Hites. 1984. Octachlorostyrene in Lake Ontario; Sources and Fates. 

Environ. Sci. Technol. 18:275-279. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Tarkpea, M., 1. Hagen, GE. Carlberg, P. Kolsaker, and H. Stofflor. 1985. Mutagenicity, Acute 

Toxicity, and Bioaccumulation Potential for Six Chlorinated Sytrenes. Bull. Environ. Contam. 

Toxicol. 35:525-530. 

Wise, P.L., and M. Wrick. 1984. Candidates for the Emerging Chemical Identification and 

Management Project: Polychlorinated Systems Memorandum, September 4, 1984. 

C-176 
OXYCHLORDANE 

CAS No.: 27304- 13-8 

CAS Preferred Nomenclature: 

2,5-methano-2 H-indeno 

(1,2b)oxirene, 2,3,4,5,6,6a,7,7octachloro1 a, 1 b,5,5a,6,6 hexahydroEmpirical Formula: C lOH&laO 

Synonyms and Common Names: 

- Octachlor epoxide 

- Oxychlordan 

- 1,2-dichlorochlordene epoxide 

REGULATORY STATUS 

l No use restrictions or regulatory standards. 

SOURCES OF OXYCHLORDANE 

Uses of Oxychlordane: 

l Oxychlordane is not used in any commercial products and is not found in technical-grade 

c hlordane. 

Other Sources 

l Oxychlordane is a major metabolic breakdown product of the pesticide chlordane 

(Taguchi and Yakushuji, 1988). It is one of many compounds formed as a result of a 

series of oxidative enzyme reactions with chlordane (Bamett and Dorough, 1974; 

Tashiro and Matsumura, 1977). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, oxychlordane is estimated to have low 

volatility (H = 3~10’~ atm l m3/mol), a moderate tendency to sorb to soil (Kw aOO), 

and a low potential for bioaccumulation (BCF = 19). 

c-177 
Persistence: 

9 Based on its structural similarity to the pesticides chlordane, die&in, and aldrin, 

oxychlordane is not expected to be susceptible to hydrolysis, but is expected to be 

affected by indirect photolysis. Biodegradation is also expected to be slow (Callahan et 

al., 1979). It is likely to be highly persistent (Kirk-Othmer, 1978). 

l Four months after application of high-purity chlordane to alfalfa, oxychlordane comprised 16% of the residues measured in the crop (WHO, 1984). 

l Oxychlordane is considered to be more persistent than its parent compound, chlordane 

(WHO, 1984). 

OXYCHLORDANE OBSERVED IN THE ENVIRONMENT 

Sample Type Concentration Reference 

Market basket foods 

(found in less than 1% of samples 

taken in 1963- 1969) 

Human breast milk 

(1976 study of 1463 women) 

Human fat 

Fat of dogs, rats, pigs, cattle 

Tokyo Bay gobyfish 

Bats (Maryland and Virginia) 

l-5 we 

75.4- 116 pg/L 

0.03-0.4 mg/kg 

(Concentrations 

not given) 

3 Mm3 

0.1 l-to 6.33 pg 

WHO, 1984 

WHO, 1984 

WHO, 1984 

WHO, 1984 

Worth@, 1983 

WHO, 1984 

HEALTH EFFECTS 

Cardnogenidty: 

l It has been suggested that chlordane metabolites (e.g., oxychlordane) may be carcinogenic in humans because chlordane causes liver cancer in mice (WHO, 1984). EPA 

has not evaluated the carcinogenic potential of oxychlordane. 

Other Toxicological Effects: 

l Oxychlordane is considered to be more toxic than its parent compound, chlordane (see 

Chlordane profile) (WHO, 1984). 

C-178 
l No other information was found on the human health effects, mutagenicity, or reproductive effects of oxychlordane. 

Toxicological Effects Indices: 

l Acute oral LD5o: rat, 19.1 mgkg (Mastri et al.. 1969, in WHO, 1984). 

l Temporary reference dose proposed by the FAOIWHO for the sum of the alpha- and 

gamma- forms of chlordane plus oxychlordane: 0.0 to 0.001 mgkg (WHO, 1984). 

l A 1972 Joint Meeting on Pesticide Residues established food residue tolerance levels 

of 0.02 to 0.5 mgkg for a sum of alpha-, gamma-, and oxychlordane (WHO, 1984). 

C-l 79 
PHYSICAL CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility. S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant H @ 

25°C (atm l m3/mol): 

Log (Gctanol-Water Partition 

Coefficient), log &w: 

SoiI Adsorption Coefficient, K&mug): 

Fish Bioconcentration Factor, BCF: 

354.9 

solid 

134 (talc.) 

317 (talc.) 

N/A 

N/A 

200 (cab) 

IxlOA (talc.) 

3x 1 o-’ (talc.) 

2.60 (cab) 

300 (cab) 

19 (talc.) 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

C-180 
Barnett, J.R., and H.W. Dorough. 1974. Metabolism of Chlordane in Rats. J. Agric. Food Chem. 

22:612-619. 

Kirk-Othmer. 1978. Encyclopedia of Chemical Technology. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Lyman, W.L., W.F. Reehe, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation Methods - Environment. McGraw-Hill, New York. 

Mastri, C., M.L. Keplinger, and O.E. Fancher. Acute Oral Toxicity Study on Four Chlordenes in 

Albino Rats. 1969. Illinois, Industrial Bio-Test Laboratories (Report for Velsicol Chemical 

Corporation). (As cited in WHO, 1984) 

Taguchi, S., and T. Yakushiji. 1988. Influence of Termite Treatment in the Home on the Chlordane 

Concentration in Human Milk. Arch. Environ. Contam. Toxicol. 17:65-7 1. 

Tashiro, S., and F. Matsumura. 1977. Metabolic Routes of cis- and trans- Chlordane in Rats. J. 

Agric. Food Chem., 25:872-880. 

WHO (World Health Organization). 1984. Chlordane. Environmental Health Criteria 34. World 

Health Organization, Geneva. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. British Crop Protection 

Council, Craydon, England. 

C-181 
C-182 
PENTACHLOROANISOLE 

CAS No.: 1825-21-4 

CAS Preferred Nomenclature: 

Benzene, PentachloromethoxyEmpirical Formula: C7H3C150 

Synonyms and Common Names: 

- PCA 

- 2,3,4,5,6 Pentachloroanisole 

- Pentachlorophenyl methyl ether 

- Methyl pentachlorophenate 

REGULATORY STATUS 

Standards and Criteria: 

l No standards or criteria for pentachloroanisole were found. See Pentachlorophenol 

profile for standards applicable to parent compound. 

Use Restrictions and Bans: 

l Uses of pentachlorophenol were restricted in 1984 primarily to wood preservation, 

excluding logs for homes and interiors of buildings. (See Pentachlorophenol profile.) 

SOURCES OF PENTACHLOROANISOLE 

Production: 

l Not produced as a separate chemical. 

Other Sources: 

l Pentachloroanisole is a metabolic product of pentacblorophenol. It can be formed by 

microorganisms in the soil environment (Kaufman, 1978; Cserjesi and Johnson, 1972) 

and in aquatic sediments (Pierce and Victor, 1978). 

C-183 
FATE IN ENVIRONMENT 

Partitiouinpr: 

l Based on its physical/chemical properties, pentachloroanisole is volatile (H = 8x10-’ 

atm l m3/mo1), strongly sorbs to organic matter (Kow = 457,000). and has a high potential 

for bioaccumulation (BCF = 10,000). It is also retained longer by fish than pentachlorophenol (tl/2 = 6 to 24 days for pentachloroanisole versus a tl/2 = 0.25 to 1 day 

for pentachiorophenol, Lech et al., 1978). 

Persistence: 

l Environmental fate data for pentachloroanisole are scarce. Rate constants for 

hydrolysis, photolysis. or acid-base dissociation were not found. Based on its chemical 

structure, it would not be expected to hydrolyze (Lyman et al., 1982) but may undergo 

photolysis (Sadtler, 1979). Conversion back to pentachlorophenol in soils can occur 

under both aerobic and anaerobic conditions, but is faster under anaerobic conditions 

(42% in 24 days vs. 6% under aerobic conditions, Kaufman, 1978). 

PENTACHLOROANISOLE OBSERVED IN THE ENVIRONMENT 

l In lake contaminated with fuel oil containing pentachlorophenol in Mississippi (Pierce 

and Victor, 1978): 

Water cm@) 0.03- 1.94 

Sediment (mglg) M-80 

Fii Tissue (rig/g wet weight) 30-250 

HEALTH EFFECTS 

Carcinogenicity: 

l No data found. EPA has not evaluated the carcinogenic potential for pentachloroanisole. 

The data for pentachlorophenol carcinogenicity are currently under review (IRIS, 1989). 

vitv; No data found. 

Reproductive Ef’fects: 

l Female rats fed pentachloroanisole at a dose of 41 mg/kg/day gained less weight during 

pregnancy. Male offspring had lower birth weights and were smaller in length. Female 

offspring exhibited no such effects. (Welsh et al., 1987.) 

C-184 
Toxicolo&al Effects Indices: 

. Oral LDw: rats 500 mgkg (Sax, 1984). 

C-185 
Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&r: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H @ 

25°C (atm l m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log Kow: 

Soil Adsorption Coefficient, I&&ml/g): 

Fish Bioconcentration Factor, BCF: 

280.4 

solid 

104 (talc.) 

258 (talc.) 

N/A 

N/A 

0.2 (talc.) 

5x 1o’3 (talc.) 

8x 1o’3 (talc.) 

5.66 (cab) 

4.2~10~ (talc.) 

1 .ox104 (talc.) 

Reference 

Windholz. 1983 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Callahan et al., 

1982 

Lyman et al., 1982 

Lyman et al., 1982 

C-186 
Callahan, M.A., M.W. Slim& N.W. Gabel. I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfke, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029a. 

Csejesi, A.J., and E.L. Johnson. 1972. Methylation of Pentachlorophenol by Trichoderma ti 

gatum. Can. J. Microbial. 18:45-49. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, Washington, DC. 

Kaufman, D.D. 1978. Degradation of Pentachlorophenol in Soil, and by Soil Microorganisms. In: 

Pentachlorophenol Chemistry, Pharmacology, and Environmental Toxicology (K.R. Rao, ed.), pp. 

27-39. Plenum Press, New York. 

Lech. J.J., A.H. Glickman, and C.N. Statham. 1978. Studies on the Uptake, Disposition and 

Metabolism of Pentachlorophenol and Pentachloroanisole in Rainbow Trout (Salmo, pp. 

107-l 13. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Pierce, R.H., Jr., and D.M. Victor. 1978. Fate of Pentachlorophenol in an Aquatic Ecosystem. In: 

Pentachlorophenol Chemistry, Pharmacology, and Environmental Toxicology (K-R. Rao, ed.), pp. 

27-39. Plenum Press, New York. 

Sadtler Research Labs. 1979. Sadtlers Handbook of Ultraviolet Spectra. Sadtler Research Labs, 

Division of Bio-Rad Labs, Inc., Philadelphia. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold 

Co., New York. 

Welsh, J.J., T.F. Collins, T.N. Black, S.L. Graham, and M.W. O’Donnell, Jr. 1987. Teratogenic 

Potential of Purified Pentachlorophenol and Pentachloroanisole in Subchronically Exposed 

Sprague-Dawley Rats. Food Chem. Toxicol. 25(2): 163- 172. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

C-187 
C-188 
PENTACHLOROBENZENE 

CAS No.: 608-93-5 

CAS Preferred Nomenclature: 

Benzene, pentachloroEmpirical Formula: C&C 15 

Cl 

v 

C 

Cl 

Cl Cl 

Cl 

C6H Cl5 

Synonyms and Common Names: 

- QCB 

- 1,2,3,4,5 Pentachlorobenzene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Standard Maxiconsumption of fish) (IRIS, 1989): mum Contaminant Level: 

35 P&v-L None established at present 

l EPA Ambient Water Quality Criteria l EPA Drinking Water Health Advisories: 

(for protection of aquatic organisms) None established at present 

(IRIS, 1989): 

Freshwater Saltwater 

Acute, l.tg/L 250 160 

Chronic, pg/L 50 129 

Above are LECs (Lowest Effect Concentration) 

l Food and Drug Administration Action 

Level for Fish: 

None established at present 

Use -and None found. 

SOURCES OF PENTACHLOROBENZENE 

Produa: No data found. 

m: No data found. 

C-189 
Other Sources: 

9 Pentachlorobenzene is an impurity (approximately 0.17%) in the soil fungicide pentachloronitrobenzene (Verschueren, 1983; Klaassen et al., 1986). 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, pentachlorobenezene is highly volatile (H = 

3.8~10~~ atm l m3/mo1), is strongly sorbed to soil (KOW z 155,000). and has a high 

potential for bioaccumulation. Experimentally determined values for BCF ranged from 

1.3~10~ to 2x10’ (Oliver and Niimi. 1983). 

l The steady-state bioconcentration factor found for bluegills was 3,400 (CIS database). 

Persistence: 

l Little information specific to pentachlorobenzene was found in the literature. Much of 

its behavior is inferred from that of hexa- and tetrachlorobenzenes. Neither hydrolysis 

nor chemical oxidation of pentachlorobenzene is expected to be environmentally significant based on the behavior of these related compounds. Although chlorobenzenes 

of 3 or fewerchlotinescan be biodegraded, hexa- and pentachlorobenzene are considered 

resistant to biodegradation (Bailey, 1983). 

+ Pentachlorobenzene has been found to undergo photolytic degradation in 

acetonittile/water mixtures at wavelengths >285 nm (Choudhry and Hutzinger, 1984). 

After 24 hours, 41.2% of an initial pentachlorobenzene concentration of approximately 

1mM underwent nonsensitized degradation while 53.8% disappeared in 4 hours when 

acetone at 0.55 M was present as a sensitizer. Roughly 3.4% of the pentachlorobenzene 

that underwent sensitized photolysis was converted to PCBs; lesser amounts were 

converted by direct photolysis. 

PENTACHLOROBENZENE OBSERVED IN THE ENVIRONMENT 

l No data available. 

C-190 
Carcinogenidty: 

l Not yet evaluated by EPA for carcinogenicity (IRIS, 1989). 

l EPA (1980) reports one study that alludes to carcinogenicity of pentachlorobenzene in 

mice but not in rats and dogs. No details are available. 

w: No data available. 

Reproductive Effects: 

l Weanling rat pups of mothers receiving 18 mg/kg/day developed tremors (IRIS, 1989). 

l Pregnant rats given 50,100, or 200 mg/kg orally during days 6- 15 of gestation produced 

sternal defects suggestive of retarded development (U.S. EPA, 1980). 

Other Toxkological Effects: 

l Liver and kidney toxicity observed in rats fed pentachlorobenzene at doses as low as 8.3 

mg/kg/day (IRIS, 1989). 

Toxicological Effects Indices: 

l Reference Dose (RfD): 8~10~ mg/kg/day @US, 1989). 

c-191 
PHYSICAL/CHEMICAL PROPERTIES 

Value 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, HO 25OC 

(atm l m3/mo1): 

Log (Gctanol-Water Partition 

Coefficient), log &w: 

Soil Adsorption Coefficient, 

GC (mU$ 

Fish Bioconcentration 

Factor, BCF: 

250.3 

solid 

86 

277 

1.8342 (16.5’) 

N/A 

0.24(22’) 

2.8~10-~(25~) 

(talc . ) 

3.8~10’~ (talc.) 

5.19 

5.8~10~ (talc.) 

1.3x105-2.0~10~ 

(expfl.) 

2125 

Reference 

Windholz, 1983 

Weast, 1986 

Weast, 1986 

Weast, 1986 

Verschueren. 1983 

Lyman et al., 1982 

Lyman et al., 1982 

U.S. EPA. 1986 

Lyman et al., 1982 

Oliver & Niimi, 

1983 

U.S.EPA, 1986 

C-192 
Bailey, R.E. 1983. Comment on Chlorobenzenes in Sediments, Water, and Selected Fish from 

Lakes Superior, Huron, Erie, and Ontario. Environ. Sci. Technol. 17:504. 

Choudhry, G.G., and 0. Hutzinger, 1984. Acetone-sensitized and Non-sensitized Photolysis of 

Tetra- Penta- and Hexachlorobenzenes in Acetonitrile-water Mixtures: Photoisomerization and 

Formation of Several Products including Polychlorinated Biphenyls. Environ. Sci. Technol. 

18:235-241. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Klaassen, C.D., M.D. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology. The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

Oliver, B.G., and A.J. Niimi. 1983. Bioconcentration of Chlorobenzenes from Water by Rainbow 

Trout: Correlations with Partition Coefficients and Environmental Residues. Environ. Sci. Technol. 17:287-291. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

U.S. EPA. 1980. Ambient Water Quality Criteria for ChIorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA-440/5-80-028. 

U.S. EPA. 1986. Superfund Public HeaIth Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Emergency and Remedial Response, Washington, DC. EPA-540/l-86/060. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Weast, R.C., ed. 1986. CRC Handbook of Chemistry and Physics. 67th ed. CRC Press, Boca 

Raton, FL. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A world compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-193 

PENTACHLORONITROBENZENE 

CAS No.: 82-68-8 

CAS Preferred Nomenclature: 

Benzene, pentachloronitroEmpirical Formula: C&lsN@ 

Synonyms and Common Names: 

- Brassicol - Terraclo 

- Quintozene -PcNB 

- Fungiclor - Folosan 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories: 

consumption of fsh): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l EPA Tolerance Levels (40 CFR 

(for protection of aquatic organisms): 180.291): 

No specific criteria or LELs have been 0.1 ppm for cottonseed 

developed for PCNB (IRIS, 1989) 0.2 ppm for collards, kale, and 

mustard greens 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

* Food and Drug Administration Action 

Levels for Fish: 

None established at present 

l Use of pentachloronitrobenzene itself has not been restricted; however, the allowable 

level of the contaminant hexachlorobenzene has been set at 0.1 percent (U.S. EPA, 

19868). 

c-195 
SOURCES OF PENTACHLORONITROBENZENE 

Total Pentachloronitrobenzene Produced: 

l In 197 1. approximately 3 million pounds were produced by Olin Co. (Ouellette and 

King, 1977). 

Uses of Pentachloronitrotnmzene: 

l Pentachloronitrobenzene has been used primarily as a soil fungicide and as a seed 

dressing agent (e.g., peanuts). Other uses have been to control stem and root rot for 

flowers and vegetables (e.g., cabbage), and molds on flowers, cotton, and turf (Farm 

Chemicals Handbook, 1985). 

Other: None found. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its hysical/chemical properties, pentachloronitrobenzene is somewhat volatile 

(H = 1 x 10 -s atm l m3/moi). is strongly sorbed to soil organic matter (GW = 282,000) 

and has a low potential for bioaccumulation (BCF values derived experimentally range 

from 6.3 to 79) (Verschueren, 1983). 

Persistence: 

l Pentachloronitrobenzene can undergo hydrolysis (Kh = 2.8 x lO-5/hr) (Eltington, et al., 

1986) and aqueous photoreduction (A.D. Little, 1974). The estimated half-life is 2.8 

years at a pH of 7, so hydrolysis is unlikely to be environmentally significant in most 

cases. Biotransformation in soils can also occur, particularly under anaerobic conditions 

(Verschueren, 1983). 

PENTACHLORONITROBENZENE OBSERVED IN THE ENVIRONMENT 

l No data found. 

C-196 
HEALTH EFFECTS 

CarcinogenMy: 

l Dietary exposure of mice to pentachloronitrobenzeene (1206 ppm for 18 months) induced 

liver tumors (IARC, 1973). Similar studies in rats (2500 ppm for 25 months) showed 

no increased incidence of tumors (IARC, 1973). Pentachloronitrobenzene is classified 

as category 3 by IARC and Class C by EPA, indicating that there is limited evidence of 

carcinogenicity in animals and that additional studies are needed to characterize the 

effect of this chemical (IARC, 1973; PHRED, 1988). 

WC Activity: No data found. 

ReproductiveEffects: 

l Cleft palates were observed in the offspring of mice exposed orally to 500 mgkg of 

pentachloronitrobenzene (Courtney, 1983; Klaassen et al., 1986). 

l No effects were observed in rats given 1653 ppm pentachloronitrobenzene (Jordan and 

Borzelleca, 1973). 

Other Toxicological Effects: 

l Dogs fed pentachloronitrobenzene for 2 years at levels between 180 ppm and 1080 ppm 

developed various levels of liver damage, abnormal bile production, and secondary 

kidney degeneration (RTECS, 1984; IRIS, 1989). 

Toxicological Effects Indices: 

l Reference Dose (RfD): 3 x 10m3 mg/kg/day (IRIS, 1989). 

l Oral LD50: rats, 1200-1650 mg/kg (Klassen et al., 1986). 

c-197 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

295.34 

solid 

146 

328 (with slight 

decomp.) 

1.718 

N/A 

4.4 x 10-l 

7.11 x 1o’2 

Vapor Pressure, P (mm Hg): 1.13 x lo+ (25OC) 

Henry’s Law Constant, H @ 

25°C (atm l m3/mol): 1.0 x lo-4 

Hydrolysis, KN l/hr: 2.8 x lO-5 

Log (Octanol-Water Partition 

Coefficient), log bw: 5.45 

Soil Adsorption Coefficient, I& (mL/g): 1.4x lo4 

Fish Bioconcentration 6.3 to 79 

Factor, BCF: @xpW 

Verschueren, 1983 

Verschueren, 1983 

Windholz, 1983 

Windholz, 1983 

Hartley & Kidd, 1983 

U.S. EPA, 1986; 

Jaber et al., 1984 

Jaber et al., 1984 

Lyman et al., 1982 

Ellington et al., 1986 

Jaber et al., 1984 

Lyman et al., 1982 

Verschueren, 1983 

C-298 
Courtney, D. 1973. The Effect of Pentachloronitrobenzene on Fetal Kidneys. Toxicol. Appl. 

Phatmacol. 25:455. 

Ellington, J.J., F.E. Stancil, Jr., and W.D. Payne. 1986. Measurement of Hydrolysis Rate Constants 

for Evaluation of Hazardous Waste Land Disposal. Vol. I. U.S. Environmental Protection Agency, 

Athens. GA. EPA/600/3-861043. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Hartley, D., and H. Kidd, eds. 1983. The Agrochemicals Handbook. The Royal Society of 

Chemistry, Nottingham, England. 

IARC (International Agency for Research on Cancer). 1973. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 5. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information System. U.S. EPA, Washington, DC. 

Jager, K.W. 1970. AIdrin, Dieldrin, Endrin and Telodrin: An Epidemiological and Toxicological 

Study of Long-Term Occupational Exposure. Elsevier Publ. Co., Amsterdam, The Netherlands. 

Jordon, R.J., and J.F. Borzelleca. 1973. Teratogenic Studies with Pentachloronitrobenzene in Rats. 

Toxicol. Appl. Pharmacol. 25:454. 

Klaassen, C.D., M.O. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology. The Basic 

Science of Poisons. Macmillan Publishing Co., New York. 

Ouellette, R.P.. and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co., New York. 

PHRED. 1988. Public Health Risk Evaluation Database. Draft 204. February 18, 1988. Phase 

Linear Systems, Inc. for U.S. Environmental Protection Agency, Office of Emergency and Remedial 

Response. 

Registry of Toxic Effects of Chemical Substances (RTECS) Database. 1984. Available through 

the National Library of Medicine’s MEDLARS system, National Institute of Occupational Safety 

and Health (NIOSH). 

U.S. EPA. 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Washington, D.C. Report #PB81- 

117-392. 

U.S. EPA. 1985. Suspended, Cancelled, and Restricted Pesticides. U.S. Environmental Protection 

Agency, Office of Pesticides and Toxic Substances, Washington, DC. 

c-199 
U.S. EPA. 1986a. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

U.S. EPA. 1986b. Superfund Public Health Evaluation Manual, U.S. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA-540/l-86/060. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

c-200 
PENTACHLOROPHENOL 

CAS No.: 87-86-5 

CAS Preferred Nomenclature: Phenol, pentachloroEmpirical Formula: C&K150 

Synonyms and Common Names: 

- PCP - Penta 

- Permatox - Chlorophen 

- Penchlorol - Pet-mite 

- Fungilen - Dowicide 7 

- Prevent01 P - Liroprem 

- Permacide - Priltox 

- Chem-To1 - Durotox 

- Santobrite - Lauxtol 

- Penwar - SantophenR 

- Termi-Trol - Weedone 

REGULATORY STATUS 

Standards and Criteria: 

OH 

a B3: 0 

a 

a 

6 

C,HCI,O 

l EPA Water Quality Criteria (IRIS, l EPA Drinking Water Health Advisories 

1989): (52 FR 175; IRIS, 1989): 

for human consumption of fish and &i&( 10 kg): 

water = 1.01 mg/L to control undesirabIe l-day exposure = 1.0 mg/L 

taste and odor = 30 ug/L lo-day and long-term exposure = 

0.3 mg/L 

adult(70 kg): 

long-term exposure = 1.05 mg/L 

lifetime exposure = 0.22 mg/L 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic or- Level for Fish: 

ganisms)(IRIS, 1989): None established at present 

Freshwater Saltwater 

Chronic, j.tg/L 22 13 

Acute, jtg/L 13 7.9 

c-201 
l EPA Drinking Water Standards 

(IRIS, 1989): 

Proposed Maximum Contaminant 

Level = 0.22 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0.22 mg/L 

Use Restrictions and Bans: 

l In 1984, most uses as an herbicide, antimicrobial agent (e.g., in cooling towers), 

defoliant, disinfectant, and in marine anti-fouling paint were discontinued (49 FR 

48367). 

l Continued uses allowed: wood preservative if not on logs for homes or interior of 

buildings, in oil field flood waters, and in pulp and paper mill solutions (49 FR 48367). 

SOURCES OF PENTACHLOROPHENOL 

Total Pentachlorophenol Produced: 

+ Pentachlorophenol (PCP) was developed as a wood preservative in 1936. 

+ Four million pounds were produced in 1971 (Oueliette and King, 1977). By 1974 

production had increased to 54 million pounds, of which 44 million pounds were used 

in wood preservation. In 1984, uses were curtailed. By 1986 only one company, Vulcan 

Materials, was producing pentachlorophenol (SRI, 1986). 

l In aquatic systems a major metabolic product of pentachlorophenol is pentachloroanisole 

(C7H3ClsO). 

Uses of Pentachlorophenol: 

l Major use (90%) is as a wood preservative to control termites and fungal rot for utility 

poles, fence posts, railroad ties, and exterior lumber (Klaassen et al., 1986). 

l Other uses (9%) include production of sodium pentacNorophenate (Na-PCP). This was 

used in marine anti-fouling paint; in cooling tower water to control microorganism 

growth; and to prevent fungal rot in carpets, canvas, and other textiles (Cirelli, 1978). 

l PCP has also been used as a microbial agent in oil field flooding waters and drilling 

muds and in the paper and pulp industry (Cirelli, 1978). 

l PCP and Na-PCP together were formerly the second most used pesticide in the U.S. 

(Cirelli, 1978), for example, as a pre-harvest defoliant for cotton and pre-emergence 

herbicide (Agrochemicals Handbook, 1978). 

c-202 
Other Sources: 

l PCP is a breakdown product of the biotransformation of hexachlorobenzene and 

pentachlorobenzene (Koss and Koransky, 1978). 

FATE IN ENVIRONMENT 

Partitioninfx: 

l Based on its physical/chemical properties, pentachlorophenol can volatilize (H = 

2.75~10~~ atm l m3/mol), although this is not a dominant fate process. For example, 

Kv in a shallow stream is calculated to be O.O24/day, compared to the photolysis rate of 

l.l/day (Mills et al., 1985). PCP sorbs strongly to soil organic matter (KOW = 132,000) 

and can bioaccumulate (BCF ~1,000). 

Persistence: 

l PCP exists predominantly (over 90%) as an anion in waters having a pH of 5.7 or higher 

(pKa = 4.7). Hydrolysis and volatilization are thus not generally environmentally 

significant. Photolysis is rapid (Kpo = 1.224Ih.r), with half-lives of 0.2 and 4.8 hours at 

depths of 10 cm and 300 cm, respectively, in a clear body of water at the latitude of 

Cleveland on a midsummer day (Callahan et al., 1979). 

l PCP can be degraded by a variety of microorganisms; one PCP-degrading strain 

) was found to degrade PCP in natural waters at initial concentrations 

of 10 ppb to 100 ppb, usually within 48 hours (Alexander and Aleem, 196 1). First-order 

biotransformation rate constants in water range from 0.05 to O.S/day (Mills et al., 1985). 

However, pentachlorophenol in soils degrades more slowly. In four laboratory experiments, 14, ranged from 4.2 x lOA to 5.2 x lO?day (Tabak et al., 1981; Baker and 

Mayfield, 1980). 

HEALTH EFFECTS 

Carcinogenic&y: 

l There was no evidence of the carcinogenicity of pure PCP in mice and rats fed doses of 

up Co 30 mg/kg/day for 2 years (U.S. EPA, 1984). However, technical-grade PCP may 

be carcinogenic because of its contamination with the highly carcinogenic dioxins and 

furans (IRIS, 1989). 

l EPA has assigned pentachlorophenol to Group D; not classif=d as to human carcinogenicity. The research data are currently under review (IRIS, 1989). 

C-203 
Mutagenic Activity: 

l Tests have yielded conflicting results. There were no observed mutagenic effects in 

Drosoohila (fruit flies) (IARC, 1979) or m bacteria (Ames test). 

Some mutations were observed in mice and m (yeast) (Scow 

et al., 1980). 

Reproductive Effects: 

l PCP has caused fetal posioning in rats (Scow et al., 1980). The basic response was 

reproductive failure with those surviving having subcutaneous fluid retention and 

swelling, kidney damage, and skeletal defects of the skull, ribs, and vertebrae. The 

incidence increased at higher doses (IARC, 1979). 

Other Toxicological Effects: 

l Acute (short-term, high-dose) and chronic (long-term, low-dose) effects both can include 

(U.S. EPA, 1984): 

- skin irritation - fever 

- profuse sweating - uchycardia (rapid hearbeat) 

- kidney damage - visioadamage 

- labored breathing - weakness 

- heart failure - convulsions. 

l Chronic human exposure to PCP has been associated with aplastic anemia (Roberts, 

198 1). Exposure to PCP aggravates pre-existing kidney and liver diseases (Clayton and 

Clayton, 1982). 

l Fatalities due to PCP exposure have occurred (Klaassen et al., 1986). 

Toxicologicd Effects Indfces: 

l Reference Dose (RfD): 0.03 mg/kg/day (IRIS, 1989). 

l TWA-TLV (Time-weighted average, threshold limit value) for occupational skin exposure: 0.5 mg/m3 (ACGM, 1986). 

l For a 70-kg (150-lb) person, a lethal oral dose is 50-500 mg/kg (IRIS, 1989). 

c-204 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H @ 25OC 

(atm l m3/mo1): 

Hydrolysis: Ka, Umole/hr; 

Ku. l/hr; &, Umo1eIh.r: 

Log (Octanol-Water Partition 

Coefficient), log Kow: 

Soil Adsorption Coefficient, Koc (mug): 

Fish Bioconcentration Factor, BCF: 

266.3 

solid 

190-191 

309-310 

1.978 (22/4OC) 

4.74 

14 (20”) 

1.1 x lOA 

(20°) 

2.75 x 1O’6 

4.6 x 1Oa 

2.4 x lo4 

0.138 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Windholz, 1983 

Callahan et al., 1979 

Callahan et al., 1979 

Callahan et al., 1979 

Mabey et al., 1982 

Park et al., 1980 

Leo, 1982 

5.12 

5.3 x lo4 

770 (talc.) 

900 - 1,000 

Mabey et al., 1982 

Lyman et al., 1982 

Callahan et al., 1979 

c-205 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Environment. ACGIH, Cincinnati, OH. 

Agrochemicals Handbook. 1982. Meister Publishing Co., Willoughby, OH. 

Alexander, M., and M.H. Aleem. 196 1. Effect of Chemical Structure on Microbial Decomposition 

of Aromatic Herbicides. J. Agric. Food Chem. 9( 1): 44-47. 

Baker, M.D., and C.I. Mayfield. 1980. Microbial and Nonbiological Decomposition of 

Chlorophenols and Phenols in Soil, Water, Air. Soil Pollution 13:411. 

Buhler, D.R., M.E. Rasmussen, and H.S. Nakave, 1973. Occurrence of Hexachlorophene and 

Pentachlorophenol in Sewage and Water. Environ. Sci. Technol. 7:929-934. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, LP. May, CF. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. II. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029b. 

CirelIi, D.P. 1978. Patterns of Pentachlorophenol Usage in the United States of America - An 

Overview. In Pentachlorophenol: Chemistry, Pharmacology, and Environmental Toxicology, ed. 

K.R. Rao. Plenum Press, New York. 

IARC (International Agency for Research on Cancer). 1979. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans, Vol. 20. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd. ed. John Wiley and Sons, Inc., 

New York. 

Klaassen, C.D., M.O. Amdur, and J. Doulh, eds. 1986. Casarett and Doull’s Toxicology. The 

Science of Poisons. Macmillan Publishing Co., New York. 

Koss, G., and W. Komasky. 1978. Pentachlorophenol in Different Species of Vertebrates after 

Administration of Hexachlorobenzene and Pentachlorobenzene. In Pentachlorophenol: Chemistry, 

Pharamacology, and Environmental Toxicology, ed. RR. Rae. Plenum Press, New York. 

Leo, A.J. 1983. Log P Parameter Database. Medchem Project, Pomona College, Claremont, CA. 

Lyman, W.J., W.F. Reehe, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods-Environment. McGraw-Hill, New York. 

c-206 
Mabey, W.R., J.H. Smith. R.T. Podoll, H.L. Johnson, T. Mill, T.W. Chou, J. Gates, I.W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440/4-81-014. 

Mills, W.B., D.B. Porcella, M.J. Ungs, S.A. Gherini, K.V. Summers, L. Mok, G.L. Rupp, G.L. 

Bowie, and D.A. Haith. 1985. Water Quality Assessment: A Screening Procedure for Toxic and 

Conventional Pollutants in Surface and Ground Water. U.S. Environmental Protection Agency, 

Athens, GA. EPA 600/6-85/002a. 

Ouellette, R.P., and J.A. King. 1977. Chemical Week Pesticides Register. McGraw-Hill Book Co., 

New York. 

Park, R.A., C.I. Connolly, J.R. Albanese, L.S. Clesceri, S.W. Heitzman, H.H. Herbrandson, B.H. 

Indyke, J.R. Loehe, S. Ross, D.D. Sharma. and W.W. Shuster. 1980. Modeling Transport and 

Behavior of Pesticides and Other Toxic Organic Materials in Aquatic Environments (PEST). Report 

No. 7. Center for Ecological Modeling, Renselaer Polytechnic Institute, Troy, NY. 

Roberts, H.J. 1981. Aplastic Anemia due to Pentachlorophenol. The New England Journal of 

Medicine 305(27):1650-1651. 

Scow, K., M. Goyer, J. Perwak, E. Payne, R. Thomas, D. Wallace, P. Walker, M. Wood, and L. 

Delpire. 1980. An Exposure and Risk Assessment for Pentachlorophenol. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Office of Water and Waste 

Management, Washington, DC. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Tabak, H.H., S.A. Quave, C.I. Mashni, and E.F. Barth. 198 1. Biodegradation Studies with Organic 

Priority Pollutant Compounds. J. Water Pollution Control Fed. 55: 1503- 15 18. 

U.S. EPA. 1976. Summary of Reported Episodes involving Pentachlorophenol. Pesticide Episode 

Review System. U.S. EPA, Office of Pesticide Programs, Pesticide Episode Response Branch, 

Operations Division, Washington, DC. 

U.S. EPA. 1980a. Ambient Water Quality Criteria for Pentachlorophenol. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Washington, DC. PBSl-117764. 

U.S. EPA. 1980b. An Exposure and Risk Assessment for Pentachlorophenol. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Washington, DC. EPA-440/4-8 l021. 

U.S. EPA. 1984. Health Effects Assessment for Pentachlorophenol. U.S. Environmental Protection Agency, Washington, DC. EPA/540/i-86-043. 

C-207 
U.S. EPA. 1986. Super-fund Public Health Evaluation Manual. U.S. Environmental Protection 

Agency, Office of Solid Waste and Emergency Response, Washington, DC. EPA 540/l- 86/060. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York. 

Windholz, M.. ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

Wong, A.S., and D.E. Cosby. 1978. Photolysis of Pentachlorophenol in Water. In Pentachlorophenol: Chemistry, Pharmacology, and Environmental Toxicology, ed. K.R. Rao, pp. 

19-25. Plenum Press, New York. 

Worthing, C.R., ed. 1979. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon. England. 

Zitko, V., 0. Hutzinger, and P.M.K. Chou. 1974. Determination of Pentachlorphenol and 

Chlorobiphenylols in Biological Samples. Bull. Environ. Contam. Toxicol. 12(6):649-653. 

C-208 
PERTHANE 

CAS No.: 72-56-O 

CAS Preferred Nomenclature: 

Benzene, I.1 -(2,2-dichloroethylidene) 

bis (4ethyl)- 

Empirical Formula: C 18H2612 

Synonyms and Common Names: 

- Ethylan 

- l ,l-Dichloro-2,2-bis(p-ethylphenyl)R 

- ethane 

REGULATORY STATUS 

m!f-J ; C}% 

cl-c-cl 

n 

%"20C'2 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories: 

consumption of fish): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l EPA Tolerance Levels for raw agricul- 

(for protection of aquatic organisms): tural commodities (40 CFR 180.139): 

None established at present in meat and milk = 0 ppm 

in other commodities = 15 ppm 

l EPA Drinking Water Standard Maxi- * Food and Drug Administration Action 

mum Contaminant Level: Levei for Fish: 

None established at present None established at present 

Use Restriction and Bans: 

l In 1980, all registered uses were cancelled (45 FR 41694). 

SOURCES OF PERTHANE 

Total Perthane Produced: 

l Perthane was produced by Rohm and Haas, Inc. from 1950 until it was discontinued in 

1980 (Farm Chemicals Handbook, 1985). 

c-209 
Uses of Perthane: 

l Prior to 1980, perthane was used in a minor capacity as an insecticide on a variety of 

crops and in certain household settings. Its structural similarity to DDT made it 

particularly effective in controlling pests on pears, and leafhoppers and larvae on various 

vegetables (i.e., peppers, tomatoes, broccoli, brussel sprouts, cauliflower, kohlrabi, 

lettuce, spinach, and potatoes) (Ouellette and King, 1977; McEwen and Stephenson, 

1979; Hayes, 1982; U.S. EPA, 1986). 

l Perthane was registered as an insecticide for use on the foliage of grapes, apples, and 

cherries. 

l In homes and dog kennels, pert&me was used in controlling animal pests (U.S. EPA, 

1986). 

l Perthane has also been used in mothproofing blankets, upholstery, and other textile 

products (Hayes, 1982; U.S. EPA, 1986). 

Other: None identified. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its estimated physical/chemical properties, perthane is moderately volatile (H 

= 6.1~10~~ atm l m3/mol, is very strongly sorbed to soil (I& ~13,800,000), and has a 

high potential for bioaccumulation (BCF = 6.6~10~). 

Persistence: 

l Although perthane is structurally similar to DDT, it is not as persistent and can undergo 

both biodegradation and photolysis (Ware, 1975; McEwen and Stephenson, 1979; TDB, 

19851. 

HEALTH EFFECTS 

Carcinogenkity: 

l In one study with mice, females, but not males, developed liver tumors as a result of 2 

years of exposure to perthane in their diet (3000 ppm) (Reuber, 1980). 

l EPA has not yet classified perthane as to its potential carcinogenicity. 

B: No data found. 

m: No data found. 

c-210 
Other Todcologkal Effects: 

l There is no information available on any adverse human health effects caused by acute 

(short-term, high-dose) exposure to perthane. In a few experimental cases, perthane was 

used as a therapeutic agent in the treatment of prostate and breast cancers. Several of 

the exposed persons developed diarrhea, vomiting, and nausea. There was no evidence 

of liver, kidney, or nerve damage. However, there were no demonstrable benefits from 

the treatments (Hayes, 1982). 

l Rats fed perthane for 2 years at doses between 500 and 5,000 ppm demonstrated no 

adverse health effects. There were some minor liver changes (Hayes, 1982). 

l Perthane was lethal to dogs that received doses of 5,000 ppm for 22 weeks. Lower levels 

either had no effects (100 ppm) or caused some adrenal degeneration (1,000 ppm) 

(Hayes, 1982). 

Toxicologkal Effects Indices: 

l Oral LDso: rats, 6600 to 8170 mg/kg; mice, 9340 mg/kg (McEwen and Stephenson, 

1979; Hayes, 1982; RTECS, 1984). 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constanf p&: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25OC (atm l m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log hw: 

Soil Adsorption Coefficient, I& (mL/g): 

Fish Bioconcentration Factor, BCF: 

307.3 

Crystalline 

solid; technical 

grade, waxy solid 

56-57 

N/A 

N/A 

N/A 

0.1 

1 .5x1o-5 (talc.) 

6.1x10-’ (talc.) 

7.14 (talc.) 

1.1x106 (talc.) 

6.6x 1 o5 (talc.) 

Hayes, 1982 

Hayes, 1982 

Windholz, 1983 

Hollifield, 1979 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

Lyman et al., 1982 

c-212 
Farm Chemicals Handbook. 1985. Meister Publishing Co.. Willoughby, OH. 

Hayes, W.J., Jr. 1982. Pesticides Studied in Man, Waverly Press, Inc., Baltimore, MD. 

Hollifield, H.C. 1979. Rapid Nephelometric Estimate of Water Solubility 01 Highly Insoluble 

Organic Chemicals of Environmental Interest. Bull. Environ. Contarn. Toxicol. 23:57-586. 

Lyman, W.L., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co., New York. 

McEwen, F.L. and G.R. Stephenson, 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, Inc., New York. 

Ouellette, R.P., and J.A. Ring. 1977. Chemical Week Pesticides Register. McGraw-Hill Book 

Co., New York. 

Registry of Toxic Effects of Chemical Substances (RTECS) Database. 1984. Available through 

the National Library of Medicine’s. MEDLARS system, National Institute of Occupational Safety 

and Health (NIOSH). 

Reuber, M.D. 1980. Histopathology of Carcinomas of the Liver in Mice Fed Perthane. Tumori. 

66:277-283. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS system, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1986. Computer retrieval from Office of Pesticides for registered sites and number of 

products registered. 

Ware, G.W. 1975. Pesticides: An Auto-tutorial Approach. W.H. Freeman and Co., San Francisco. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck dc Co., Rahway, NJ. 

C-213 
C-214 
POLYCHLORINATED BIPHENYLS 

CAS No.: 1336-36-3 (undifferentiated) 

Specific CAS numbers have also been assigned to PCBs with various levels of chlorination and 

fc lr individual Aroclors. Some of the other CAS numbers include: 

Total Monochlorobiphenyl 27323- 18-8 

Total Dichlorobiphenyl 255 12-42-g 

Total Trichlorobiphenyl 25323-68-6 

Total Tetrachlorobiphenyl 269 14-33-O F 

Total Pentachlorobiphenyl 25429-29-2 

Total Hexachlorobiphenyl 2660 l-64-9 

Total Heptachlorobiphenyl 28655-7 l-2 

C’@@C 

Total Octachlorobiphenyl 3 1472-83-O 

Total Nonachlorobiphenyl 53742-07-7 C,&Cls, H~xach!ombiphyi 

Total Decachlorobiphenyl 205 l-24-3 Major Componml of Arodor 126( 

CAS Preferred Nomenclature: 

1,1 ‘-Biphenyl, chloro-derivatives 

Empirical Formula: Ct~t~xClx, where x is 1 to 10 

Synonyms and Common Names: 

- Chlorinated biphenyls 

- Chlorinated diphenyls 

- PCBs 

- Aroclors* 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories 

consumption of fish) (IRIS, 1989): for Aroclor 1016 (U.S. EPA, 1987): 

0.045 ngL a (10 Kg): 

long-term exposure = 1 lg/L 

aduls (70 Kg): 

long-term exposure = 4 pg/L 

l AKIC~O~S arc mixtures of PCBs that have been designated using a four-digit oumbaing system. The first two digits indicate the 

Pprent mh~~le (12 qmscats bipbenyl). The next two digits indicate tbe percult cbiorine. Up to 8 Cl atoms can be prrscnr 

c-215 
l EPA Ambient Water Quality Criteria l Food and Drug Administration 

(for protection of aquatic or- Tolerance Level for Fish and Shellfish 

ganisms)(U.S. EPA, 1976): (21 CFR 109.30): 

&eshwate[ 2 PPm 

Acute, pg/L 2.0 10.0 

Chronic. pg/L 0.014 0.03 

l EPA Drinking Water Standards (40 

CFR Part 141): 

Proposed Maximum Contaminant 

Level = 0.0005 mg/L 

Proposed Maximum Contaminant 

Level Goal = 0 mg/L 

Use Restrictions and Bans: 

l In 1977. EPA banned the production-based discharge of PCBs (CWA 307(a)( 1)). 

l In May 1979, EPA banned PCB manufacture, processing, and distribution in commerce 

(~50 ppm). Continued use was allowed in totally-enclosed electrical systems (40 CFR 

76). 

. In August, 1982,40 CFR 76 was revised to restrict uses of PCBs in electrical equipment. 

Some equipment was phased out. PCB transformers and electromagnets posing a risk 

to food were banned after October 1, 1985. In restricted access areas, PCB tranformers 

and large capacitors could be used until the equipment is worn out. 

l In 1985. EPA established standards to lower fire-related risk. The use of electrical 

equipment in commercial buildings and other high-risk areas was phased out. 

SOURCES OF PCBs 

Total PCB Production: 

l PCB production in the U.S. began in 1929 and stopped in 1977 (Ghirelli et al., 1983). 

Production peaked in 1970 at 85 million pounds (Matthews and Dedrick, 1984). Annual 

production between 1971 and 1977 averaged about 40 million pounds (ATSDR, 1987). 

Uses of PCBs: 

l PCBs are a family of chemicals. Commercial products can be mixtures of up to 209 

different compounds. After 1974, PCBs were used primarily as a dielectric fluid in 

capacitors and transformers. 

C-216 
l Prior to 1974, PCBs were used in other products as well: 

- plasticizer in plastic and rubber products 

- lubricant in hydraulic and vacuum fluids 

- ink carrier and solvent in manufacturing process for carbonless paper 

- sealer for gaskets and furnaces (Versar 1976, 1980; Ghirelh et al, 1983; ATSDR, 

1987). 

Other Sources: 

l Trace quantities of PCBs can be produced during manufacture of chlorinated hydrocarbon compounds in the presence of catalysts or at high temperatures (e.g. I,1 ,ltrichloroethene, tetrachloroethene, carbon tetrachloride) (Versa-r, 1983). 

FATE IN ENVIRONMENT 

Partitioning: 

. PCBs differ in their behavior depending on the number of chlorine atoms present. A 

higher number of chlorines (e.g., Aroclor 1260) makes the compound less soluble in 

water, and more refractory (i.e., does not degrade). PCBs, in general, are relatively 

insoluble, sorb strongly to organic matter (ROW = 750,000), and can volatilize (half-lives 

are 10 to 12 hours) (Callahan et al., 1979). In lakes, volatilization is considered to be 

an important loss process (Swackhamer and Armstrong, 1986). PCBs have a high 

potential for bioaccumulation (BCF values range from 26,000 to 660,000 [Leifer et al, 

19831). 

Persistence: 

l PCBs can undergo photoiysis, although specific rate constants in water were not found 

(Leifler et al., 1983; Callahan, et al., 1979). PCBs do not hydrolyze at a significant rate 

(Mabey et al., 1982). Biotransformation of KBs with three or fewer chlorines (e.g., 

Aroclor 1221 and 1232) can occur, while other PCBs are essentially refractory (Brown 

et al., 1987, Eeifler et al., 1983). Highly chlorinated PCBs can degrade by dechlorination 

reactions under anaerobic conditions to less chlorinated PCBs. These can then 

biodegrade (Brown et al., 1987). 

HEALTH EFFECTS 

Carcinogenic&y: 

l PCBs administered orally have been shown to cause liver tumors in rats and mice 

(Norback and Weltman, 1985; U.S. EPA 1985, 1987). They are classified as probable 

human carcinogens: IARC class 2b; EPA class B2 (IARC, 1982; IRIS, 1988). 

C-217 
l Because PCBs can be contaminated with other compounds (e.g.,chlorinated dibenzofurans. dioxin), it is difficult to assess the cause of observed cancers in human exposure 

incidents. 

Mutagenic Activity: 

l PCBs have not been shown to be mutagenic in either in vitro or in vivo experimental 

tests (ATSDR, 1987). 

l Negative results were obtained from the Ames bacterial test, the rat dominant lethal tests 

and fruit fly chromosomal tests (U.S. EPA, 1984). 

Reproductive Effects: 

l PCBs are fetotoxic in rats. monkeys, minks, and rabbits (U.S. EPA, 1984). 

. PCBs have not been found to be teratogenic in rats. mice, or monkeys (ATSDR, 1987). 

Other Toxkologid Effects: 

The major toxic effect in animals is liver damage (IARC, 1978). 

Other effects in animals include stomach, thyroid, and kidney damage, porphyria, and immunosuppressive effects (ATSDR, 1987). 

Accidental and occupational exposures of humans (to relatively high levels of PCBs) have resulted 

in chloracne and liver damage (Matthews and Dedrick, 1984; U.S. EPA, 1984; ATSDR, 1987). 

Toxicologicd Effects Indices: 

Cancer potency factor (CPF), total PCBs: 7.7 (m&/day)” (ATSDR, 1987) 

Reference Dose (RfD), Aroclor 1016: 0.0001 mg/kg/day (ATSDR, 1987) 

TWA-TLV (time-weighted average, threshold limit value), for occupational exposures: 

Aroclor 1254* = 0.5 m 

Y 

m3 (ACGM, 1986) 

Aroclor 1242 = 1 mg/m (ACGIH, 1986) 

l Oral LD5o: mink, 750 mg/kg (Aroclor 1221); rats. 1010 mg/kg (Aroclor 1254). 

‘Am&n are ~UX~UZU of PC& that hwa beam desigmtai using a fourdigit munbahg systau. The first two digits irxihte rhc 

paratt mokatie (I2 rcpmcotr bi@myl). The oext two digio i&ate the plaat cbbcine. Up 00 8 Ct atans caa be prrrsot 

C-218 
Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“C): 

Boiling Point (“C): 

Density, (g/cm3 at 25OC): 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

Vapor pressure, P (mm Hg): 

200.7-375.7 Hutzinger et al., 1974 

liquid 

N/A 

275420 Mackay et al., 1983 

1.15-1.58 at 25OC: Callahan et al., 1979 

N/A 

0.0027 (Aroclor 1260) Monsanto, 1974 

0.59 (Aroclor 1221) 

7.7~101 lm5 (Aroclor 1254) 

6.7~10~~ (Aroclor 1221) 

Callahan et al., 1979 

Hydrolysis: 

Henry’s Law Constant KB @ 

25OC (atm l m31mol): 

not environmentally 

significant 

5.28x104(Anxlor 1242) 

4.6x 1 Om3 (Aroclor 1260) 

Mabey et al., 1982 

ATSDR, 1987 

Log (Octanol-Water Partition 

Coefficient), log I&: 4.7 (Aroclor 1221) Hansch and Leo, 1985 

6.8 (Aroclor 1260) 

Soil Adsorption Coefficient, Koc (mug): 5.3x105 Mabey et al., 1982 

Fish Bioconcentration Factor, BCF: 26,000-660,000 Leifer et al., 1983 

31,200 U.S. EPA, 1980 

c-219 
ACGIH (American Conference of Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Occupational Exposures to Chemicals. ACGIH, Cincinnati, OH. 

ATSDR (Agency for Toxic Substances and Disease Registry). 1987. Draft Toxicological Profile 

for Selected PCBs. ATSDR. U.S. Public Health Service. 

Brown, J.F., Jr., B.L. Bedard, M.J. Brennan, J.C. Camahan, H. Feng, and R.E. Wagner. 1987. 

Polychlorinated Biphenyl Dechlorination in Aquatic Sediments. Science 236:709-7 12. 

Callahan, M.A., M.W. Slimak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri, W.R. Mabey, B.R. Holt, and C. Gould. 1979. Water-Related 

Environmental Fate of 129 Priority Pollutants, Vol. I. U.S. Environmental Protection Agency, 

Office of Water Planning and Standards, Washington, DC. EPA-440/4-79-029a. 

Ghirelli. R.P. F.H. Palmer. T.L. Spielman, M. Jung, R.L. Severeid, G.W. Bowes, D.B. Cohen. 

1983. Polychlorinated Biphenyls. California State Water Resources Control Board. Special 

Projects Report No. 83- lsp. 

Hansch, C. and A.J. Leo. 1985. Log P Data Base. Pomona College, Claremont, CA. 

Hutzinger, S., S. Safe, and V. Zitko. 1974. The Chemistry of PCBs. Chemical Rubber Publishing 

Co., Cleveland, OH. 

International Agency for Research on Cancer. 1978. IARC Monographs on the Evaluation of the 

Carcinogenic Risk of Chemicals to Humans, Vol. 18. IARC, Lyon, France. 

IntemationaI Agency for Research on Cancer. 1982. IARC Monographs on the Evaluation of the 

Carcinogenic Risk of Chemicals to Humans, Vol. 29. IARC, Lyon, France. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Leifer, A., R.H. Brink, G.C. Thorn, K.G. Partymiller. 1983. Environmental Transport and 

Transformation of Polychlorinated Biphenyls. U.S. Environmental Protection Agency, 

Washington, DC. EPA-560/5-83-025. 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. MilI, T.W. Chou, J. Gates, I.W. Partridge, 

H. Jaber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440- 4-81-014. 

Mackay, D., W.Y. Shiu, J. BilIington, and G.L. Huang. 1983. Physical Chemical Properties of 

Polychlorinated Biphenyls in Physical Behavior of PCBs in the Great Lakes. (D. Mackay, S. 

Paterson, S.J. Eisenreich, and M.S. Simmons, eds.). Ann Arbor Science, Ann Arbor, MI. 

c-220 
Matthews, H.B.. and R.L. Dedrick. 1984. Pharmacokinetics of PCBs. Ann. Rev. Phannacol. 

Toxicol. 24:85- 103. 

Monsanto. 1974. PCBs-Aroclors Technical Bulletin O/PL 360A. St. Louis, MO. 

Norback, D.H., and R.H. Weltman. 1985. Polychlorinated Biphenyl Induction of Hepatocellular 

Carcinoma in the Sprague-Hawley Rat. Envir. Health Perspective 60:97- 105. 

Swackhamer, D.L., and D.E. Armstrong. 1986. Estimation of the Atmospheric and Nonatmospheric Contributions and Losses of Polychlorinated Biphenyls for Lake Michigan on the Basis of 

Sediment Records of Remote Lakes. Environ. Science and Technol. 20(9):879-883. 

U.S. EPA. 1976. Quality Criteria for Water. US. Environmental Protection Agency, Office of 

Water and Hazardous Materials, Washington, DC. 

U.S. EPA. 1980. Ambient Water Quality Criteria Document. U.S. Environmental Protection 

Agency, Washington, DC. EPA 440/5-80 Series. 

U.S. EPA. 1984. Health Effects Assessment for Polychlorinated Biphenyls. U.S. Environmental 

Protection Agency, Office of Emergency and Remedial Response. Washington, DC. EPA-540/l86-004. 

U.S. EPA. 1985. Draft Drinking Water Criteria Dcoument for Polychlorinated Biphenyls (PCBs). 

U.S. Environmental Protection Agency, Washington, DC. NTIS #PB86-1183lUAS. 

U.S. EPA. 1987. Final Drinking Water Criteria Documents for Polychlorinatcd Biphenyls. U.S. 

Environmental Protection Agency, Washington, DC. ECACO-CIN-414. 

Versar. 1976. PCBs in the United States: Industrial Use and Environmental Distribution. Prepared 

by Versar, Inc., for U.S. Environmental Protection Agency under contract 68-01-3259, Task 1. 

Versar. 1980. Production and Use of PCB 1248 and 1254. Prepared by Versar, Inc., for U.S. 

Environmental Protection Agency, Monitoring and Data Support Division, under contract 68-01- 

3852, Task 22, Subtask 1. 

Versar. 1983. Exposure Assessment for Incidentally Produced Polychlorinated Biphenyls (PCBs). 

Prepared by Versar, Inc., for U.S. Environmental Protection Agency, Office of Toxic substances, 

under contract 68-O l-625 1, Task 2. 

Wilson, D.L. 1988. Project Summary Report on Decontamination of PCB-Gearing Sediments. 

U.S. Environmental Protection Agency, Hazardous Waste Engineering Research Laboratory, 

Cincinnati, OH. EPM600/52-87/093. 

c-221 
PCBs 

OBSERVATIONS AND EFFECTS ON PISCIVOROUS WILDLIFE 

During the last two decades, polychlorinated biphenyls (PCBs) were commonly detected in the 

tissues and eggs of fish-eating birds. Szaro et al. (1979) found PCBs in all eggs that were collected 

from successful colonies of the herring gull and great black-backed gull in Maine. PCBs were also 

detected in 50% of black-crowned night heron eggs from the intermountain western states (Kenny 

et al., 1984). PCB residues were detected in 83% of the ospreys found dead or moribund in the 

eastern states (Weimeyer et al., 1987), and in 90% of various heron species collected nationwide 

(66 percent found dead or moribund) (Ohlendorf et al., 1981). 

PCB residues were apparently the cause of death of many ring-billed gulls in southern Ontario in 

1969 and 1973. Of the specimens sampled that died of no apparent disease, 61% had residues of 

PCBs in the brain exceeding the lethal level of 310 ppm, and 30% had PCB concentrations greater 

than 200 ppm in the brain (Stickel et al., 1984). DDE and dieldrin were also present in most 

specimens. DDE residues were at a lethal level (250 ppm) in one specimen, and dieldrin residues 

were at a lethal level (5 ppm) in more than 14% of the dead birds. 

High reproductive failure of Lake Ontario herring gulls in the early 1970s prompted an investigation 

of the organochlorine concentration in the gull eggs. PCB concentrations of up to 180 ppm were 

detected. This level is one order of magnitude greater than the concentration found in eggs from 

successful herring colonies on Lakes Erie, Huron, and Superior. Reproductive success of the Lake 

Ontario herring gull colonies improved in latter years, parallelling a decline in PCB and other 

organochlorines concentrations in gull eggs (We&oh et al., 1979). However, Gilman et al. (1978, 

1977) suggest that high levels of mirex, not PCBs, in the eggs were to blame for the reproductive 

failure. 

In 1981 and 1982 duck hunters from New York and New Jersey were cautioned about eating wild 

waterfowl. The waterfowl from the Hudson and Niagara River areas contained greater than 5 ppm 

PCBs (fresh weight), which was in excess of FDA tolerances for poultry (Eisler, 1986). 

Fish-eating mammals are also affected by PCBs. Mink are very sensitive to PCBs and are the most 

sensitive of the wildlife species tested (Eisler, 1986). Aconcentration as low as 0.64 ppm wet weight 

in food can cause reproductive failure in mink (Plantonow and Karstud, 1973). Ringer (1983) 

determined that a concentration of 0.67 ppm in the mink diet causes reproductive failure. In the 

field, residues of PCBs indicative of reproductive failure have been observed in mink from western 

Maryland and northern Oregon (Henny et al., 1981; O’Shea et al., 1981). 

River otters from the Columbia River in Oregon were found with high levels of PCBs. Henny et 

al. (1981) suggest these elevated PCB levels may be contributing to the declining harvest of the 

Columbia River otter. 

Based on Plantonow and Karstud’s 1973 mink study, the International Joint Commission (a United 

States-Canada Treaty Organization) set an objective for PCB in fsh at 0.1 ppm to protect piscivorous 

c-222 
wildlife (Newell et al., 1987). The State of New York proposed a slightly less conservative tish 

flesh criterion of 0.13 ppm from the same data to protect piscivorous wildlife (Newell et al., 1987). 

The effects of PCBs on piscivorous wildlife are summarized in the following table: 

Effects of PCB Concentrations on Pisdvorous Wildlife 

Animal 

Birds 

Mink 

Mink 

Piscivorous 

Wildlife 

3 10 ppm (brain) death 

0.64 mg/kg 

(diet) 

reproduction 

impaired 

0.67 mg/kg 

(diet) 

or 

0.225 pprn/day 

(diet) 

reproduction 

impaired 

Stickel, 1984 

Plantonow and 

Karstud, 1973 

Ringer, 1983 

0.1 mg/kgfday 

(diet) 

NOEL Ringer, 1983 

0.13 ppm (diet) 

0.11 ppm (diet) 

estimated 

NOEL 

cancer risk 

of lo’2 

Newell et al., 

1987 

Newell et al., 

1987 

C-223 
Eisler. R. 1986. Polychiorinated Biphenyl Hazards to Fish, Wildlife and Invertebrates: A Synoptic 

Review. U.S. Fish Wildl. Serv. Biol. Rep. 85(1.7). 

Gilman, A.P.. G.A. Fox, D.B Peakall., S. M. Teeple, T.R. Carroll and G.T. Hatmes. 1977. 

Reproductive Parameters and Egg Contaminant Levels of Great Lakes Herring Gulls. J. Wildl. 

Manage. 41:458-468. (As cited in Eisler, 1985) 

Gilman, A.P., D. J. Kallett, G.A. Fox, L.J. Allan, in J. Learning and D.B. Peakall. 1978. Effects 

of Injected Organochlorines on Naturally Incubated Herring Gull Eggs. J. Wildl. Manage. 

42:484-493. (As cited in Eisler, 1985) 

Kenny, C.J., L.J. Blus, S. V. Gregory, and C. J. Stafford. 1981. PCBs and Organochlorine 

Pesticides in Wild Mink and River Otters from Oregon. In Worldwide Furbearer Conference 

Proceedings, Vol. III, ed. J.A. Chapman and 0. Pursley, pp. 1763- 1780. Frostburgh, MD. (As cited 

in Eisler, 1986) 

Kenny, C.J., L.J. Blus, A.J. Krynitsky, and C.M. Bunck. 1984. Current Impact of DDE on 

Black-Crowned Night-Herons in the Intermountain West. J. Wildl. Manage. 48( 1): 1-13. 

Newell, A.J., D. Johnson, and L.K. Allen. 1987. Niagara River Biota Contamination Project: Fish 

Flesh Criteria for Piscivorous Wildlife. Tech. Rep. 87-3. NY Dept Environ. Conserv., Div. Fish 

Wildl., Bureau Environ. Protection. 

Ohlendorf, H.M., D.M. Swineford, and L.N. Locke. 198 1. Organochlorine Residues and Mortality 

of Herons. Pest. Monit. J. 14(4):125-135. 

O’Shea, T.J., T.E. Kaiser, G.R. Askins, and J.A. Chapman. 1981. Polychlorinated biphenyis in a 

wild mink population. In Worldwide Furbearer Conference Proceedings, Vol. III, ed. J.A. Chapman 

and D. Pursley, pp. 1746-1752. Frostburgh, Md. (As cited in Eisler, 1986) 

Plantonow, N., and C. Karstud. 1973. Dietary Effects of Polychlorinated Biphenyls on Mink. Can. 

J. Comp. Med. 37:391-400. (As cited in Newell, 1987) 

Ringer, R. 1983. Toxicology of PCBs in Minks and Ferrets. In PCBs: Human and Environmental 

Hazards, ed. F.D’It.ri and M. Kamrin, pp. 227-140. Butterworth Pub., Woburn, MA. (As cited in 

Newell et al., 1987) 

Stickel, W.H., L.F. Stickel, R.A. Dyrland, and D.L. Hughes, 1984. Aroclor 1254 Residues in Birds: 

Lethal Levels and Loss Rates. Arch. Environ. Contam. Toxicol. 13:7-13. 

Szaro, R.C., N.C. Coon, and E. Kolbe. 1979. Pesticides and PCB of Common Eider, Herring GuIl 

and Great Black-Backed GulI Eggs. Bull. Environm. Contam. Toxicol. 22:394-399. 

C-224 
Weimeyer, S.N., SK Schmeling, and A. Anderson, 1987. Environmental Poflutant and Necropsy 

Data for Ospreys from the Eastern United States, 1975-1982, J. Wildl. Diseases 23(2):279-291. 

Weseloh, D.V., P. Mineau, D.J. Hallet, 1979. Organochlorine Contaminants and Trends in 

Reproduction in Great Lakes Herring Gulls, 1974-1978. Trans. N. Am. Wildl. Nat. Resour. Conf. 

44:543-557. 

c-225 
c-224 
1,2,3,4 AND 1,2,3,5 TETRACHLOROBENZENE 

1,2,3+TETRACHLOROBENZENE: 

CAS No.: 634-66-2 

CASPrefferredNomenclature: 

Benzene, 1,2,3,4-tetrachloroEmpirical Formula: C6H2CL4 

Synonyms and Common Names: 

- 1,2,3,4 TCB 

1,2,3,5TETRACHLOROBENZENE: 

CAS No.: 634-90-2 

CAS Preferred Nomenclature: 

Benzene 7 1 9 2 , 3 t %trachloroEmpirical Formula: C&I2C4 

Synonyms and Common Names: 

- 1,2,3,5 TCB 

REGULATORY STATUS 

Cl l-l 0 0 Cl 

cl Cl 

l EPA Water Quality Criteria (for l EPA Drinking Water Health Advisories: 

human consumption of fish): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic organisms): Level for Fish: 

None established at present None established at present 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use None found. 

C-227 
SOURCES OF 1,2,3,4 AND 1,2,3,5 TETRACHLOROBENZENE 

. ToQJJ.J.3.4 and.5 TCB Produ& 

l No current producers for either tetrachlorobenzene were identified (SRI, 1986). 

Uses . of la.4 -1.26.5 TCB, 

. 1,2,3,4 TCB has been used as a component of dielectric fluids (Verschueren, 1983). 

l No information was found on the uses of 1,2,3,5 TCB. 

. soua None identified. 

FATE IN ENVIRONMENT 

l Based on their properties, both 1,2,3,4 and 1,2,3,5 TCB are moderately volatile (estimated H = 1.300 to 1,400 atm l m3/mole), strongly sorb to soil (bW = 43,000 to 

83,000). and have a high potential for bioaccumulation. (BCF values from experimental 

data ranged from 1,800 to 72,000.) 

l Little information is available on the photolysis and hydrolysis of either 1,2,3,4or 1,2,3,5 

TCB, but based on the similarity of their structure to 1,2,4,5 TCB, neither process is 

expected to be environmentally significant. 

l Because of the high degree of chlorination of 1,2,3,4 and 1,2,3,5 TCB, biodegradation 

is not expected to occur readily (Perwak et al., 1983). However, in a solution of 200 

mg/L of 1,2,3,4 TCB, Pseudomonas bacteria were able to produce 33% ring degradation 

after 120 hours at 30” (Verschueren, 1983). It is likely that 1,2,3,5 TCB would behave 

similarly. 

HEALTH EFFECTS 

. No data found. EPA has not classified the potential carcinogenicity of either 1,2,3,4 or 

1,2,3,5 TCB. 

C-228 
l No adequate data available (U.S. EPA, 1980). 

l In rats 1,2,3,4 TCB reduced embryonic growth at the level that also caused maternal 

poisoning effects (1000 mgkg) (TDB, 1985). 

l No data were found for 1,2.3,5 TCB. 

. Tordco)oeicalects, 

+ Liver damage was produced in rats fed high doses of 1.2.3.4 TCB (1,000 to 6,600 

mg/kg/day) (TDB, 1985). 

l Rats fed 1.2.3.5 TCB (75 mgkg) for 2 months developed enlarged adrenal glands. No 

specific health effects were noted as a result of this condition (U.S. EPA. 1980). 

None found. 

C-229 
PHYSICAL/CHEMICAL PROPERTIES 

1.2.3.4 TETRACHLOROBENZENE: Value Reference 

Molecular Weight: 2 15.9 Verschueren, 1983 

Physical State @ 2O*C: solid needles Verschueren, 1983 

Melting Point (“0 47.5 Weast, 1986 

Boiling Point (“C): 254 Weasf 1986 

Specific Gravity: 1.70 Kirk-Otbmer, 1982 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 5.92 Banerjee, 1984 

3.5 (22OC) Verschueren, 1983 

Vapor Pressure, P (mm Hg): 0.027 (25*C) Kirk-Othmer, 1982 

Henry’s Law Constant, H @ 

25*C (atm l m3/mol): 1.3x1o’3 (talc.) Lyman et al., 1982 

Log (Octanol-Water Partition 

Coefficient), log KOW: 4.64 

Soil Adsorption Coefficient, Koc (mL/g): 1 .2x104 (talc.) Lyman et al., 1982 

Fish Bioconcentration Factor, BCF: 2100 (talc.) Lyman et al., 1982; 

1,125 to 12,000 US. EPA, 1980 

(expt.M 

C-230 
PHYSICAL/CHEMICAL PROPERTIES 

I ,2,3,5 TETRACHLOROBENZENE: Value Reference 

Molecular Weight: 215.9 Verschueren, 1983 

Physical State @ 20°C: solid 

Melting Point (“C): 54.5 Weast, 1986 

Boiling Point (“C): 246 Weast, 1986 

Specific Gravity: N/A 

Acid Dissociation Constant, p&: N/A 

Water Solubility, S (mg/L): 5.10 Banerjee, 1984 

2.4 (22OC) Verschueren, 1983 

Vapor Pressure, P (mm Hg): 1 @ 58.2”C Weast, 1986 

Henry’s Law Constant, H @ 

25*C (atm l m3/mol): 1.4x1o-3 (talc.) Lyman et al., 1982 

Log (Octanol-Water Partition 

Coefficient), log Kow: 4.92 Leo, 1983 

Soil Adsorption Coefficient, I& (mL/g): 2.0x lo4 (talc.) Lyman et al., 1982 

Fish Bioconcentration Factor, BCF: 4,000 (talc.) Lyman et al., 1982 

1,800 to 72,000 U.S. EPA, 1980; 

6qt.l. > Verschueren, 1983 

C-231 
REFERENCES 

Banerjee, S. 1984. Solubility of Organic Mixtures in Water. Environ. Sci. Technol. 18:587-591. 

Hawley, G.G. 198 1, The Condensed Chemical Dictionary. 10th ed. Van Nostrand Reinhold, Inc., 

New York. 

IARC (International Agency for Research on Cancer). 1977. IARC Monographs on the Evaluation 

of the Carcinogenic Risk of Chemicals to Humans. Vol. 15. IARC, Lyon, France. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Leo, A.J. 1983. Log P Parameter Database. Pomona College, Claremont, CA. 

Lyman, W.G., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co.. New York 

Oliver, B.G., and A.J. Niimi. 1983. Bioconcentration of Chlorobenzenes from Water by Rainbow 

Trout: Correlations with Partition Coefficients and Environmental Residues. Environ. Sci. Technol. 17:287-291. 

Penvak J., E. Cole, S. Coons, N. Green, W. Lyman, M. Miller, J.H. Ong, and K. Scow. 1983. 

Evaluation of Waterborne Exposure Pathways to Paragraph 4(c) Pollutants. U.S. EPA Draft Report. 

EPA Contract 68-01-5949. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine, TDB Peer Review Committee. 

U.S. EPA 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA 440/5-80-028. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Weast, R-C., ed. 1986. CRC Handbook of Chemistry and Physics. 67th ed. CRC Press, Boca 

Raton, FL. 

C-232 
1,2,4,5 TETRACHLOROBENZENE 

CAS No.: 95-94-3 

CAS Preferred Nomenclature: 

Benzene, 1,2,4,5tetrachloroEmpirical Formula: C6H2Cl4 

Synonyms and Common Names: 

- 1,2,4,5 TCB 

- 5Tetrachlorobenzene 

- s-Tetrachlorobenzene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Standard Maxiconsumption of fish)(45 FR 79318): mum Contaminant Level: 

43 pi& None established at present 

l EPA Ambient Water Quality Criteria l EPA Drinking Water Health Advisories 

(for protection of aquatic organisms) None established at present 

(IRIS, 1989): 

Freshwater Saltwater 

Acute, pg/L 250 160 

Chronic, pg/L 50 129 

Above are LECs (Lowest Effect Concentration), 

l Food and Drug Administration Action 

Level for Fish: 

None established at present 

Yse None found. 

C-233 
Total 13.4.5 Tetrachlorobenzene Produced: 

+ In 1977, Dow Chemical produced between 10 million and 50 million pounds of 1,2,4,5 

TCB (Perwak et al., 1983). 

Uses of 1,2,4,5 Tetrachlorobenzene: 

l 1,2,4,5 TCB is a chlorophenoxy compound used as a precursor for the production of the 

herbicide, 2,4,5 T(2,4,5 trichlorophenoxyacetic acid). 2,4,5 T was a major component 

of Agent Orange, the defoliant used in Vietnam (Klaassen et al., 1986). 

l 1,2,4,5 TCB has also been used as a precursor for the production of other organic 

chemicals and in the dye industry (Perwak et al., 1983). 

l It has also been utilized in the moisture-proofing of electrical insulation (Penvak et al., 

1983). 

Other None identified. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, 1,2,4,5 TCB is highly volatile (H = 0.027 atm 

l m3/mole). strongly sorbs to soil (KoW ~47,ooO), and has a high potential for bioaccumulation. BCF values from experimental data ranged between 5,300 and 13,000. 

Persistence: 

l Photolysis is not expected to be significant for 1,2,4,5 TCB since little absorption occurs 

in the solar region (>290 mm) for the chemical (Perwak et al., 1983). 

. Biodegradation is not expected to occur readily because of the high degree of chlorination, although m bacteria are able to produce 30% ring disruption of a 200 

mg/L solution at 30’ after 120 hours (Perwak et al., 1983; Verschueren, 1983). In one 

study under anaerobic conditions, chlorobenzenes persisted for 7 years (TDB, 1985). 

l Hydrolysis of 1,2,4,5 TCB is not expected to be environmentally significant (Perwak 

et al., 1983). 

1,2,4,!j TETRACHLOROBENZENE OBSERVED IN THE ENVIRONMENT 

l No data available. 

C-234 
HEALTH EFFECTS 

Carcinogenicity: 

l EPA has not yet evaluated the potential carcinogenicity of 1,2,4,5 TCB (IRIS, 1989). 

Mutagenic Activity: 

l No adequate data available (U.S. EPA, 1980). 

ctiveEflects: No data found. 

Other Toxicologkal Effects: 

l No reported effects on humans. 

l Rats fed 1,2,4,5 TCB for 13 weeks developed kidney damage at relatively moderate 

doses (0.34 mg/kg/day). Liver damage was also reported to occur at higher doses (3.4 

to 32 mg/kg/day). A higher dose (200 mg/kg/day) caused a significant increase in deaths 

(IRIS, 1989). 

l Dogs fed 1,2,4,5 TCB (5 mg/kg/day) for 2 years showed no adverse health effects (IRIS, 

1988). 

ToxicologW Effects Indices: 

l Reference Dose (RfD): 3~10~ mg/kg/day (IRIS, 1989). 

l Oral LDso: rats, 1500 mg/kg; mice, 1035 mgkg (Tatken and Lewis, 1984). 

C-235 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (‘CT): 

Boiling Point (“0: 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, H @ 

25°C (atrn l m3/mo1): 

Log (Octanol-Water Partition 

Coefficient), log Kow: 

Soil Adsorption Coefficient,& (mug): 

Fish Bioconcentration Factor, 

BCF: 

215.9 

solid 

139.5 

248 

1.833 

N/A 

6.0 

0.3 (22°C) 

0.045 (25°C) 

0.027 (talc.) 

4.67 

1 .6x103 

5300 to 13000 

(expfl. 1 

1125 

W indholz. 1983 

Kirk-Othmer, 1984 

Kirk-Othmer, 1984 

Kirk-Othmer, 1984 

PHRED, 1988 

Verschueren, 1983 

Kirk-Othmer, 1984 

Lyman et al., 1982 

PHRED, 1988 

PHRED, 1988 

Oliver and Niimi, 

1983 

PHRED, 1988; 

U.S. EPA, 1980 

C-234 
IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Kirk-Ochmer Encyclopedia of Chemical Technology. 1984. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Klaassen, C.D., M.O. Amdur, and J. Doull, eds. 1986. Casarett and Doull’s Toxicology: The Basic 

Science of Poisons. 3rd ed. Macmillan Publishing Co., New York. 

Lyman, W.G.. W.F. Reehl, and D.H. Rosenblatt 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill Book Co., New York. 

Oliver, B.G., and A.J. Niimi. 1983 Bioconcentration of Chlorobenzene from Water by Rainbow 

Trout: Correlations with Partition Coefficients and Environmental Residues. Environ. Sci. Technol. 17:287-29 1. 

Perwak J., E. Cole, S. Coons, N. Green, W. Lyman, M. Miller, J.H. Ong, and K. Scow. 1983. 

Evaluation of Waterborne Exposure Pathways to Paragraph 4(c) Pollutants. Draft Report U.S. 

Environmental Protection Agency, Washington, DC. EPA Contract 68-01-5949. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

Tatken, R.L., and R.J. Lewis, Sr., eds. 1983. Registry of Toxic Effects of Chemical Substances. 

(RTECS). 1981-82 ed. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine, TDB Peer Review Committee. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA 440/5-80-028. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Weast, R.C., ed. 1986. CRC Handbook of Chemistry And Physics. 67th ed. CRC Press, Boca 

Raton, FL. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

C-237 
C-238 
1,2,3 TRICHLOROBENZENE 

CAS No.: 87-61-6 

CAS Preferred Nomenclature: 

Benzene,l,2,3-trichloroEmpirical Formula: C6H3C 13 

Synonyms and Common Names: 

- 1.2.6~trichlorobenzene 

- vie-trichlorobenzene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria l EPA Drinking Water Health 

(for human consumption of fsh): Advisories: 

None established at present None established at present 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic Level for Fish: 

organisms): None established at present 

None established at present 

l EPA Drinking Water Standard 

Maximum Contaminant Level: 

None established at present 

Use: None found. 

SOURCES OF 1,2,3 TRICHLOROBENZENE 

I,td1,2,3 Trichlorobenzene Produced: 

l In 1977, Dow Chemical Company in Midland, Michigan, produced between 1 and 10 

million pounds of 1,2,3 trichlorobenzene (Pen+& et al., 1983). In 1986, Standard 

Chlorine Chemical (Delaware City, Delaware) was the only producer, but production 

figures are not available (SRI, 1986). 

C-239 
Uses of 1,2,3 Trichlorobenzene: 

. 1.2.3 trichlorobenzene is not commonly used directly, but instead is used as an intermediate in chemical synthesis (Sax, 1986). 

. 1.2.3 uichlorobenzene is used as a solvent for high-melting products, as a coolant in 

electrical installations and glass tempering, for polyester dying, termite preparations, 

synthetic transformer oil, lubricants, heat transfer medium, and insecticides (Sax, 1986). 

None found. 

FATE IN ENVIRONMENT 

Partitionine: 

l Based on its physical/chemical properties, 1,2,3 trichlorobenzene sorbs moderately 

strongly to sediment (I&W = 12,900). Volatilization can occur from water at a moderate 

rate (H = 9.3x10d atm l m3/mol). The potential for bioaccumulation is high based on 

experimental data. (BCF ranged between 1,200 and 2,600.) 

Persistence: 

l Direct photolysis of 1.2.3 trichlorobenzene is not likely to occur in natural waters 

(Perwak et al., 1983). 

l Hydrolysis is not an environmentally significant process (Ellington et al., 1986). 

l Biotransformation of 1,2,3 trichlorobenzene may occur but at an unknown rate. No 

degradation occurred beneath the water table (anaerobic conditions) (TDB, 1986). 

Perwak et al. (1983) reported that 10% of 1,2,3 trichlorobenzene degraded after 12 weeks 

in a soil containing high organic matter and up to 8% volatilized, while only 2% degraded 

in a soil with low organic material content (up to 40% volatilized). Degradation by 

-bacteria is more rapid; at 30°, 87% ring disruption occurred within 120 

hours in a concentration of 200 mg/L 1.2.3 trichlorobenzene (Verschueren, 1983). 

HEALTH EFFECTS 

Carcinogenicity: 

l No data found. EPA has not classified the potential carcinogenicity of 1,2,3 

trichlorobenzene. 

. . v No data found. 

c-240 
ReDroductive No data found. 

Other Toxicologkal Effects: 

l Trichlorobenzenes can cause liver damage in humans and animals (Gosselin, 1984; 

HSDB, 1988). 

l 1,2,3 trichlorobenzene is irritating to human eyes and mucous membranes of the 

respiratory tract (Sax, 1986; HSDB, 1988). 

l 1.2.3 trichlorobenzene is considered moderately toxic to humans with acute or chronic 

ingestion or inhalation (Sax, 1986). 

l At high doses, technical-grade trichlorobenzene (30% 1.2.3 TCB and 70% 1,2,4 TCB) 

is moderately irritating to rabbit skin (HSDB, 1988). 

Toxicoloticai Effects Indkes: 

l None found for human exposure. 

l Chronic Hazard Level for rats: 0.01 mg/kg/day/5.5 month {loss of hair) (Sax, 1986). 

C-241 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

Melting Point (“0 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pI& 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25OC (atm l m3/mol): 

Log (Octanol-Water Partition 

Coefficient), log K~w: 

Soil Adsorption Coefficient, K (mug): 

Fish Bioconcentration Factor, BCF: 

181.45 

solid, white 

crystals 

53.5 

218.5 

1.69 

N/A 

12 @ 22OC 

0.07 8 25OC 

9.3x104 (cab) 

4.11 

4600 (caic.) 

1200-2600 

(expti.) 

Kirk-Othmer, 1982 

Sax, 1986 

Kirk-Othmer. 1982 

Kirk-Othmer, 1982 

Windholz, 1983 

Verschueren, 1983 

U.S. EPA, 1980 

Lyman et al., 1982 

Leo, 1983 

Lyman et al., 1982 

Oliver and Niimi, 

1983 

C-242 
Ellington, J.J., F.E. Stancil, Jr., and W.D. Payne. 1986. Measurement of Hydrolysis Rate Constants 

for Evaluation of Hazardous Waste Land Disposal. Vol. I. U.S. Environmental Protection Agency, 

Athens, GA. EPA/600/3-86/043. 

Gosselin, R.E., R.P. Smith, H.C. Hodge, and J.E. Braddock. 1984. Clinical Toxicology of 

Commercial Products. 5th ed. The Williams and Wilkins Co., Baltimore. 

HSDB. 1988. Hazardous Substances Data Base. National Library of Medicine, Bethesda, MD. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Leo, A.J. 1983. Log P Parameter Database, Issue #24 (dated 12/16/83). Obtained from the 

MedChem Project, Pomona College, Claremont, CA. 

Lyman, W.G., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill Book Co., New York 

Oliver, B.G., and A.J. Niimi. 1983. Bioconcentration of Chlorobenzenes from Water by Rainbow 

Trout: Correlations with Partition Coefficients and Environmental Residues. Environ. Sci. Technol. 17:287-291. 

Perwak, J., E. Cole, S. Coons, N. Green, W. Lyman, M. MilIer, J.H. Gng, and K. Scow. 1983. 

Evaluation of Waterborne Exposure Pathways to Paragraph 4(c) Pollutants. Draft Report U.S. 

Environmental Protection Agency, Washington, DC. EPA Contract 68-01-5949. 

Sax, N.I. 1986. Hazardous Chemicals, Information Annual, No. I. Van Nostrand Reinhold Co., 

New York. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS system, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Washington, DC. EPA 440/5-80- 

028. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

C-243 
Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck and Co., Rahway, NJ. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-244 
1,2,4 TRICHLOROBENZENE 

CAS No.: 120-82-l 

CAS Preferred Nomenclature: 

Benzene, 1,2,4,-trichloroEmpirical Formula: C6H3C 13 

Synonyms and Common Names: 

- Hostetex L-PEC 

- Unsym-Trichlorobenzene 

- 1,2,4 Trichlorobenzol 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human + EPA Drinking Water Health Advisories: 

consumption of fish) (U.S. EPA, 1989): None established at present 

15.4 mg/L 

l EPA Ambient Water Quality Criteria + Food and Drug Administration Action 

(for protection of aquatic organisms): Level for Fish: 

None established at present None established at present 

l EPA Drinking Water Standard Maximum Contaminant Level: 

(U.S. EPA, 1989) 

Proposed MCLG 9 q/L 

. . se- None 

found. 

SOURCES OF 1,2,4 TRICHLOROBENZENE 

Total 1,2,4 Trkhlorobenzene Produced: 

+ In 1979, 16 million pounds of 1,2,4 trichlorobenzene were produced (Perwak et al., 

1983). 

C-245 
Uses of 1.2.4 Trkhlorobenzene: 

l 1,2,4 ttichlorobenzene is used as a solvent in chemical manufacturing, in dyes and 

intermediate production, and in transformer dielectric fluid. In addition, it is used as a 

degreaser. lubricant, and termiticide (Verschueren, 1983; Sax, 1986). 

Other: None found. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physical/chemical properties, 1,2,4 trichlorobenzene strongly sorbs to 

organics (&~19,900) and can volatilize (H = 2.3~10~~ atm l m3/mol). In addition, 

the potential for bioaccumulation is high (BCF estimated as 2,800). 

Persistence: 

. 1,2,4 trichlorobenzene is not expected to undergo hydrolysis at an environmentally 

significant rate (Mabey et al., 1982). 

l The biotransformation rate of 1.2.4 trichlorobenzene is reportedly very slow. After 135 

hours, no degradation of 0.1 mg/L 1,2,4 trichlorobenzene exposed to normal sewage 

occurred. However, 56% was degraded by adapted sewage (Verschueren, 1983). 

m bacteria transformed 1,2,4 trichlorobenzene at a faster rate, with concentrations of 200 mg/L (at 30’) undergoing 92% ring disruption after 120 hours 

(Verschueren, 1983). 

HEALTH EFFECTS 

Carchogenldty: 

l McNamara et al. (198 1) reported no increased incidence of tumors in a 6-month feeding 

study. A 2-year skin painting study with 1,2,4 trichlorobenzene demonstrated no 

increase in tumors in mice (HSDB, 1988). These studies, however, am not considered 

adequate for caxcinogenicity assessment. 

l No tumor development was observed in mice inhaling 600 ppm 1,2,4 trichlorobenzene 

daily for 6 months (U.S. EPA, 1980). 

l EPA has not classified the carcinogenic potential of 1.2.4 trichlorobenzene. 

Mutagenic Activity: 

l 1,2,4 trichiorobenzene was found to be nonmutagenic in the bacterium a 

. . m (McNamara et al., 198 1). 

c-244 
Reproductive Effects: 

L While no increases in teratogenicity or embryo lethality were observed in rats fed 360 

mg/kg/day on days 9-13 of gestation, retarded embryonic development occurred 

(Kitchin and Ebron, 1983). 

Other Toxicological Effects: 

l Chronic (long-term, low-dose) exposure to 1,2,4 trichlorobenzene has resulted in liver, 

kidney, brain, and lung damage in animals (Sittig, 1985; HSDB, 1988). 

l In humans, exposure to 1,2,4 trichlorobenzene has been reported as causing central 

nervous system stimulation, headache, dermatitis, and skin, eye, and throat irritation 

(Sax, 1986; HSDB, 1988). 

l At high doses, technical-grade trichlorobenzene (30% 1,2,3 TCB and 70% 1,2,4 TCB 

is moderately irritating to rabbit skin (HSDB, 1988). 

ToxicoIogkal Effects Iudices: 

l Reference Dose (RfD): 2x10-2 mg/kg/day (PHRBD, 1988). 

l TLV-C (threshold limit value-ceiling - 

posure): 40 mg/m3 (ACGIH, 1986). 

not to be exceeded during occupational exl Oral LD5o: rat, 756 mg/lcg (U.S. EPA, 1980; HSDB, 1988). 

C-247 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 2OT: 

Melting Point (‘C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25OC (atm l m3/mol): 

Log (Octanol-Water Partition Coefficient), log Kow: 

Soil Adsorption Coefficient, 

Koc (mUg): 

Fish Bioconcentration Factor, BCF: 

181.45 

clear liquid 

17.15 

213.8 

1.45 (20/4”C) 

N/A 

30 63’ 25°C 

0.29 @ 25OC 

2.3x 10-3 

4.3 

9.2x103 

2800 (talc.) 

Kirk-Othmer, 1984 

Kirk-Othmer, 1984 

Kirk-Othmer, 1984 

Weast. 1986 

Sax. 1986 

U.S. EPA. 1980 

Mabey et al., 1982 

PHRED, 1988 

PHRED, 1988 

PHRED, 1988; 

ICF, 1985 

C-248 
REFERENCES 

ACGIH (American Conference for Governmental Industrial Hygienists). 1986. Threshold Limit 

Values for Chemical Substances in the Work Place. ACGIH, Cincinnati, OH. 

Callahan, M.A., M. W. Shmak, N.W. Gabel, I.P. May, C.F. Fowler, J.R. Freed, P. Jennings, R.L. 

Durfee, F.C. Whitmore, B. Maestri. 1979. Water Related Environmental Fate of 129 Priority 

Pollutants. U.S. Environmental Protection Agency, Washington DC. EPA-440/4-79-029a. 

HSDB. 1988. Hazardous Substances Data Base. National Library of Medicine, Bethesda, MD. 

ICF, Inc., 1985. Draft Superfund Public Health Evaluation Manual. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Kitchin, K.T., and M.T. Ebron. 1983. Material Hepatic and Embryonic Effects of 1,2,4- 

Trichlorobenzene in the Rat. Environ. Res. 3 1:362-373. 

Lyman, W.G., W.F. Reehl, and D.H. Rosenblatt. 1982. Handbook of Chemical Property Estimation Methods. McGraw-Hill Book Co., New York 

Mabey, W.R., J.H. Smith, R.T. Podoll, H.L. Johnson, T. Mill, T. W. Chou, J. Gates, J.W. Patridge, 

H. Saber, and D. Vandenberg. 1982. Aquatic Fate Process Data for Organic Priority Pollutants. 

SRI International. EPA 440/4-g I-O 14. 

McNamara, P.W., M. Byrne, M. Goyer, P. Lucas, K. Scow, and M. Wood. 198 1. An Exposure 

and Risk Assessment for 1,2,4,-Trichlorobenzene. U.S. Environmental Protection Agency, Office 

of Water Regulations and Standards, Washington, DC. EPA 44014-85-017. 

Perwk, J., E. Cole, S. Coons, N. Green, W. Lyman, M. Miller, J.H. Ong, and K. Scow. 1983. 

Evaluation of Waterborne Exposure Pathways to Paragraph 4(c) Pollutants. Draft Report. U.S. 

Environmental Protection Agency, Washington, DC. EPA contract 68-01-5949. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. EPA Office of Emergency and 

Remedial Response, Washington, DC. 

Sax, N-1. 1986. Hazardous Chemicals Information Annual. No. 1. Van Nostrand Reinhold Co., 

New York. 

Sittig, M. 1985. Handbook of Toxic and Hazardous Chemicals and Carcinogens. 2nd ed. Noyes 

Publications: Park Ridge, NJ. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

C-249 
U.S. EPA. 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA 440/5-80-028. 

U.S. EPA. 1987. Draft of RCRA Facility Investigation,(ELFI) Guidance. U.S. Environmental 

Protection Agency, Office of Solid Waste, Washington, DC. EPA 53O/SW-87-001. 

U.S. EPA, 1989. Draft Summary of Drinking Water Regulations and Health Advisories, U.S. 

Environmental Protection Agency, Office of Drinking Water, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold. New York. 

Weast, R.C., ed. 1986. CRC Handbook of Chemistry and Physics. 67 ed. CRC Press, Boca Raton, 

FL. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

c-250 
1,3,5 TRICHLOROBENZENE 

CAS No.: 108-70-3 

CAS Preferred Nomenclature: 

Benzene, 1.3.5~trichloroEmpirical Formula: C6H3C 13 1,3,5-trichlofoboruono 

Synonyms and Common Names: 

- sym-Trichlorobenzene 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human l EPA Drinking Water Health Advisories: 

consumption of fish): None established at present 

None established at present 

l EPA Ambient Water Quality Criteria l Food and Drug Administration Action 

(for protection of aquatic organisms): Level for Fish: 

None established at present None established at present 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use None found. 

SOURCES OF 1,3,5 TRICHLOROBENZENE 

Total 1,3,5 Trichlorobenzene Produced: 

l In 1986,1,3,5 trichlorobenzene was produced by Southland Corporation. No production 

data are available (SRI, 1986). 

Uses of 1,3,5 Trichlorobenzene: 

l 1,3,5 trichlorobenzene is commonly used as an intermediate in chemical synthesis of 

other organic compounds (Sax, 1984). 
l 1,3,5 trichlorobenzene is also used as a solvent for dyes in textile manufacture (KirkOthmer, 1982). 

None found. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based on its physictichemical properties, 1.3,5 uichiorobenzene is moderately volatile 

(H estimated to be 6.0 x 10m3 atm l m3/mo1), is moderately sorbed to soil (~W=lO,OOO), 

and has a high potential for bioaccumulation. (BCF from experimental data range from 

1,800 to 4.100.) 

Persistence: 

l Hydrolysis and aqueous photolysis are expected to be unimportant under environmental 

conditions based on the structural similarity with 1,2,3 and 1,2,4 trichlorobenzene. 

l Using fresh sewage, 1,3,5 trichlorobenzene at an initial concentration of 1.0 mg/L was 

not degraded after 135 hours, compared with 47% degraded using acclimated sewage. 

Biodegradation by Pseudomonas bacteria was found to be more rapid, with 78% of an 

initial 200-mg/L sample degraded (ring disruption) after 120 hours at 30°C (Verschueren, 

1983). 

1,3,5 TRICHLOROBENZENE OBSERVED IN THE ENVIRONMENT 

9 No data available. 

HEALTH EFFECTS 

Carcinogenicity: 

l No data found. EPA has not classified the potential carcinogenicity of I,3,5 

trichlorobenzene. 

. v: No data found. 

Reproductive Effects: 

l No teratogenic effects were observed in rats when mothers were fed 135 ttichlorobenzene at doses between 75 and 600 mg/kg. There were some mild changes in bone 

development (at unspecified doses) (U.S. EPA, 1985). 

c-252 
Other Toxicological Effects: 

. 1,3,5 trichlorobenzene has been foound to be moderately irritating to human skin, eyes, 

and mucous membranes (Sax, 1984). 

l Rats that inhaled 1.3,5 trichlorobenzene on a schedule simulating possible occupational 

exposures (6 hours/day, 5 days/week, for 13 weeks) developed some reversibIe changes 

to lung tissues (U.S. EPA, 1985). 

l It has been reported that trichlorobenzenes cause liver damage to humans and animals, 

but it is not known which one (1.35 1,2,3 or 1,2,4 trichlorobenzene) is the toxic 

component (Gosselin, 1984). 

. None found. 

C-253 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 2O*C: 

Melting Point (“C): 

Boiling Point (“0 

Specific Gravity: 

Acid Dissociation Constant, pKa: 

Water Solubility, S (mg/L): 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25*C (atm l m3/mol): 

Log (Octanol- Water 

Partition Coefficient), log &w: 

Soil Adsorption Coefficient, K&mug): 

Fish Bioconcentration Factor, BCF: 

181.45 

solid 

63.4 

208.5 

N/A 

N/A 

5.88 @ 2o”c 

0.15 (2YC) 

6.0x10-3 (talc.) 

4.49 

9 100 (talc.) 

1400 (talc.) 

1800-4100 

(exptl.) 

Kirk-Othmer, 1982 

Windholz, 1983 

Kirk-Othmer, 1982 

Verschueren, 1983 

U.S. EPA, 1980 

Lyman et al., 1982 

Leo, 1983 

Lyman et al., 1982 

Lyman et al., 1982 

Oliver & Niimi, 1983 

C-254 
Gosselin, R.E., R.P. Smith, H.C. Hodge, and J.E. Braddock. 1984. Clinical Toxicology of 

Commercial Products. 5th ed. The Williams and Wilkins Co., Baltimore. 

Kirk-Othmer Encyclopedia of Chemical Technology. 1982. 3rd ed. John Wiley and Sons, Inc., 

New York. 

Leo, A.J. 1983. Log P Parameter Database, Pomona College, Claremont, CA. 

Lyman, W.G., W.F. Reehl, and D.H. Rosenblatt. 1982 Handbook of Chemical Property Estimation 

Methods. McGraw-Hill Book Co.. New York. 

Oliver, B.G., and A.J. Niimi. 1983. Bioconcentration of Chlorobenzenes from Water by Rainbow 

Trout: Correlations with Partition Coefficients and Environmental Residues. Environ. Sci. Technol. 17:287-291. 

Sax, N.I. 1984. Dangerous Properties of Industrial Materials. 6th ed. Van Nostrand Reinhold Co., 

New York. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Toxicology Data Bank (TDB) Database. 19851986. Avaiiable through the National Library of 

Medicine’s MEDLARS System, National Library of Medicine, TDB Peer Review Committee. 

U.S. EPA. 1980. Ambient Water Quality Criteria for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Water Regulations and Standards, Criteria and Standards Division, 

Washington, DC. EPA 440/5-80-028. 

U.S. EPA. 1985. Health Assessment Document for Chlorinated Benzenes. U.S. Environmental 

Protection Agency, Office of Health and Environmental Assessment, Washington, DC. EPA 

600/8-84-O 15F. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicab. 10th ed. Merck & Co., Rahway, NJ. 

c-255 
C-256 
TRIFLURALIN 

CAS No.: 1582-09-8 

CAS Preferred Nomenclature: 

Benzenamine, 2,6-dinitro-N,Ndipropyl-4-(trifluoromethyl)- 

Empirical Formula: C 13H 16F3N304 

Synonyms and Common Names: 

- Treflan - Triflurex 

- Trefanocide - Crisalin 

- Elancolan - Trim 

- Ipersan - Ipifluor 

REGULATORY STATUS 

Standards and Criteria: 

l EPA Water Quality Criteria (for human 

consumption of fish): 

None established at present 

l EPA Ambient Water Quality Criteria 

(for protection of aquatic 

organisms): 

None established at present 

l EPA Drinking Water Standard Maximum Contaminant Level: 

None established at present 

Use Restrictions and Bans: 

l EPA Drinking Water Health Advisories 

(IRIS, 1989): 

w(lO kg): 

1 day, 1 O-day, long-term 

exposures = 30 pg/L 

iiduls (70 kg): 

long-term exposure = 30 pg/L 

lifetime exposure = 2 pg/L 

l EPA Tolerance Levels in foods for 

human consumption (40 CFB 180.207): 

0.05 to 2 ppm 

l Food and Drug Administration Action 

Level for Fish: 

None established at present 

l As of August 1982, all technical formulations were to be formulated to contain less than 

0.5 ppm of N-nitrosamine contaminants (47 FR 33777). 

C-257 
SOURCES OF TRIFLURALIN 

Total Trifhralin Produced: 

l The herbicidal properties of the dinitroanilines, particularly trifluralin, were first 

reported in 1960 (Farm Chemicals Handbook, 1985). In 1982,25,000 tons of trifluralin 

were produced, of which 18,000 tons were used in the U.S. (Green et al., 1987). In 1986, 

only the Eli Lilly Co. produced trifluralin (SRI, 1986). 

Uses of Triflurdin: 

l Trifluralin is used as a herbicide to control annual grasses and broadleaf weeds in a wide 

variety of agricultural crops and in some domestic and industrial situations (Worthing, 

1983; U.S. EPA, 1987a). 

l The primary uses of trifluraiin are on cotton and soybeans. In 1987, the uses were 

divided as follows: 65% on soybeans, 19% on cotton, 8% on sunflowers, 4% on wheat, 

and 6% for all other purposes (U.S. EPA, 1987a). 

l Trifluralin is registered for use on 40 broadleaf crops (McEwen and Stephenson, 1979). 

It is also used to control weeds in orchards and in vegetable crops (47 FR 33777). 

a Nonagricultural uses are the control of grasses (e.g., barnyard grass, chickweed, 

crabgrass) in rights-of-way, for outdoor domestic sites and industrial sites (McEwen and 

Stephenson, 1979; Thomson, 1983; Farm Chemicals Handbook, 1985; U.S. EPA, 

1987a). 

None identified. 

FATE IN ENVIRONMENT 

Partitioning: 

l Based upon its physical/chemical properties, trifluralin is predicted to volatilize relatively slowly from both water (H = 1.9 x IO4 atm l m3/mo1) and soil surfaces (P/S& = 

3.3 x lO”0 mm Hg l Umg, corresponding to an estimated volatilization half-life of 48 

days), adsorb relatively strongly to soils and sediments (& = 218,8OO), and have a high 

potential for bioaccumulation (BCF = 1.8 x lo3 to 6.0 x 103) (Lyman et aL, 1982). 

+ Trifluralin appears to have a very low potential for leaching. Gray et al. (1982) reported 

that after elution with 60 cm of water, >90% of the applied trifluralin and >99% of the 

trifluralin accounted for remained in the upper 5 cm of soil columns packed with a sandy 

loam (oc = 0.8%), a silt loam (oc = 2,8%), or a clay Loam (oc = 1.3%) soil. Helling and 

Turner (1968) reported that trifluralin was essentially immobile (IQ = 0.0) on soil 

thin-layer chromatography plates using 14 different soils. 

C-258 
l Bionomics (1973) reported trifluralin tissue concentrations of 5.5 to 12 mg/kg in bluegill 

sunfish exposed to an average of 7.9 pg/L over 35 days. The tissue to water concentration ratios correspond to non-steady-state bioconcentration factors of 7.0 x lo2 to 1.5 x 

103. 

Persistence: 

l Mosier and Saunders (1978) reported that trifluralin at 30°C did not undergo any 

detectable hydrolysis at pH 3.6, or 9 over a 32-day period. 

l Trifluralin is susceptible to photolytic degradation (McEwen and Stephenson, 1979; 

TDB, 1985). A study by Zepp and Baughman reported a half-life of approximately 1 

hour for trifluralin in water exposed to sunlight (TDB, 1985). 

l Trifluralin is also biodegradable; a Pseudomonas bacterium has been found that decomposes it in aqueous media (Lyman et al., 1982.) The rate of biodegradation is uncertain. 

Parr and Smith (1973) reported that the rate of trifluralin degradation in a silt loam soil 

was much greater under anaerobic conditions (~1% remaining after 20 days incubation) 

than under aerobic conditions (approximately 85% remaining after 20 days incubation). 

l In soil, half-lives of 3 to more than 27 weeks have been reported (Verschueren, 1983). 

The associated dissipation rates ranged from O.O33/day to O.O037/day. Other detexminations of trifluralin half-lives are: 

- 21 to 35 days in irrigated soils 

- 126 to greater than 190 days in a sandy loam soil 

- 50 days in sandy loam soil in a greenhouse (Worthing, 1983). 

l Research by Golab et al. (1979) showed that trifluralin can undergo dealkylation and 

cyclazation reactions to form 28 different breakdown products. 

HEALTH EFFECTS 

Cardnogenidly: 

l EPA has classified trifluralin as a possible human carcinogen (group C) on the basis that 

there is only limited evidence from animal experiments that it causes cancer (U.S. EPA, 

1987a, b). 

l In a feeding experiment with rats, trifluralin caused kidney tumors, but only at very high 

doses (6500 ppm) and at a rate only slightly greater than that seen in control animals 

(Tatken and Lewis, 1983; U.S. EPA, 1987a). 

l Studies with mice and hamsters showed that technical-grade trifluraiin caused liver and 

lung tumors. However, it was not certain whether these were caused by the trifluralin 

alone or by the nitrosamine contaminant (84-88 ppm dipropylnitrosamine) (47 FR 

33777; Gosselin et al., 1984; U.S. EPA, 1987a). 

C-259 
l Similar chemicals (e.g., ethalfluralin) have been demonstrated to cause tumors in rats 

(US. EPA, 1987a). 

Mutagenic Activity: 

l Trifluralin is not considered to be mutagenic. The dominant lethal test with mice was 

negative as were tests with yeast cells and sister chromatid (chromosome) exchange in 

hamster cells (U.S. EPA, 1987a). 

Reproductive Effects: 

l Trifluralin has not been shown to impair the reproductive ability of rats, rabbits, or dogs 

(U.S. EPA, 1987a. b). The only adverse effect demonstrated was reduced birth weights 

in rats exposed to high doses (IRIS, 1989). 

Other Toxicological Effects: 

+ Trifluralin is not acutely toxic to humans but may cause eye or skin irritation in exposed 

humans (Dreisbach, 1980; U.S. EPA, 1987a). 

l Long-term, low-dose (chronic) exposure to trifluralin caused kidney damage in rats (at 

200 ppm) (U.S. EPA, 1987a). 

Toxicological Effects Indices: 

9 Reference Dose (RfD): 7.5~10~~ mgAcg/day (IRIS, 1989). 

l Cancer Potency Factor (CPF): 7.7~10.~ (mgAcg/day)*’ (IRIS, 1989). 

l Oral LD5o: mice, 500 mg/kg; rats, 10,000 mgkg; dogs, chickens, rabbits, 2 mg/kg (U.S. 

EPA, 1987b). 

c-260 
PHYSICAL/CHEMICAL PROPERTIES 

Value Reference 

Molecular Weight: 

Physical State @ 20°C: 

335.3 

yellow-orange 

crystalline solid 

Melting Point (“C): 

Boiling Point (“C): 

Specific Gravity: 

Acid Dissociation Constant, p&: 

Water Solubility, S (mg/L): 

48.5-49 

139-140 @ 

4.2 mm Hg 

N/A 

0.3 

4.0 @ 27°C 

Vapor Pressure, P (mm Hg): 

Henry’s Law Constant, 

H @ 25°C (atm l m3/mol): 

Log (Gctanol-Water Partition 

Coefficient), log Gw: 

Soil Adsorption Coefficient, Koc (mL/g): 

Fish Bioconcentration Factor, BCF: 

1.1x10-4 (25OC) 

1.9x10” (talc.) 

5.34 

1.37x104 

1800-6000 

Worthing, 1983 

Worthing, 1983; 

U.S. EPA, 1987b 

Worthing, 1983 

Windholz, 1983 

N/A 

U.S. EPA, 1987b; 

Herbicide Handbook, 1983 

Worthing, 1983; 

Verschueren, 1983 

U.S. EPA, 1987a 

Lyman et al., 1982 

Leo, 1983 

PHRED, 1988 

Worthing, 1983 

C-261 
REFERENCES 

Bionomics EG+G. 1973. Exposure of Fish to 14C-trifluralin: Accumulation, Distribution, and 

Elimination of 14C Residues. Submitted to U.S. Environmental Protection Agency by Elanco 

Products Co. 

Dreisbach, R.H. 1980. Handbook of Poisoning: Prevention, Diagnosis and Treatment. Lange 

Medical Publications, Los Altos, CA. 

Farm Chemicals Handbook. 1985. Meister Publishing Co., Willoughby, OH. 

Golab, T., W.A. Althaus, and H.L. Wooten. 1979. Fate of 14C) Trifluralin in Soil, J. Agric. Food 

Chem. 27:163. 

Gosselin, R.E., R.P. Smith, H.C. Hodge, and J.E. Braddock. 1984. Clinical Toxicology of 

Commercial Products. 5th ed. The Williams and Wilkins Co., Baltimore. 

Gray, J.E., A. Loh, R.F. Sieck. et al. 1982. Laboratory Leaching of Ethalfluralin. Eli Lilly Co. 

Green, M.B., G.S. Hartley, and T.F. West. 1987. Chemicals for Crop Improvement and Pest 

Management. 3rd ed. Pergamon Press. Oxford, England. 

Helling, C.S. 1976. Dinitroaniline Herbicides in Soils. J. Environ. Qual. 5( l):l-15. 

Helling and Turner. 1968. Pesticide Mobility: Determination by Soil Thin-Layer Chromatography. Sci. 162:562-563. 

Herbicide Handbook. 1983 Weed Science Society of America. 5th ed. Champaign, IL. 

IRIS. 1989. Integrated Risk Information System. U.S. Environmental Protection Agency, 

Washington, DC. 

Leo, A.J. 1983. Log P Parameter Database, Issue #24 (dated 12/16/83). Obtained from the 

Medchem Project, Pomona College, Claremont, CA. 

Lyman, W.J., W.F. Reehl, and D.H. Rosenblatt, eds. 1982. Handbook of Chemical Property 

Estimation Methods. McGraw-Hill, New York. 

McEwen, F.L., and G.R. Stephenson. 1979. The Use and Significance of Pesticides in the 

Environment. John Wiley and Sons, New York. 

Mosier, J., and D. Saunders. 1978. A Hydrolysis Study on the Herbicide Trifluralin. Eli Lilly Co. 

Submitted to U.S. Environmental Protection Agency, Washington, DC. 

C-262 
Parr, J.F., and S. Smith. 1973. Degradation of Trifluralin Under Laboratory Conditions and Soil 

Anaerobiosis. Soil Sci. 115(1):55-63. 

PHRED. 1988. Public Health Risk Evaluation Database. U.S. Environmental Protection Agency, 

Office of Emergency and Remedial Response, Washington, DC. 

SRI (Stanford Research Institute). 1986. Directory of Chemical Producers. Stanford Research 

Institute, Menlo Park, CA. 

Tatken, R.L., and R.J. Lewis, Sr., eds. 1983. Registry of Toxic Effects of Chemicals Substances 

(RTECS). 198 l-82 ed. 

Thomson, W.T. 1985. Agricultural Chemicals Book II - Herbicide. 1981-82 ed. 

Toxicology Data Bank (TDB) Database. 1985-1986. Available through the National Library of 

Medicine’s MEDLARS system, National Library of Medicine. TDB Peer Review Committee. 

U.S. EPA. 1987a. Guidance for the Reregistration of Pesticide Products Containing Trifluralin as 

the Active Ingredient. U.S. Environmental Protection Agency, Office of Pesticides and Toxic 

Substances, Washington, DC. EPA 540 RS-87 195. 

U.S. EPA. 1987b. Draft Trifluralin Health Advisory. U.S. Environmental Protection Agency, 

Office of Drinking Water, Washington, DC. 

Verschueren, K. 1983. Handbook of Environmental Data on Organic Chemicals. 2nd ed. Van 

Nostrand Reinhold, New York. 

Windholz, M., ed. 1983. The Merck Index: An Encyclopedia of Chemicals, Drugs, and Biologicals. 10th ed. Merck & Co., Rahway, NJ. 

Worthing, C.R., ed. 1983. The Pesticide Manual: A World Compendium. 7th ed. British Crop 

Protection Council, Croydon, England. 

C-263 
APPENDIX D 

Data Tables 
APPENDIX D-1 

Site Description Matrix * 

*Also included in Volume I, Appendix B-3 
Key to Table D-1 

Matrix of Episodes and Site Descriptions 

Descriptions of the column headings for Table D-l are as follows: 

COLUMN HEADING DESCRIPTION 

1. 

2. 

3. 

4. 

5. 

6. 

7. 

8. 

9. 

10. 

11. 

12. 

13. 

14. 

15. 

16. 

16. 

17. 

18. 

EPA REGION The U.S. Environmental Protection Agency Region which includes the 

sample location. 

EPISODE The EPA Episode Number which is specific to each sampling event. 

LATITUDE The latitude of the sample site in degrees, minutes and seconds. 

LONGITUDE The longitude of the sample site in degrees, minutes and seconds. 

STATE The state closest to the sample location. 

WATERBODY Name of the water where the sample was collected. 

LOCATION The nearest town, road or county to the sample location. 

NSQ Sample site selected using a statistical procedure to represent a subset of 

the sites in the USGS NASQAN network. 

B Background site as selected for study. 

POINT SOURCES: Point sources include the following six categories: 

PPC Site near paper and pulp mill using chlorine for process). (includes mills 

using the sulfite process). 

PPNC Site near paper and pulp mill not using chlorine for bleaching as well as 

deinking plants. 

REFINERY Site near refinery using the catalytic reforming process. 

NPL SITE Site near an EPA National Priority List Site (Superfund site). 

OTHER INDUSTRY Site near industrial discharge other than a paper mill or refinery. 

POTW Site near discharge of a Publicly Owned Treatment Works (municipal 

sewage). 

WP Site near active or former wood pereserving activity. 

NONPOINT; Nonpoint sources include the following two categories: 

URBAN Site receives urban runoff. 

AGRICULTURE Site receives agricultural runoff. 

SITE DESCRIPTION A brief sentence or list of additional information concerning the site. 

D-1-1 
D-1-2 
TABLE D-I 

Mawix of Episodes and Site Descriptions 

- 

u 

b 

I 

I 

I 

I 

I 

I 

I 

I 

I 

1 

I 

I 

I 

I 

I 

I 

I 

I 

I 

11 

II 

II 

!I 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

--- I -___ 

2375 41:36:47N 071:58:26W 

2349 42:37;25N U7t:U;IOW 

3151 42335322N 072:2t:&IW 

3150 42335:46N VR.Q3:27W 

23% 44:tbION oxk13:SftW 

2721 44:15:2ON OXh1OtsOW 

272s 44:.3OzO!lN ORkt5SllW 

3026 44zlO:2IIN ~M25W 

3023 45:OII:UIN 06~l!XSW 

2x58 443&m 067:55:3ow 

.w22 4432:wN ommI5w 

2355 444!k2oN 068:429W 

2722 43:34:35N UNh33:45W 

3u27 43:34%N m33:55W 

3023 4t543ON m5.5.m 

.3#24 44:WSKlN tWk15:lsW 

3025 44;4!k4lN 069z24:Mw 

3152 44:24:42N U7l:tl:29W 

3426 Q35;45N tnl:12:2Ow 

3429 39:34:3ON 075331:tXtW 

3430 39:183XlN tJ74373OW 

2651 393tHON 074:3S~O0W 

3427 4039:15N 074:09:16W 

2653 40543ON 07412.m 

Wit 40343:15N M4M:ISW 

333 4012tt:24N 074:03.40w 

3434 40:27:(YtN 07403:oOW 

2654 3957:MN 074:12:3OW 

3304 43:59:xw lm.o(:w 

3M 42:51:45N 07%:52:ooW 

32%I 42:52ztIIN 078523W 

3)ol 43:2&m 07843.oOW 

2326 42:llMN tml~lmw 

CT OuinipiacRivct 

CT Ouioncbaug Riw 

MA Merrimack RiKr 

MA Milkrr Rivet 

MA OtterRivet 

ME AadrtscqiaR. 

ME AndtoscoggiaR. 

ME AndroscqgiaR. 

ME Andr~nR. 

ME BcaraLakc 

ME Narra@ugusR. 

ME No&P& 

ME PewbsaxR. 

ME SamRim 

ME !&oRivcr 

ME Sandy Pond 

ME Scbastiamk E. Br. 

ME S.&Amok W. Br. 

NH Androsca@inR. 

NJ Arthur Kill 

NJ lktwuc River 

NJ Great b Harbor 

NJ MulliiRiva 

NJ Newark Bay 

NJ P~suicRivct 

NJ Pas&River 

NJ RaritanBay 

NJ Sandy Hook 

NI TmuRivet 

NY Black River D&a 

NY Buffalo Harbm 

NY BuffabRiw 

Nod Hswzlr 

Jcwtt City 

Tyngs Island 

Green Bank 

Eliibcsh 

PtiCMa 

NCWd 

NY E+~tc. Mik Ctt& Olcdt 

NY Gcncucc Riw B&Do& 

NY Ge-R&t Belmont 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

T 

PlOWHlW 

=i 

tPr*(lolm~~d~~*) -- 

hdustry cficmicrl & pe.~icideq ekcttaaiu; pbics; mctrls; SuperLad 

site (solwxur) 

Id.: nrgamic hem. & pcs~., tcdiks; Superfund site (Fursnr) 

Ind.: chcm. k pcs~.. industrial WWIP; P&P mill oa Natma R. (bib.); 

supcrflmd site (sohents) 

Ewing Paper Milb; wooded area; &: cropl;mnd.s and grazing fields 

Ening Paper Mills; woo&d arca; Ag.: aopbds irnd gszbg f&k 

IntcrnAaml Paper. Boise Cascade. James Rivet; Ind : tcaiks 

lncetortional Paper Co. in Jay 

Boise CZasadc in Rumford, rutd,wmdcd area 

Id: teniks; downstream d papct mills 

Two blucbcr~ ptmrsig pbs; blueberry fields (peslicas) 

Noiwdustrl;waodcdandawampyuu 

J- Rivu Cotpotatioa m Old Torm 

Same as #27; POIW 00 upatteam bib. yc~ is Baclqymmd site 

Slmcrrm2;POTWoauprlrumIrb.~kB~ouod~t 

lmlusttial WWTP 

lndorttial WWTP 

James Rivet Ccqmtatiaa 

GAP cacp. (clwn. mumfacsuring) 

Sup&tad site (several sitcq tials & org. chcmicab) 

B~~+omd mn thugb brs afgicultutd area and FOTW ncatby 

waodcd area 

Marcal Paper and P&P mill 011 lrib.; lad.: meta& c&m. B put.; 

supuflmd rile (solvents) 

80 I&let AK: cbcm. maoufacluting 

P&P mill clllwnr iislobq Enam Co.; tthl.: chcm.; SupctIund site (LcKraI 

s&s; metals & org. &cm.) 

Exon co. 

Ind.: chemical; Superlund site (chlurobcatcnc; Hg) 

Fw ppw milts (PPNC); Air Brake Co.; hydrqxnwr; &in-y fictds 

Ind.: chcmiol. steel. pclrochcmicsl; Lndfillr 

AU&J Clmmiul (dadsct d HCB); landfills 

lnd.: Harriwa Radialor; dub. (HCB); A&: admds nd cqhm& 

Same as 3309. Sampkd t&w Bclmonl Dun. Supfmbd de ir 

approximately IO mites upstream (hcrry mclals. bydtocabns.) 

Same as 2326 

- --- - 

D-1-3 
E. 

Ia 

i 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

II 

I1 

II 

II 

II 

II 

II 

II 

II 

II 

II 

If 

II 

II 

II 

II 

Ill 

Ill 

111 

III 

Ill 

Ill 

III 

111 

_-. . 

i#d 

u -- 

13% 

33lY 

332n 

2109 

3259 

3m 

3321 

3322 

3260 

2.328 

2329 

3323 

3324 

3325 

3326 

33aa 

3297 

3299 

3302 

3303 

3412 

3305 

2322 

no9 

WI1 

I307 

1327 

I432 

u31 

!?I0 

1147 

nxJ9 

me 

m-l 

1149 

,100 

1317 

-. 

* 

1 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

4 

I 

I 

1 

3 

3 

3’ 

3 

3 

3 

13 

- --___ - 

f.aJw+I laqt4dc 

U:57:MN 074:4!MOW 

. -.. --___- 

9r(l wkddy IrDllu - 

NY GrassRivcr MJSSCllJ 

9U:40:OON 073:M~W NY Great Swtb Bay B&ykm 

W).10:45N 073: l9.OOW NY Greet South 8J,’ BJ~+'J" 

4I:l6:XIN 07357~W NY HudsonRiKr Peekskill 

43:08:00N 073:%:3OW NY HudsonRiwr 

ll:ZO~N 07357:MW NY HudxmRivcr 

Forl Miller 

Peettkill 

IO:3&l:4ON O-fMOdOW NY Jamaica Bay New York 

K):37:4SN on:47zOOW NY hmica BJ~ New York 

t3:51:3ON 07322iUW NY IA&C Champlain TiirogJ 

t3:20:2SN 07%43314W NY Late Ontuio okott 

13: 14&3SN l?77:32.03W NY btc Ontario Rochcslcr 

fO:48:00N 073:45.AMlW NY Littk Neck BJY long Is. Sound 

KI47.IMN 073345.aW NY littk Necb BJY Long Is. Sound 

lOz49tNlN 073:4ooW NY MJ~SSCI~ BJY lmtg Is. Sound 

IO:K):ION U73:4D:IsW NY M~nbassc~t BJY Lmg Is. Swmd 

13:15:30N 079~03z45W NY NiwraR. D&J PlXtcr 

13:039ON 078:58:SSW NY Niqpra River Niagua Falls 

13zU.?~tlON 078:53:4SW 

13: Io:?aN 079:0x low 

14:123ON 075~oOW 

l3:18tKIN 0’&3l%!OW 

W:W34lN 071:uzOOW 

NY luiagarl River N. Tonrwanda 

NY N&JJ~J River Lcwistm 

NY Oswcgalchk River Nevron Falls 

NY Oswcgo Harbor Oswcgo 

NY Raquclte Riw MJsscnJ 

U:59:ooN 073:2l:oOW 

,5.a.dJON U?3:2tm 

3:ll.lsN 077.3l:3oW 

4:423ON 075:28:3OW 

NY Ricbelicu River Rouses Pt. 

VY Ricbeliiu R&r Rouses Ft. 

riY Rochester Embny. Racbestcr 

rlY SI. Lawrence River ogdcnsburg 

033:MN 074:m: I SW 

7:59:4ON 066:466:2SW 

8264ON 066M:sWW 

R:52:2ON 0?7:02:15W 

8:52:mN 077amw 

8:35aN tJls:12aJw 

9:4R:tMlN 07S:39:44W 

9:35MN 075:37:SOW 

9:43:58N U75:45:3Tw 

Y:l5:36N 076131:MW 

9malN 079:01aJw 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

I 

t 

I 

b 

rlY Upper Bay New York 

PR tiuajanilla Bay 

DR SanJuanHubm 

x3 E. Polomar Riur 

X2 PotaaicRkw Park 

x lndiJnRitw 

IE Red Clay Creek 

X RcdLioaCreek 

)E White Clay Creek 

AD Baltimore Harbor 

AD Potomac R.N. Br. 

San JUJO 

DC 

N. d W&on Br 

Rouxi& Bcacl 

ASblJUd 

T)imIS ComCl 

-pron 

Baltimore 

WCsMlpOrt 

-- 

ZL!! 

X 

X 

i 

X 

X 

TABLE D-l (Cunt.) 

?olNr SOURCE? _- -- - _..-_ ._- .-.- --- 

N?L olher 

WC r?Nt- W? Rf,q SMm Id ?UlW 

X 

x x 

X X 

x x 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X X 

X 

X 

x x 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

I 

-- 

NONFOlh 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

> 

lr 

x 

n 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

~____-_-. 

-*lk9criJun 

(hcl8narr~d*yn~~) 

Sampkd bcbw ALCOA’S wthll (PC6 cmcern); GM & Rcyndds (2 -- 

miks b&w mouth d r&r) 

sanK Js 3320 

s8llK 8s 3319 

SJIIK as 3409; ind.: cbcm.; P&P mill 150 river miles updream; SupxfunJ 

site (PCB) 

For1 Milkr Pulp end Paper (Wnch. ~V~II & Co.) 

Same as noP, Ind.: drem.; P&P mill 150 river miles up&cam; Supcrfuad 

site (PCB) 

Ind.: &cm.; airport; landliil 

lad.: chcm.; Jirpnrt; lJr+dfti 

lntcrnatioal Paper Co. 

Ag.: rppk orchards and crap&nds 

Ind.: cbem (hd~k); Site it the mouth dGcnuec River 

.%mc as 3324 

SJmc Js 3323 

SJmc 8s 3326 

s8mc Js 3325 

Id: cbcm.; Olin, Dupoat. Oxirkntal (HCB); Ag.: orcbuda; landfti 

Ind.: &cm.; Olin, Dupnnt. Oxidcntal Cbcm. (HCB). (uunpaaira 

downstream d cite) 

Id: chcmiul 

Ind.: &em.; Olin, Dupanl, Otidental (HCB); Ag.: orchards 

Ncwlon FJIIs Paper Mill (defunct since October IY84) 

lod.: Chca 

Patsdam Paper l rbd Norfolk Paper (PPNQ; ALCOA. GM, Rep&la 

(upl=d-W 

lad.: chcmiul 

Pondcrosa Fiis (out d twiness more thin 4 years); Dow cbcmiul in 

CJIIJdJ 

Sampkd It 69th Street Piir 

Grihbcan Gulf Rctiniw Carp.; l&fill 

Ind.: mct~l platin& milm& illegal dump (l~difi); A&: muhmom f& 

lhemical spill (HCB amarn); SuptxM site (HCB) 

wcsrvJco (iJdim¶); NUJI 

D-l-4 
TABLE D-I (Cont.) 

- 

Kl 

RI 

ii 

II 

II 

II 

II. 

III 

III 

III 

111 

111 

Ill 

III 

111 

Ill 

III 

III 

Ill 

Ill 

III 

III 

III 

111 

Ill 

III 

III 

III 

111 

III 

111 

III 

ur 

‘A 

I 

I 

I 

I 

I 

1 

I 

I 

/ 

I 

I 

I 

I 

a 

1 

7 

‘I 

! 

a 

w 

I - 

2231 

3103 

3316 

3161 

3420 

3094 

3095 

3096 

3318 

3419 

3310 

3101 

2215 

2212 

3104 

3415 

2211 

l414 

5315 

I216 

)422 

w21 

2225 

2228 

2227 

2220 

3423 

3424 

3193 

3258 

!.500 

1314 

1311 

I312 

1313 

L3-M 

009 

- 

wm& w 

393X3lN (IF6:lOQgW 

399SDN @76zI(MIIw 

41:2HON 078341OW 

3956mN 075: l4:35W 

39:53:42N 076:mw 

90:02:24N 074:59:2oW 

3!3533oON 075311:46W 

395136N B75:llMOW 

4IL?3:2ON 078:2):2OW 

42ztKk25N awMIz:SW 

0:3!HON 075:14:35W 

4OzO3NN 0752823W 

90: 173oN m52333w 

39SkMN 075:l I:ZOW 

39:58:22N 075~11~53W 

41:233m 075:uJ.aw 

KkO300N 076:mW 

ll:18:MN 075:4&45W 

Uh2l:OON 0762300W 

11:33:22N 077:4l:28W 

?6:33:1ON 076:54:57W 

37:47315N moo:o6w 

37:3SSXlN 079325300W 

37340315N 07ROS:lOW 

36:46:13N 077:095!3W 

37:46.)3N 037:39:57W 

37:31:55N Ul6:48:4OW 

3732:OlN 0765O:yIW 

SkOl:45N 07855:Y)W 

366:49:48N 076:17:3OW 

k?:n:OON 08l:&%kJW 

ltl:31:3ON 081:54:37W 

l9MIJoN ams1:52w 

yMlp:ION OMk4L25W 

Fk31: ION 0775230W 

k32:UIN C6RM45W 

E244lN OBXlMOW 

Bywmklh+ Lmdmm 

MD Susqueh~naRiver Cowwiqo 

MD Susr~uebannaRiver Co-ngo 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

PA 

?A 

PA 

PA 

VA 

VA 

VA 

VA 

VA 

VA 

VA 

/A 

!/A 

{A 

uv 

clJrim River RiCWJ~ 

Cobbs Creek Phiidelphia 

Codorus Creek Spring Grow 

Del~w~rc River Torresdak 

Dcl~ware Rinr Shuylkill Jnd. 

Dcl~wrre R&r l=yslFrankslown Bra& gladder St&n 

Lake Erie Erie 

Lehigh River EasIon 

Lisle Valley Creek Paoli 

MoaongJllcIa Riir clnirtaa 

Scbuyikill River PhifJdelphiJ 

Schuylkill River Philadelphia 

SUSqIKhJnnJ N.Br. RJwm 

Squelman~ River Cdumbia 

Susquchanna River Piitstoa 

Uniw Canal Lcbanm 

Young Womens Cr. RcBlackwater Ritw Riverdale 

Jackson R&r CWillgl~ 

Jpmu River Glugm 

James River Cartemilk 

Nortoway River Sebrcll 

Pamunkcy R&r Haaovcr 

Pamunkcy River wesl P&l 

Pamunkey River West Point 

RoJnokc River Brookneal 

S.Br Elizabeth R. Norfdk 

KJIIJW~J River Nitro 

uv KJUJ~J Riir Winfield 

WV obio Rim NW. Martinssle 

WV Ohii River Wkceling 

WV Opeqwn Creek Lidnglon 

U Al~b River c3Jibacnc 

4L UbJEIJ River Moatgomery 

X 

rolNl souRcps 

N?L Other 

WC rrNc wr rrmy Sk Im4 rcnw 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

x 

X 

X 

X’ x 

X 

X 

x x 

x x 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

f 

II 

NON?OlN 

--- 

- 

-s*rPenttcb P~pcrs in Johnsonburg; rur~k, rcid miae drJirq,e 

Old PCP plam (defuud fur more tb~n 5 years); laadfti 

P.H. Gladtfelder in Spring Grove 

Coastal Eagle Point Oil Co. in NJ; Inorganic them. 

Mobil Oil in NJ; lnd.: clnxn; multiple sources; Ag.: croplands (trucking uf 

=gCtJhkS) 

Appktua Paper on lhe Juniata River (lldter Creek) 

Hammermill Paper (indirect); railyard, food processing plant 

Sled industy 

Paoli Railyard (historic PCB problems) 

Id: ino& &cm. and pest. 

SJmc w 31~. two refineries; Ind.: org. chcm. & pest.; P&P mill; 

Superfund siIc (FQ) 

Same as 2212; two relinerics: Ind.: org. chcm. & pest.; P&P mill; 

Superfund s&c (PCP) 

Superfund rite (Imy metals) 

Gladtfekkr (bkackkraft) 20 miles upslrcam cm hb~lrry 

Superfund site (heavy mel~k); acid mine drainJgc 

Pesticide ccmcern 

Union Camp Corporation in Franklin 

weJl*Jco GxporJlion 

tighl qriculturc; rural 

Westvaw (PPC); Virginia Fibers and Nckocsa Edwards (PPNC) 

Union Camp is 20 miles downstream of samplii site 

UpslrCJm from Ihe ChcJ5CpCJkC C0rporJtic-n 

chcasepc.Jkc Gxporation (upwrcam of site) 

Cbcasepcakc Corporation (dormscream olsitc) 

RUlJl 

Ind.: pcslicidcs (Monsanto); rural 

Ouakcr State Gil Rcfming; steel industries; urban runoff 

Ag.: or&r&, rural 

Alabama Riwzr Pulp Company 

Ind.: organic them. & pesl.; Pence-posl -parry, Ag.: croplands 
- 

E 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

- 

w 

# 

3360 

31-m 

2xT2 

3172 

3328 

3171 

3169 

3168 

3331 

3332 

2151 

3329 

3334 

3174 

2148 

3333 

2142 

3173 

2152 

3330 

3337 

3177 

3375 

3376 

3377 

3378 

3178 

3179 

2294 

8176 

33x 

t2!a 

5175 

3338 

310 

333s 

r0lN-r BWRCRJ __ .- 

nn olbw 

WC rmc WC Rray by 111 rum 

NONRMN 

- 

--- 

laulw4sw 6yWIy l.udu PEL-! (CdYlrh~dCUlJd*~~) 

32mSN 085rO3:43W AL clwlJboocbu COltCdOO X ~~Kr~inAL~~~oGAmtcrbucoclALridc) 

31:2!woN o8522aw AL CbodJW,JtC,lCJ R. Hcuy CO. X 

311tMllN OUXO2&lW AL CoaccubRiver E. Brcaa X Container CorpotJlim 

3 I:25:07N Ml6:26:4SW AL CmuRivcr ALGA SIJIC I X 

33:17:24N 086:21:42W AL CuocaRiver CnaJJPii X X Kimhcrly Chrk; wooded WCJ; A&: cr- and grazing fwldr 

31.QkO2N 0811:13:24W AL Cowarts Creek HoustoaCa. X 

3J:SO:lSN 0&31:46W AL InlandLkc Bbwt Co. X 

xM2:mN 087:57:48w AL MobikRiver 0urCddCr. X X X Smral chcm. & pest. plants; Hydra-powu 

m3omN ot37:M: ISW FL II Mile Creek cvl-Ill X X cb~~~pian htcmatioaJl Corp. in Carttoruncnl; rural; swampland; Ag.: 

UN 

XUlk52N 081:2!%28W FL ArncliiRivcr Fernandina Bc X I’lT Rapnicr. Inc. 

Xk2323MN OR533:24W PL Ectmf~Crcek PJOMIJ Ciiy X 

momJN mwkalw FL F-R&r Perry X X Buckeye Cellulorc, rural; swamp&d, Ag.: grazing fields 

2!kM31N 085:17:59W FL Gulf Co. Cad Sl.JOC X X h. Joe PJ,NX (imdireU) 

27zl2:lgN OlJOz47:2gW FL lakeOkcccbdue Okcccbobec X 

27:3854N -21:lOW PL Hinfiarl Vero Beach X Cdkded below dinicy strudure 

3om38N o85:*25w FL sI.AndrcwBJy Pamama City X X Soulbwc~I Fore~I lad, let (iadirai) (Slow Caatairtcr Corp.) 

293W8N 081:37:32W PL St.JobnsRiver P&IL X X X GeagiaPa&cCoqmrtiion 

3oQMloN . . m1:eaoW FL St.JobmRivcr Greu Cv. Spr X Wood trea4mcnt pht 

3&21:3cN 062.0(:s4w FL St. M~sRiir M-Y X X 

mmm lxl3:15zaIw FL W&blamo&River BlreSe X 

31:EtloN oB1:4!IzOOw GA AllamabaRivcr Jesup X X ITT R~yottiu, Inc.: swampland; Ag.: ~opl~adr 

w&.QoN oln4oslw GA ~t1Jhoocbee R. Gaincsvilk X X X X %WII dSclmvillc: heavy md~$ wood produds; 16-z chicken farms and 

orchards 

33:39:24N lRUdOSW GA Chal~rboocbce R. Au&U X X BcutBoudaaHwy92 

3332&37N oB4:W~ GA -tatiR. WLilcsburg X 

33cl6:45N @35dXtXlW GA C~JII- R. FruLlin X 

3lM).fm msQ4m GA ChJtlJ-R. DooJldaanvilk X X Grul Soubcm Pa&c Paper Company 

3455row lw3:I(MIow GA Clu4loogaRivcr cw- X 

S4z27.a llfl35RW 3A Chcst~la River JbOWZLhliC X X X Mining: gdc& send, JIMI gJvCk Ag.: orchards, dairy farms & cbiikcn 

bones 

32~Ol:2oN 083:M:XJW GA flinl Riwx L Blacksbear X Pro&r k Gamhk (Buckeye Cellulose) 

ms2.aoN 06436mw GA LakcSeminok X X X GCCJI Southern Pacific Paper Company 

m43:37N a31:329ow GA North Riwx (mm&) St. Mary~ X Gil- Paper Campmy 

9:22ZSN oBl:f6:3SW 3A S~nrub Riur A-J X X ,=dCd PJ,,C&OJd iU f%Wd9 c-i,+ h‘ik bd.: f=t. 

j2zlmoN aelm5ow 3A &andRii - X X X X F~I Howard Paper (PPC). Unioo Camp aad S~OOC conlaia~ Corp. 

@‘f’WiN-po~~ 

33zkmN ael:s6~ GA SavannabRiwx b”=‘J X X X Pm&rosa Fibax (indinxl) 

31:1gm au:45- 3A SpriqCrcek Eulrw X 

lla15N oB1:31:3SW ;A TurtkR. (mm&) S. BrunsukkR X Brunswick Paper d Pulp on he Turtk R.; mrrsbti, won&d arm; Ag.: 

grting flewi 

TABLE D-l (Cont.) 

D-l-6 
TABLE D-l (Cont.) 

-- 

El 

UC 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

IV 

FW 

0 

3183 

3339 

3182 

M56 

lAudt Laqllmh BuWdDIb+ - 

38:24:22N 082:35:52W KY BiiSdyR. cankhburg 

M:SS:JlN 089Sl5:52W KY MissiuippiRiw Wid;lilTC 

36:55:27N 086:52:47W KY MudRiver Rus.sellvilk 

38:CKMON lR5563OW KY OhioRivcr West Point 

2341 38:46BN 004:57:52W 

3181 38xJO3ON 08556:3OW 

3446 38:24:22N 082:35:52W 

3185 3O25zOON 08994f~IW 

2126 32:20:4lN 090:51:48W 

3445 30:19:32N oBB:31%XlW 

3341 30:25:2ON oBs:31:lOW 

3340 31:13:28N 089m5OW 

3435 3M.5:OON 0!91:3OzmW 

2133 32:29314N O!XMzU2W 

3184 3Z:28~N 090:493ooW 

3344 34:U:MN 078:10:30W 

2139 35:4OAT2N 093M:DW 

3165 34:43:5ON 079339:24W 

3345 35: 15:06N 082:40:45W 

3164 35:56145N 079z19:MW 

3342 34330N 078:MzCQW 

3167 35:ZO:35N 07850:20W 

3166 35:08mN 0833&15W 

2138 35:15:29N O77~35mW 

3395 35:ll:MN 077M:4SW 

3343 35132tO5N 082:54:4OW 

3346 35:SI:55N U76:45:4OW 

3385 35:59:25N 081:31:32W 

3347 34:42:3ON @30~5l:Y)W 

3186 32:IS:SON (na.SJ:lOW 

3348 33:2l:UN ml8:WW 

3187 32:29:46N 080:31:33W 

3349 33:5ldBN tXKk37:32W 

2301 35:29z45N llKkIp.58W 

3189 35:5%37N o&Q:58:18W 

2298 35:16:3lN 06858:36W 

3350 35:PXBN oBI:48:13W 

2297 36:0056N 083z4954W 

KY Ohio River Markland 

KY OhioRivu WcsIpoinl 

KY BiiSandyR. Catkttsburg 

MS BernardBayuu Gulrpofl 

MS Bii Black River Botina 

MS Chnon Effluent Pascagoulr 

MS Escatawpa River Moss PoinI 

MS Leaf River New Augusta 

MS Mississippi River NM&Z 

MS YaumRircr Redwood 

MS YazooRivcr Redwuud 

NC Cape Fear R&r RkgChvood 

NC CaIIaloochec Creek Cattaloocbec 

NC DeepRiver Ramscur Dam 

NC French Broad River Piiah For& 

NC Haw River Spupahaw 

NC Lumber Rivw Lumherlon 

NC McdliiPund Morrisvilk 

NC Nantbalia River Macon co. 

NC NcuscRiver KblSlOO 

NC Neusc River New Bern 

NC PigumRivcr a* 

NC Roanokc River Plymouth 

VC Yadkin River Patterson 

SC C8Iawbr Riir Carawba 

SC Charkston Harbor Charlesron 

SC Smupi~ River Gewgclom 

PC St. Hckna Suund 

EC WaIereeRiwr EasIorcr 

I-N BuffaluRivcr Flalwoods 

I-N FI. Loudon Rcs. 

M Hat&c River Bolivar 

rN HiwasceRiKr IMhoua 

M Hols~onRivcr Krmlviuc 

POINT SOURC68 

NrL O(btr 

‘rc ?rNC W Rfq Sk Id Knw 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

(C~hrk~drhru9l@~*) 

Ashland Oil Inc.; Ind.: &em,. iron l ud s&xl; cual minii limber 

Westvaa Corporalion; Ag.: croplands 

Ind.: melal pla~iq rendering planI; Ag.: croplands 

Same as 3181; lnd.: c&m. dr pest.. rcliwq Ag.: crops; Superfund site 

(PCB’S; sotvcnls; dioxias & kraN) 

Williieuc Industries; multiple sources; rural 

Same as 20%; Ind.: chcm. & pest.. refinery. Ag.: crops; Superfund tile 

(PCB’s; solvents; diotins & furans) 

Ashland Oil rcliocry, crul mioing 

lad.: chcm.; woud trcaImcnt; (gas recovery) refinery, rural; Superfund site 

(SolvenIs) 

Ag.: soyhans and cn~ton 

Chcnon reliocry, InIcrnalional Paper; shipyard; fertilizer company 

lntemalional Paper Company 

Leaf River Forcs( Produds 

International Paper Company 

Same as 3184; Ind.: paper; fertilizzr plant 

Same as 213% lad.: paper; fcrtiliir plan1 

Federal Paper Buard; rurni, swampland; wooded area; Ag.: croplands 

Champion Paper (PPC-indircd source); wooded area 

Ecusta (diic mill using chlorine); rural; wooded area; Ag.: croplands 

lad.: tcx~&q rural; &: croplands 

Alpha Cellulusc (sullile mill using chlorine) 

Koppers Company (wood Ireat.); Superfund tile - wuod IrcaI. (PCP) 

Weyerhaeuser Company 

WcycrhaclKu company 

Champion In~crnalional in Canlon; rur&, wooded ueq Ag.: cruplands 

WcFrhacuscr Company on Welch Creek rural; wuodcd area; Ag.: 

croplands 

Se&d Air Corporation (maker absorban paper for meal Irays) 

Bowatcr Carolitu; rural; wwrkd area; Ag.: cropbds 

Wes~vau, Paper and Pulp; Amoco chemical plant 

lntcmbmal Paper Gmpany; rural; waled UU; Ag.: uoplaods 

Union Camp CorpomIion; rurrl; wooded area; A&: r%+d 

Ind.: aluminum 

Bowatcr South Paper Company, rural; woo&d area; Ag.; croplands 

Industry metals 
VJ ry 3401 2379

V 2383 

V 3113 

V 2380 

V 3114 

v ’ 3115 

V 3117 

V 2059 

V 33% 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

2of& 38:075ON 087:56:2OW 

2057 38:3&45N 087:17:3oW 

3119 42:33:ooN 08554:oOW 

3118 45:S&OON 087MtX3W 

1994 43:03:001rl 083:48:45w 

3120 42:393oON 082:lo:CQW 

3122 45:47:oON oB7:59aW 

199% 43:15:05N 084:14:55W 

3148 43:15:05N 084:14:55W 

2432 43: 19:5-/N 0&08:42W 

2410 42:16:4SN IX3.07:ZOW 

2431 46:29:45N 084:22:25W 

243U 46:34:3ON 085:15:IOW 

2435 47:55:23N 089308:42W 

2387 44:16:08N 093:Zl~SW 

2437 44:41:33N 093:38:35W 

3112 45:58:17N 094:ZZMW 

3t25 44:33:34# 092:25:47W 

2785 48:36:29N 093:24:13W 

1001 48:35:29N 092:53:34W 

2416 41:29:50N 081:42:lOW 

2394 39:33:44N 084:lS:IYW 

247Y 39:15:53N O84:4o:u)W 

~palllde -Me 

36:33:02N 082:35~W 

35:OS:lSN 090:05:WW 

35:03:54N 085:20:28W 

36:OI:ZON 083:lZ.oOW 

35:56:24N 083:10:52W 

35:S015N 0%4*13W 

35:03:54N 086: 16:39W 

37:37:31 N 089325:42W 

41:3%47N 088Sb%SVW 

41:52:13N 088:18:3lW 

4l:lP4ON 088:4S:lOW 

3*43:Ix%J WI:31 ro4w 

38:32:3ON 09Ozl5~W 

42:21 :lON 087:49:4OW 

4l:37:lON 087:29:15W 

4l:37:lON 087:29:15w 

IN Holslon R.. S. Fork 

TN Mississippi bver 

TN Nkkajack Reservdr 

TN Pigeon River 

IN PigeonRiver 

TN Tennesec River 

TN Ten- River 

IL Big Muddy River 

IL Des Rams River 

IL Fox River 

IL Illinois River 

IL Mississippi River 

IL Monsanto Bffluenc 

IL Lake Michigm 

IN Indiana Harbor Can. 

IN Itiana Harbor Can. 

IN Wabash River 

IN White River 

Ml AllcganLake 

MI Eacmabr River 

Ml FlinIRiver 

MI KahmamoRiwr 

Ml McnomimeRiwr 

MI MuskegonLake 

Ml MuskcgonlAe 

Ml Muskegon River 

Ml RwgeRiver 

MI St Ma~ys River 

Ml Tahquamecon R. 

Ml WashingtonC~ck 

MN CannonMe 

MN MiMeslMa River 

MN Missmi~t River 

MN Mississippi River 

MN Rainy River 

MN Ramy Riwx 

DH Cuyahnga River 

OH Gnx Miami Rwrr 

OH Great Miami River 

Wtspm 

Nonconnah Cr. 

Newporl 

Newpon 

Knorvdk 

Hardin co. 

Grand Tower 

bwn 

Geoeva 

M&U@ 

Ww 

l3.s St. Louis 

WlUlkCgan 

Ea.uchicago 

East Chicago 

New Hamr~ny 

Fkletshurg 

Allegan 

nushiig 

Saugaluck 

Quinnesec 

Musl;egon 

Muskegon 

Bridgton 

River Roufp 

Sauli St. Mane 

Pamdisc 

hle Royale 

FairbaUll 

Jordan 

Liuk Falls 

Red Wing 

Intern’1 Falls 

hem’1 Falls 

Ckveland 

Franklin 

NW. Baltmuw 

I 

* 

X 

X 

X 

X 

X 

X 

X 

X 

x I 

rPc PPNC WP urny sic Im4 fYnw -. 

X 

X 

X 

X 

X 

X 

X 

x x 

x x 

X 

X 

X 

X 

X 

X 

X 

X X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

dx 

::!:: 

G ! 

X 

x x 

x x 

X 

x x 

XIX 

X 

X 

X 

x I x 

x I 

I 

X 

x I 

X 

x 1 :: 

X 

x 1 x 

,” I 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

( Mead Corporation (ChIoMe Dioxide process I 

Map-o. Exxon. Umun wtinenes; cen*lnt f.x~ory: soybean pmcessIng 

lnd., them.; coke; endenng; r;ulyar&; landlill 

Champon InlemaImmal In Nonh Carulrna 

Champon ImemalIonal m Nor01 Camhna 

Tennesee River Pulp and Paper In Counce. 7?+ 

Id.; orgaaruc &em. % pest.; Refimencs (downsueam); sti: melnerawr 

lnd.; them. & pest.; Uruon od. Texaco. Mohd; Ammunition piam 

Cekxex Corporauon (deinkmg) 

SIX chcrntcal/pharmaceultcal planrr (parad~hlorcbenx?x) 

(@en lake sample; Superfund sne (PCB) a1 Waukrgan Harbor 

Same as 33%; Amoco 011; Ind.. prunarily steel; wast~a~r; Supc~fund >II~ 

(PCB) 

Same as 2059; Amoco Oil; Ind.: prunanly SIC& wa.sIrwacer; Suprtfuru.l SW 

PCB) 

Ind.: clam. & pst.; coal InmIng; (SW a1 1he IIloulh ol the Wabash R.) 

Hydra-power. coal mming 

Hiskncal PCB contaminaton from paper dcmking; Superfund site (PCB) 

Mead Cotpotanon (historical PCB conIanunaIIon) 

Auromobik manufacmring (heavy meuls and uds) 

Histmcal PCB comaminauon sne LS &wns~~um of Kalamazoo 

Champion InIernauonal CorpordliolI 

Scot1 Paper (mdirecl); Power t them planI; Ag.: oxh.: same as 3148. 

Superhmd siIe (FCB) 

.Scou Paper (indirect); Power & clam plaru. Ag.. on-h.; - as 1998; 

Superfund silt (FCB) 

Far upsueam of hkachkrdf1 (Scoa Pqxr Company) 

inc.: heavy steel; chcm.; auiomobile (PCB’s in ellluem) 

St Mary’s Paper; Algonra Steel; dndgmg 

Canadian Bleach Krdn P&P mill abw~ 30 mllcr upwmd In Thunder Bay, 

tit. 

Hcnnepin Paper 

Ashland OUKoch ReAnIng. urban ruIu)lt hI\Iucal PCB comammauon 

Boise Cascade on bo1h sides of Ihe river 

Sne IS ahovc lhe dam Boise Cara& oulfall IS below dam. 

Ind cluzm.; 0Il. 

Appldon Papers and MlamI Papers (timkIng). Ind: melals and oIhhus 

Sorg P&P mdl (demkmg). Pmctu a1u.l Gamble. Ag. nmoff; Supcr(und UIC 

-.- --___- -. - ~__. --. _ .__. ___-.. _-. ...~___- ~... -- - -___ -..-. 

D-I-8 
- 

3 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

V 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

vl 

VI 

vl 

VI 

VI 

VI 

VI 

ldll& ia@lm& ~ 

3924:4ON 084914W 

3132 39 17:36N @32:55:4gW 

3135 44:4!UYN 0913038W 

3136 4924.m 091:13:1gW 

3137 45:5s:uIN 0!%264Mr 

2429 l4:273N oBB.~:XlW 

3138 44:16:1oN aB8:n:l8W 

3140 t4:13:24N llB8:2734W 

3143 l4M:43N aee:3l&klW 

3144 l3332z17N Ilg927%w 

2422 l63621N 090:52:38W 

3134 MOl:58N tXl8LBz45W 

3141 13:03:26N oL)7:53:54W 

2427 lSm:16N lk37:44:5OW 

3142 13:43:51N 067:47.01W 

3110 l4:5&oON 092AHOW 

2397 u:37:27N 089z25:14w 

2608 14: 16.9DN 8BsU3.~W 

3106 l4:16:oON Ct89z53zIX1W 

3lIn l5:01:2oN 0893909w 

3108 l5:11%31N 889z41koDW 

3109 u:M:5m awk45w 

3145 I5:26: Im 889:43:56W 

3146 u:525m 08mww 

20.?3 l5:2OSN m:17:54W 

3060 !4:a6:41N 1XQti38W 

3062 l4z109N 091:43:56W 

3061 13: lo: l8N 092:393oOW 

3078 u:M:39N 092:07:28w 

3443 w- 091:31aw 

Ml5 L3:3397N lBl:lIl5W 

2018 is:r):43N 8QlL45W 

NJ73 i5:5633N W2%T7s35W 

Ml6 rx43m w4m%lw 

3452 334: 15N OY4:OfxMW 

3077 13573m 094m49w 

Ml7 13:14:32N 0!?3358W 

3a!ln uk53MN 09325zOOW 

3x33 12:4tkIklN 091:43zIKlW 

Lralln 

OH Hamil~ooCanal Htimiltolr 

OH SciotoRivcr ChilliCOlhC 

WI Chippewa River Eau Claire 

WI Fladxau R&x E. l,a&dlb 

WI Fbmbeau River Park Falls 

WI FoxRivcr DcPere Dam 

WI FoxRiver Appklon 

WI FoxRiver Lk Bu~tcDMort 

WI FoxRivcr oshkosb 

WI Fox River, upper PO-IF 

WI LakeSuperior Asbland 

WI Mauit-Riwr Cbilton 

WI MilwaukccRivcr Milwaukee 

WI Pcsbtigo R. Harbor Pcsbtigo 

WI Sb&oyganRiru Kobbx 

WI St CroixRivcr Hudson 

WI Wii R/Boom LakcRbinela&r 

WI Wismr&R&r 

WI W&River 

WI Wd River 

WI WiscocuioRivcr 

Wl W&River 

WI w do RiHr 

WI WtiRivcr 

AR ArkansasRiver 

AR ArkansasRiver 

&R ArkaosasRiver 

AR Bayou DcLoutrc 

AR BayouMc~o 

AR Bayou MCIO 

hR MimimippiRivcr 

u. PenId P 

u. Pcolcuwcll F 

Brokaw 

Memill 

wallsau 

Mohawskio 

R&&%ld 

ho Bureo 

Lir~lc Rock 

Pine Bluff 

El Dorado 

Jacksontillc 

Reydcll 

Ark- City 

bll N. SylunorcCreek FiRySii 

kR N.SylamoreCreek FiSii 

hR RdRhw lndu 

hR RcdRiir llukx 

hR Rolling Fork Riir De Gueco 

hR Sulphur Riir TCXa&uU 

LA AnacocoBayou lkridder 

IA BayouBooncldce OakRie 

TABLE D-l (Cont.) 

POINT SOURCES 

-~. -__ 

NH. OUvr 

Id lwlw 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

- 

NONMINI 

3 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

- 

Amluud Sk Durlpum 

(F.rollks lo lbc NWly or llw umpury dk) 

Canal off 0. Miami R.; Appleton Paper; Aviation plain; steel; 

hydropower; Superfund site 

Mead Corporation on Paint Creek; lnd.: inorg. chcm. & pest; Supcrfund 

sill? 

Pope sod Talhot (dcinking) 

Pope and Tahol (&inking) 

Flamhcau Paper; Ag.: croplands and grazing Iiclds 

Fort Howard, James Riwr, Green Bay Pkg., Nicolet Paper. Champion 

Kerwin Paper Company (dcinking), Gladtfcldrr. WI Tissue, Kimberly Clark 

Gladtfeldcr, WI Tiiuc Mills, Kcrwin Paper (historical PCB onlamioa1ion) 

Pondcrosa (deinking) 

Historical PCB contamioalion 

James River-Die Northern (d&king); rural 

Incinerator; HZ0 softener plant; ~g.: croplands 

Ind.: metals (biitorical PCB contamination); 308400 Industrial discharges 

Badger Paper Mills, (indirect) 

Superfund site (historical PCB contamination) 

An&moo Windows, wood Ircatmeol plant 

Upslrcam of popcr mills 

Nekoosa, Fort Edwards, Consolidated Krah; Vulcan mat. (rubber & 

pIa&); same as 3106 

Nekoou,fkrt Edwards, Consoliiatcd Krah; Vulcan mal. (rubber & 

plastiic); same as 2608 

Wmtsau Paper (sulfile mill) 

Ward Paper (d&king) 

Wood lrcalmenl plant silt is helwccn paper mills. 

Rbiiclandcr Paper Company 

Weycrbacuscr, hall dozen small mills; Ag.: croplands 

International Paper Company, woo&d area; Ag.: croplands 

Lion Oil Company 

Superfund site (dionins); rural; woo&d area 

Downstream about 30 miles of Ihc Jacksonville site (3878) 

Potlatch Corporatioq Ag.: croplands 

SUtUaS307-3 

SamcasZ-118 

Nckoasa Edwards Paper Company 

Nckoosa Paper; lime and gravel mints; Ag.: UOP and grazing lands 

Wood treatment plan~ on Bear Creek 

International Paper Company in Texas 

B&c Southern Co. (Boise C-de); rural; Ag : croplrnd 

HCB use in agriculture 

D-1-9 
TA6I.E D-l (Cont.) 

- 

Er 

RI 

i 

V 

VI 

VI 

VI 

V! 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

VI 

vl 

VI 

VI 

VII 

vi! 

VII 

VII 

- 

r-Ir3rJ lIlhWdtb+ - 

30% 3&12z 093:17.-w LA BayouD’lDdc SdfiU 

3442 30323tiN 09&Z?mW LA BsyoulAorehe NOCu, 

3353 32z31MN 09154rOOW LA Baycm~ourebc Bastrop 

3063 306m o!n:2otoow LA -uRivcr h4ms Lake 

3092 32S5fON O!Z?:47ilOW IA DogdcmonaRiver Ho& 

3352 3223zfXlN tEJ1:51dXJW LA Lake lrwio start 

3064 3OCMYlN lBO92zOOW IA Lake Powtebartrian NtuOrkans 

3OF2 32:48:t%X’t 091: I I :oOW LA Labc Providcnee 

2532 m45:3oN 091:23345W IA MississippiRives 9. Praneisvilk 

3065 3027S3N 091;Wm u Mississippi&r Baton Rouge 

3066 3OStM3N IL’lLllM)W LA Misais+iRivcr Uoion 

3418 XE%~~JN 091:17MW LA MiuiuippiRkr itachy 

3416 33%XtfION lH2SMlOW LA OuacbbaRivu Slcrtiagton 

y)80 3297StON a97aW LA OuaebitaRiwx Mollrol? 

2544 3WW23N m21:42W LA TangipabocRiir Robert 

3087 3235.MN 09Mti.SHJW IA WbmnBrakc swartz 

3425 32:33~XlN 091:5HNJW IA WhamBrake SWUtX 

3074 35:463!3N 105:3!Z7W NM Riohfora Tcrrcro 

3105 35:13:42N 09&31:35W OK Fan CnbbRucrvuir Foli cobh 

3090 36.1M.dXlN 095z16;ooW OK Fan GitsoaRca. Pyrer Creek 

3~73 36:52m 09656SHlW OK Kaw Rd 

2027 3438:lEN 094:M:45W OK KiamkbiRivcr Big Cedar 

3076 33:57aN 094:35&lOW OK LittkRiir Goodwater 

3041 3356M)N 095.%‘aW OK RcdRiver 

2026 34:14xT3N 0%5832W OK WashiiRiver Durmmd 

3089 35:41mwll OP5:ll:tMW OK WebbcrsFaIls Mdogce 

3CdM 26:11:42N 097%06W TX Anoyo Cdorado Ha&lgcn 

3085 7&585!3N 095:2334lW TX Brazes Rkr Freeporf 

3t%fI 2!Jz4tk48N 094:585OW TX HousIorr SbipCbnl Morgan Point 

3069 27:5l:m O97:%324lW TX Inter Hubor Corpus Cbridi 

3081 31:25:5LIN o(w:U:%W TX L*lkcSam Rayburn L&in 

2280 2&57:35N 0%:41:13W TX LvaeaRiwr Edna 

3075 28.-N 096:52MW TX McaquitcBay 

)093 ’ 31.OIUON 091:48:39W TX Necba Rivu DiboU 

3OXl !2!&5WJN 093:54dXlW TX NecbaRii(r&I) Port Mbur 

3072 (31:05.aN 10596m TX RioGrudcR&r EIPm 

a71 291&15N 098:21:43W TX SanAnto&oRiwx &a~rf 

D2l3 3@.55:25N O98:02:12W TX So. Fc,rkR&ytJr, Br&p 

3035 4203:54N 091:47:48W IA Cedar River P&kl 

3037 41:u1:s7N 093:4O:oBW IA DcsMoincsRivcr Des Mu&s 

3038 41:33z02N m31:29W IA DcsMoinesRiur Des Moinu 

4J34 41:34:53N 09Lt23:23W IA Mi&sippiRivcr Le chlirc 

X 

X 

X 

X 

X 

X 

X 

X 

.~ 

POINT sOUEClL¶ 

-- - 

NFL O&w 

WC WNC wr Phy ill* Id Porn 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

x 

X 

X X 

X X 

X 

X 

X X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

I I 

i 

(rwwr~~r*wlr~lbImm~~) 

Citgo Pwokum Corporation; Ind.: &em. 

Shell aad Norco Rcliocric~ Sbcll cbcmiul plant 

IntcmatiooaI Paper Company, rurat 

Conom, lat.; Ind.: cbem. 

Ahow. Bayou LaFourche. This dammed water feeds Wham Brake. 

HCB use in agriculture 

crown wlcrhaeh 

Georgia Pacific Corporation. Crown Z&crbaeh; two rcliierics 

lad.: mukipk sourax; Ag.: cropland and gazing 

Georgia Pacific and James Madison Paper; rural; wooded arca 

Gcorgis Pacific and International Paper; rural, wooded aru 

Georgia Pacific in Arkansas; Ag.: uop and graziog lands 

same as 3425; International Paper Co. (diibargcs IO 8. LaFourche) 

Same as Mgl, lotcrnatiourl Paper Co. (disebargcs to 8. LaFourebe) 

~g.: croplands, goIfeoursc near the site 

RobcU Tii MiIls 

Vulcan PIan in Wichita, Kansas (chcmieal proecssing plant) 

Hwily woode4l area; Ag.: uttk 

Wood treatment: Thompson Lumber, I loffman Preserver, Nixon Bras 

Prcscrvx~ 

Wc~rhacuscr Company 

Ken McGee Rcfmiog Cnrporaticm, Total Pctrokum, Inc. 

Fort Howard Paper Company 

HCB use 

At Dow Chemical outfall 

Champion International and Simpson Paper; four rctinerics; Ag.; croplands 

Four refincricr 

Champion International Corporation on the Angclina River 

rcmpk-Eaueq Inc. in DihoU and &w&n Chemical (ruin) 

rempk-&uy lnc in SiIshcc, TX; hro rctinerieq Ind.: ebcm. & pest. 

Chevron US& lac, EI Paso RcLicq~ Cunpany 

HowclI Hydrourlmos 

Background site 

&hoot 50 miles downstream of Waterloo 

Upstream about IO miks from a PGTW 

Below POTW (I~relrcatmcnl plant) 

Ilpstrcam 01 luck and dam 81 Dawnport (alwvc dam) 
u)36S7N 0%:38:44W IA NishddnaRivu Hamburg 

1036dl7N 095338344W IA NiiRixr Hutbug 

373234N 097:16:WW KS ArkansuRiwr 

37:32z3SN 097:16:WW KS ArkmsasRii z 

36S2:3ON 09OSV:3oW MO IMe River Ditch81 Horwsvilk 

M.ltWON ORIO7:3OW MO l&k Riir Ditch 81 Horncravilk 

3934236N 091:21.~W MO MiiRivcr HUlllU 

38:52:33N @Xl.lO%W MO MiiRii wcsl Allon 

37:17&N oBp30.56W MO MiippiRivcr chpc Giradcal 

39zO7:52N -oW:zI:S8W MO Missouri Rive Kansas ciiy 

39311:14N Om5s3:4SW MO MisaowiRivu LCXiOglOU 

-44z32N 09451:36W MO MissouriRiir SI Joseph 

39z11:14N 09353345W MO MiiiRiwr Lexiog~m 

37:59z15N 093#8:45W MO OsagcRiir R41:15:32N 095:55:XJW NE MiiRivcr OIMIM 

41:08:18N 095zS2:4oW NE MisscnuiRi~r ktkvu 

41:45:42N 1@3:25.~W NE Nor~bPlatteRivcr Mcgrew 

405948N 0%91:18W NE PlaftcRivu L4Nkdk 

383OON 106zOlzfNlW CO ArbnsasRinv Salida 

3914811ON 10457:3OW CG South Pla~tcRii Dcnvcr 

~1O3ON 104591XJW M St. Vriao Riw.r Loqmont 

ti1OzOON 112:46%W MT CbrkFbrkRivcr warmsp&gs 

47RlMN IlJ:21:PW MT Cl&Fork R&r Huson 

4S:U:JSN lIlMzO4W MT East GalluinRiver Bosemao 

47:56:14N 114:llMW MT GooseBay lakside 

4S:47:48N 108:28:12W MT Yclbws~oueRiwr Biings 

47:35:2SN 103~15~ ND LittkMissouri R. Wdord ciiy 

t9~WJcooN 097:13:45W ND RcdRiir PU&i&la 

499O:ooN 097:13:4sw ND Red River Pembina 

42ze42.N 096:33:4sW SD Big Sioux River Ah00 

#2:&45N 096:33:1SW SD BiiSious River Akron 

44.9OA9N 103:49:48W SD CwkCretk Hill City 

UI45zlON 111:55:15W UT JordaaRii SakLakccity 

41:m4ON 10535:4SW WY LaramicRjwx Laramic 

42:34:27N lfl6z41:3lW WY NorthPlatte River Aluwa 

33M:CMJN 113zB2zzW AZ GilaRiver Gila Bend 

33:12zOON 115:37~W CA AlamoRiver Calipatrir 

36:41:MN 121:44.aW CA BlancoDrain Sk 

33:46:CMlN 118:oLI.&IW CA Colorado Lagoon Lag Beach 

TABLE D-l (Cont.) 

row? souncm 

Ntl. O&r 

WC rruc m aby tik Imd Nnw 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

x x 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

YONPOWl’ 

--D--w- 

(F*hIL~4&b8U9IpiI~hlk) 

1od.z chcm. and pest.; metaL; bydro-powr; uax as 3042-oppwi1c sides of 

riwr 

SynCprW.36 

Sanuas2190 

Same as 3039. Below Wiihila 

same as 2194. Below Wichita 

Same as 3040. Rice growing region 

Same as 2201. Rice growing region; heavy pesticide use 

Fi co&ted near downtow arca. 

Ind.: c&n. ; bcsvy metals; heavy shipping lraflic 

Colleacd at POTW outfall. Prwtor & Gambk paper productr, Ag 

CWfhdS 

Samras3046 

same as 2199 

Ag.: aoptands 

Ind.: cbcm. and pest.; metals; hydra power; same as 21~1 - oppusitc sides 

d river 

Defunct wood IrcaImenl plant 

Slonc Coolaina Corporation 

Sugar bed procesing plant; croplands; Same as 311 I 

Sugar beet pressing pbnl; cwplmds; Same as 2lfl0 

same as 3199 

same as 2109 

led.: pc&ib, Superfund site (chlorobc~~~~) 

Railrood tic treating pia (ddumd) 

D-l-11 
TABLE D-l {Cont.) 

- 

El 

& 

In 

In 

IX 

IX 

IX 

1X 

IX 

1X 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

IX 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

+m& 

1 Lllludc tmquude 

3273 41:45%lN 124:llzOBW 

32f16 3X47: I5N II& 17:33W 

3271 4034:00N 123:ll:oOW 

3272 37:55:tDN 122z21:oOW 

3275 4054:MN 124:OO:MlW 

3276 4Oz52:M)N 124:oo:M)W 

3289 36:48roON 121:46:oOW 

3451 34:01:45N 118:40:45W 

3354 37:57.8ON 121:18:tDW 

32&3 33:06:00N 115:48:oOW 

3355 37:56zoON 121:19:M)W 

3290 37:57:M1N 121:20:Mw 

3274 41:55:00N lWO?OOW 

3357 38:05:oON 121:44:oOW 

32o7 40:27:00N 1u:ll:tDW 

3270 40:09:00N 122:ll:tXlW 

3287 33:46:tXtN 118%%XlW 

2748 34:24:00N 119:3O:oOW 

3281 34:2O:M)N 119:04:cOW 

3264 335427N ll8:31:28W 

3450 3355:MlN 118:28ztMW 

3269 3?43xmN 121.m:00w 

3278 39:24:00N 123:06:tXlW 

2037 19:46315N US:O5:33W 

3261 21:18:00N 157:59:oOW 

3262 223430N 159:22:3OW 

2776 35:4O:tDN 114:4tItDW 

3238 605830N 149327t35W 

3241 61:l3:20N 149:51:21W 

3246 57303aN 133:14:tXtW 

2070 61:32:42N 151:30:45W 

3244 5&41xXIN 134zO3:oOW 

3245 5523:45N 131:44%lW 

3252 43:48:29N 117:00:15W 

3258 47:%05N 116:43:15W 

3249 47333.flN llCZZ.MW 

3158 42:37:25N 114:31:58W 

1478 43:OOC@N 1151296W 

5256 46:25:15N 11792MW 

1248 47: 19:OSN 116:33:35W 

5X13 45337:19N l22:45:2OW 

Sk* WDklbdy LuMwl 

CA ElkCreek Crcsccnt City 

CA Harbor Park Lake Harbor City 

CA Hayfork Creek Hayfork 

CA Lauritzcn Canal Richmond 

CA MadRiver Arcata 

CA Mad River Slough Arc&a 

CA Moss Landiag Dm. Moss Landing 

CA Mouth of Malibu Cr. Malibu 

CA New Mormon Sigh Stockton 

CA NewRiver Westmorclanc 

CA Old Mormon Slough Stockton 

CA Port of Stockton Stockton 

CA Rowdy Creek Smith River 

CA Sacramento Delta Antioch 

CA Sacramento River Anderson 

CA Sacramento River Red Bluff 

CA San Gabriel River Long Beach 

CA Santa Clara River Santa Paula 

CA Santa Clara River Santa Paula 

CA Santa Monica Bay Los Angeles 

CA Sbort Bank (Pac. 0.) Los Angclcs 

CA Stanislaus River Ripon 

CA Upper Eel River Potter Valley 

HI Honolii Stream HiJo 

HI PearlHarbor Middle Loch 

HI Waitua Paekkaa St. Kauai 

NV Colorado River Blw Hoover D 

AK Bird Creek Bird 

4K Ship Creek Anchorage 

4K Silver Bay Sitka 

9K Susitna River Susitna 

4K Vanderbilt Creek Juneau 

AK WardCove Ketchikan 

ID BoiscRivcr Parma 

10 Coutr d’Almtc Lake Cocur d’Aknc 

ID Cocttr d’Aktu R&r Coeur d’~knc 

D RockCrcck TsvinFalk 

D Snake River Kings HiB 

D Snake River LWi.510ll 

D St. Joe River St. Marie 

JR Columbia River Portland 

X 

X 

X 

X 

X 

X 

K 

X 

POINT SOURCCES 

NIL i%icr 

PPC ?PNC WP Rfmy SIta 194 mnw 

X 

X 

X 

X 

X 

X 

X 

X 

x 

X 

X 

X 

X 

VON?OlN T 

- 

rl 

f 

McNamara & Pecpe (historical PCP site) 

Multiple souras 

Sierra Pacific (historical PCP site) 

United Hcckathorn: pesticide packaging plant in 60’s (PCB’s, DDT. Pb) 

MoWa-Arcata 

Sierra Pacific 

Multiple sources 

POTS: Tapia Crak; grazing land (horses) 

McCormick and Baxter (wood preaemrs); Superfund site (solvents) 

Mulripk soura.s (HCB use) 

McCormick & Baxter (wood prcservcrs); Ag: croplands & arch.; 

Superfund site (solveots) 

McCormick & Baxter (wood prcscrvers); Superfund site (solvcots) 

Arc&a Lumber Company (ltistori~ PCP site) 

Gaylord Container Corp.; lnd.: them.; rcBncry; power plant; Ag.: 

orchards and croplands 

Simpson Paper Company; wooded arca 

Diamond lntcmational (recycled paper); Ag.: croplands and grazing 

Simpson Paper Company, PaciBc Coast Paper 

same as 3281 

Same as 2748 

El Segundo Refinery, Hyperion POTW outfall; multiple sources 

POTS: Hyperion outfall 

Multiple sources 

Louisiana Pacif* (hitorical PCP site) 

Ag.: sugar cane growing (pesticides) 

Combustion sourccq Superfund site (solvents) 

Agent Oraogc test site (not a designated superfund site) 

Salvage yard with runoff of PCB; Superbtnd site; landfill 

Alaska Pulp Company 

Louisiaoa Pacifii Corp. (sulfite mitt); Kctchikan Pulp and Paper 

Ind.: sitvcr miuing 

M&g 

Potlatcb Corporation 

D-1-12 
a 

AT 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

- 

w 

t - 

3216 

3218 

3219 

La- l.mdlI& Skk Wakrbndy Locadlm 

455 1:53N 122:47:39W OR C~umbia River St Helens 

46:09:2lN 123:24:oOW OR Columbia River WaUlla 

45:39:lON 12056zCXIW OR Columbia River D&S 

3201 45:36%N 122:43:57W OR Columbia Slough Portland 

3208 

3212 

44933ON 116:57fNW 

43:46159N 117:03309W 

45:26333N 123:14.fVW 

45:23:4ON 122:45:3OW 

45:39:53N 122:44:39W 

44:23:16N 123:14~03W 

45:17:17N 122:58:03W 

45:17:38N 122:46308W 

47:23:3ON 122:37:38W 

OR Malheur River OntUlO 

OR OwyheeRiver owyh= 

OR Tualatin River Cheny Gmve 

OR Tuafatin River cod; Park 

OR Wiflameue River Porthlnd 

OR Willameue River Haflsey 

OR Willamcue River Newburgh RxrI 

OR Willameue River Wilsonville 

WA Burley Lagoon FQdY 

WA Columbia R. (lower) Estuary 

WA Columbia River LOllgVkW 

WA Columbia River Tri Cities 

WA Columbia River Camas 

WA Columbia Rivet woody Island 

WA Columbia River Kalama 

WA Cohuubla River Dee.llshnd 

WA Commencement Bay Tacoma 

3215 

3217 

3213 

3437 

3226 

3438 46:15:36N 123:57:57w 

3220 463075ON 122:59:27w 

3221 46:06:oON 118:55:oOW 

3222 45:34:08N 122:24:42W 

3439 t6:15:@SN 123:33:32W 

3440 06:00:33N 122:51,04W 

3441 $5:58:05N 122:49:19W 

3163 47:16312N 122:25:5OW 

3191 46c58:oON 123:53zOOW 

3192 M57:13N 123:Sl:l5W 

3162 4731795N 122:24:28W 

3227 17:14:2ON 123:02:4OW 

3295 48:OS:oON 123:24:45W 

3294 )8:06:3ON 122:45:3OW 

2247 17: 12:52N 122:20:25W 

2246 17:49:52N 122:02:5CJW 

3223 18:01:52N 122:13.tKtW 

3224 #8:45:01N 122:29:02W 

3231 M:22:42N 119:2%29W 

3230 t7:ll:ION 120:02:3OW 

WA GmysHatbor Hoquiam 

WA GraysHz&or 

WA Hykbos Waterway z 

WA OaklandBay Shelton 

WA Port Angels Harbor Porn Angeles 

WA Por~Towusend Pon Townsend 

WA PuyaflupRiver PuYaffUP 

WA Snohomish MOIUOC 

WA Steamboat Slough Even% 

WA Whatcorn Waterway Bellingham 

WA YakimaRlver 

WA Yakima River Ck Elum 

!w-!L 

X 

X 

X 

TABLE D-l (Cont.) 

Ponvr solJRcEs 

N?L OUwr 

PPC PIWC W Rlmy Slk Imd FOTW 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

x x 

X 

X 

X 

X 

NONFOM 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

X 

T 

T 

rl 

MdAamul sue Dsrrlplbm 

(Frllth k Ow VI&BY of be nmplhg site) 

Boise Cascade (indirec1) 

lames River Corporation in Clatskanie 

Hydropower (PCB’s generated); food pmcessmg plant; Ag.: arch. & 

cmphunls 

Five paper mills using Cl bleach. two paper mills not using Cl bleach; 

shipyard 

Minor industries; Ag.: croplands 

fnd.: them.; smelters; shipyards; timber 

Hallscy Pulp Company (Pope and Taltxn); Ag.: cmplands 

D&king piam; other pulp mills upstrcem; Ag.: cnrplands 

Below uansformer and scrap melal salvage yard; below Superfund site 

W”.X) 

Weyemaeuser and Longview Fiber Company; Ag.: croplands & grazing 

fields 

Boise Cascade; Ag.: cmplands & grazing fields 

Crown Zelkrbach (James River Corporation) 

Boise Cascade and Weyerhaueser, Longview Fiber downstream 

Boise Cascade and Weyerhaueser, Longview Fiber downslmam 

Boise Cascade and Weyethaueser, Longview Fiber downstream 

Simpson Tacoma Kraft; US Oil and Refining; heavily industrialized; 

Superfund site (Commencement Bay) 

ITT Rayonier, inc. (sulfite mill, nonchlorine) 

Weyemaeuser Company (sulfite mill, chlorine) 

Champion Paper Company; heavily industrialized; Superhmd site 

Simpson Pulp Mill (wood overlay products) 

lTf Rayonier. Inc. 

Simpson Paper Company (downsueam) 

Light agriculuxe; umber 

Weyerhaeuser Company and Scott Paper Company; Super-fund sin! 

(solveras) 

Georgia Pacific (sulfite process) 

D-I-13 
D-l-14 
APPENDIX D-2 

Dioxins/Furans: Episode Numbers Used in Statistical Tests 

(By Category) 
TABLE D-2 

Dioxins/Furans: Episode Numbers Used in Statistical Tests (By Category) 

NAsQm WQ) 

Episode 

2015 

2016 

2017 

2023 

2026 

2070 

2098 

2105 

2122 

2126 

2148 

2151 

2152 

2191 

2205 

2220 

2228 

2246 

2247 

2280 

2298 

2309 

2322 

2358 

2430 

243 1 

2432 

2437 

2439 

2478 

2544 

2776 

3036 

3041 

State 

AR 

AR 

AR 

AR 

OK 

AK 

ND 

MS 

FL 

FL 

FL 

IA 

NE 

VA 

VA 

WA 

WA 

TX 

TN 

AL 

NY 

ME 

MI 

MI 

MI 

MN 

OH 

ID 

LA 

NV 

IA 

NE 

3042 NE 

3050 MO 

3104 PA 

3199 SD 

3281 CA 

3308 NY 

Total 40 

AGRICULTURE (AG) 

Episode State 

2280 TX 

2358 ME 

2478 ID 

3050 MO 

3082 LA 

3083 LA 

3084 TX 

3099* DE 

3105 OK 

3158* ID 

3170 AL 

3171 AL 

3180 GA 

I 3193 VA 

3208 OR 

I I 3212 OR 

I 3282 CA 

I 3352 LA / 

I 3437 OR 

I Total 19 

1 

1 SUPERFUND (NPL) 

Episode State 

3078 

3097 DE 

I 

) 3226 WA 

3261 

3272 

3414 

3415 

Total 

POTW 

HI 

CA 

PA 

PA 

7 

Episode State 

2122 

2152 FL 

2322 NY 

2432 MI 

2544 LA 

3308 NY 

3450 CA 

3451 CA 

Total 8 

BACKGROUND (B) 

Episode State 

2027 OK 

2037 HI 

2110 SD 

2139 NC 

2216 PA 

2283 TX 

2301 TN 

2379 IL 

2387 MN 

2397 WI 

2435 MI 

2651 NJ 

3001 MN 

3022 ME 

3023 ME 

3027 ME 

* No data available for dioxins/furam. Number of data vahes varies by chemical. 

D-2-I 
TABLE D-2 (Cont.) 

3028 ME 

3037 IA 

3073 AR 

3074 NM 

3075 TX 

3166 NC 

3169 AL 

3178 GA 

3179 GA 

3187 SC 

3200 co 

3205 OR 

3238 AK 

3248 ID 

3309 NY 

3320 NY 

3430 NJ 

Total 33 

PULP & PAPER 

(Chlorine) (PPC) 

Episode 

2015 

2016 

2017 

2138 

2142 

2294 

2302 

2304 

2355 

2385 

2422 

2427 

2532 

2721 

2725 

3062 

State 

AR 

AR 

NC 

FL 

GA 

AL 

AL 

ME 

MN 

WI 

WI 

L4 

ME 

AR 

3080 

3081 

3088 

3 107 

3118 

3 122 

3146 

3150 

3151 

3152 

3192 

3217 

3218 

3220 

3221 

3222 

3224 

3237 

3245 

3246 

3256 

3260 

3267 

3303 

3316 

3317 

3318 

3328 

3329 

3331 

3332 

3333 

3335 

3336 

3337 

3339 

3340 

LA 

TX 

LA 

WI 

MI 

MI 

WI 

MA 

MA 

NH 

WA 

OR 

OR 

WA 

WA 

WA 

WA 

MT 

ID 

NY 

CA 

NY 

PA 

MD 

PA 

AL 

FL 

FL 

FL 

FL 

GA 

GA 

GA 

KY 

MS 

3341 MS 

3342 NC 

3343 NC 

3344 NC 

3345 NC 

3346 NC 

3347 SC 

3348 SC 

3349 SC 

3350 TN 

3351 TN 

3353 LA 

3395 NC 

3403 TN 

3404 TN 

3416 LA 

3418 LA 

3420 PA 

3421 VA 

3422 VA 

3423 VA 

3424 VA 

3425 LA 

3435 MS 

3452 AR 

Total 78 

INDUSTRY/URBAN 

(IND/URW 

Episode State 

1994 MI 

2023 AR 

2057 IN 

2060 IN 

2191 IA 

2210 DC 

2215 PA 

2220 VA 

+ No data available for dioxinsffu.rans. Number of data values varies by chemical. 

D-2-2 
TABLE D-2 (Cont.) 

2225 

2227 

2309 

2328 

2329 

2410 

2416 

2500 

3024 

3025 

3034 

3035 

3038 

3039 

3040 

3042 

3043 

3044 

3045 

3046 

3047 

3048 

3049 

3060 

3064 

3066 

3079 

3085 

3094 

3100 

3101 

3103 

3111 

3113 

3115 

3120 

3134 

VA 

VA 

AL 

NY 

NY 

MI 

OH 

NY 

NY 

NY 

NY 

NY 

NY 

PA 

IA 

IA 

IA 

KS 

MO 

NE 

NE 

MO 

MO 

MO 

MO 

MO 

MO 

AR 

LA 

LA 

OK 

TX 

PA 

3141 

3144 

3147 

3149 

3164 

3165 

3168 

3172 

3174 

3182 

3188 

3189 

3190 

3198 

3199 

3203 

3206 

3219 

3227 

3231 

3234 

3235 

3236 

3244 

3249 

3250 

3252 

3258 

3269 

3275 

3276 

3283 

3285 

3286 

3289 

3296 

3297 

WI 

WI 

DC 

DE 

NC 

NC 

AL 

AL 

FL 

KY 

TN 

TN 

TN 

co 

SD 

OR 

OR 

OR 

WA 

WA 

PULP & PAPER 

(No Chlorine) (PPNC) 

Episode State 

3089 OK 

PA 3090 OK 

3091 OK 

3092 LA 

IL 3093 TX 

IL 3108 WI 

MI 3112 MN 

WI 3114 IL 

3135 WI 

* No data available for dioxins/furans. Number of data values varies by chemical. 

ID 

ID 

ID 

VA 

CA 

CA 

CA 

CA 

CA 

CA 

CA 

NY 

NY 

3298 

3299 

3300 

3301 

3302 

3306 

3307 

3310 

3311 

3313 

3314 

3315 

3321 

3322 

3324 

3326 

3327 

3411 

3412 

3426 

3428 

3432 

3438 

3443’ 

Total 

PA 

NY 

NY 

NY 

NY 

NY 

NY 

NY 

NJ 

NJ 

PR 

WA 

AR 

106 

O-2-3 
3136 WI 

3137 WI 

3138 WI 

3140 WI 

3143 WI 

3145 WI 

3184 MS 

3191 WA 

3270 CA 

3287 CA 

3294 WA 

3330 FL 

3360 AL 

3375 GA 

3376 GA 

3377 GA 

3378 GA 

3401 TN 

Total 27 

WOOD PRESERVERS 

0 

Episode State 

3076 OK 

3077 AR 

3110 WI 

3167 NC 

3173 FL 

3196 

3197 co 

3271 CA 

3273 CA 

3274 CA 

3278 CA 

Total 11 

TABLE D-2 (Cont.) 

REFINERY/OTHER 

INDUSTRY (R/I) 

Episode 

2026 

2380 

2383 

3061 

3063 

3069 

3071 

3072 

3086 

3095 

3096 

3125 

3183 

3264 

3312 

3431 

3434 

3442 

3444 

3446 

Total 

State 

OK 

IL 

IL 

AR 

LA 

TX 

TX 

TX 

LA 

PA 

PA 

MN 

KY 

CA 

PR 

NJ 

LA 

TN 

KY 

20 

l No data avaiiable for dioxins/furans. Number of data values varies by chemical. 

D-2-4 
APPENDIX D-3 

Xenobiotics: Episode Numbers Used in Statistical Tests 

(BY c~ww-Y) 
TABLE D-3 

Other Xenobiotics: Episode Numbers Used in Statistical Tests (By Category) 

NASQM WQ) 

Episode 

2015 

2016 

2017 

2023 

2026 

2070 

2098 

2105 

2122 

2126 

2148 

2151 

2152 

2191 

2205 

2220 

2228 

2246 

2247 

2280 

2298 

2309 

2322 

2358* 

2430 

243 1 

2432 

2437 

2439 

2478 

2544 

2776 

3036 

3041 

3042 

3050 

3104 

3199 

3281 

3308 

Total 

NE 

NE 

MO 

PA 

SD 

CA 

NY 

40 

3261 HI 

State 3272 CA 

AR 3414 PA 

AR 3415 PA 

AR Total 6 

AR 1 

OK : POTW 

AK ) Episode State 

WY ! 2122 

ND ’ AGRICULTURE (AG) 2152 FL 

MT i Episode State 2322 NY 

MS I 2280 TX 2432 MI 

FL / 2358* ME 2544 LA 

FL 2478 ID 3308 NY 

FL 3050 MO 3450* CA 

IA 3082 IA 3451’ CA 

NE 3083 LA Total a 

VA 3084 TX 

VA 3099 DE BACKGROUND (B) 

WA 3105 OK Episode State 

WA 3158 ID 2110 SD 

TX 3170 AL 2139 NC 

TN 3171 AL 2216 PA 

AL 3180 GA 2283 TX 

NY 3193 VA 2397 WI 

ME 3208 OR 2435 MI 

MI 3212 OR 2651 NJ 

MI 3282 CA 3022 ME 

MI 3352 LA 3023 ME 

MN 3437* OR 3028 ME 

OH Total 19 3037 IA 

ID 3073 AR 

LA SUPERFUND (NPL) 3074 NM 

NV Episode State 3075** TX 

IA 3097 DE 3166 NC 

3226 WA 3169 AL 

l 

l * 

No data available for other xenobiotics. Number of data values varies by chemical. 

Data available for mercury only. 

D-3-l 
3178 GA 

3200 co 

3205 OR 

3238 AK 

3248 ID 

Total 21 

PULP & PAPER 

(Chlorine) (PPC) 

Episode 

2017 

2138* * 

2294 

2302 

2422 

2532 

2721 

2725 

3107 

3118 

3122 

3151 

3152 

3192 

3222 

3224 

3237 

3245 

3246 

3260 

3267 

3303 

3316 

33 18 

3332 

3335 

3336 

State 

AR 

NC 

GA 

AL 

WI 

LA 

ME 

WI 

MI 

MI 

NH 

WA 

WA 

WA 

NY 

CA 

NY 

PA 

PA 

FL 

GA 

GA 

TABLE D-3 (Cont.) 

3340 MS 

3341 MS 

3342 NC 

3348 SC 

3395 NC 

3403 TN 

3416* LA 

3418* IA 

3420 PA 

3421 VA 

3422 VA 

3423 VA 

3424 VA 

3425 LA 

3435 MS 

Total 42 

INDUSTRY/URBAN 

(IND/URB) 

Episode State 

3043 NE 

3044 MO 

3045 MO 

3079 OK 

3085 TX 

3101 PA 

3120 MI 

3149 DE 

3172 AL 

3174 FL 

3189 TN 

3190 TN 

3203 OR 

3234 

3235 

3236 

3244** 

3258 VA 

3269’ CA 

3275‘* CA 

t 3276 CA 

3283 CA 

3285 CA 

3286 CA 

3289 CA 

3296 NY 

3298 NY 

3306 NY 

3307 NY 

3315 PA 

3411 NY 

3412 NY 

3426 NJ 

3428 NJ 

3438‘ WA 

Total 35 

PULP & PAPER 

(No Chlorine ) (PPNC) 

Episode State 

3090 OK 

3091 OK 

3108 WI 

3112 MN 

3135 WI 

3136 WI 

3140 WI 

3143 WI 

3145 WI 

3191 WA 

3287 CA 

3294 WA 

3330 FL 

3360 AL 

* No data available for other xenobiotics. Number of data values varies by chemical. 

l * Data available for mercury only. 

D-3-2 
TABLE D-3 (Cont.) 

3376 GA 

3377 GA 

3401 TN 

Total 17 

WOOD PRESERVERS 

olrp) 

Episode State 

3076 OK 

3077 AR 

3110 WI 

3167 NC 

3 173 FL 

3196 

3197** co 

3271 CA 

3273 CA 

3274 CA 

3278 CA 

Total 11 

REFINERY/OTHER 

INDUSTRY (wr) 

Episode State 

3061 AR 

3063 IA 

3072 TX 

3095 PA 

3446 KY 

Total 5 

I No data available for other xenobiotics. Number of data values varies by chemical. 

** Data available for mercury only. 

D-3-3 
D-3-4 
APPENDIX D-4 

Dioxin/Furan Data by Episode Number 
Key for DioxidFuran Data Table (Units = pg/g) 

2.3.7.8 TCDD 

1,2,3,7,8 PeCDD 

123478HxCDD . 9 . 9 . 

123678HxCDD 9 9 9 * . 

123789HxCDD 9 l P I 9 

1,2,3,4,6,7,8 HpCDD 

2,3,7,8 TCDF 

12378PeCDF 9 9 * , 

23478PeCDF I . * . 

1,23,4,7,8 HxCDF 

123678HxCDF , I . 1 . 

123789HxCDF , 9 t . 3 

234678HxCDF , * 1 9 9 

1,2,3,4,6,7,8 HpCDF 

1.2.3.4,7,8,9 HpCDF 

Tetrachlorinated dibenzodioxins 

Pentachtorinated dibenzodioxins 

Hexachlorinated dibenzodioxins 

Heptachlorinated dibenzodioxins 

Tetrachlorinated dibenzofurans 

Pentachlorinated dibenzofumns 

Hexachlorinated dibenzofurans 

Heptachlorinated dibenzofurans 

1746-01-6 

40321-764 

39227-28-6 

57653-85-7 

19408-74-3 

3787 1-004 

51207-31-g 

57117-41-6 

57117-31-4 

70648-26-g 

57117-44-g 

72918-21-9 

60851-w-5 

67562-394 

55673-89-7 

ND = Not Detected Episode Number: Refer to Site Matrix Table 

;i 

= Not Analyzed 

= Below 40 percent recovery D-l for Waterbody Name and Location 

DPE = Diphenyl Ether interference, a “I”’ in the 

column indicates that there was interference SCC = Sample Control Center Numbers 

with the analyses for 2,3,4,7,8 PeCDF; 1,2,3,4,6,7 

HxCDF; 123478HxCDF;and23467,8 9 . 9 t 9 1 . * I 

HxCDF 

= Asterisk on 1,2,3,4,7,8 HxCDF indicates S = Confumation Sample* 

coelu tion with 1,2,3,4,6,7 HxCDF on GC column 

(DB5 3OM)x 

= Environmental Sqple 

= Duplicate Sample 

Sample Type 

F = Field Sample 

L = LabDuplicate 

M = Mollusks/Crustaceans 

0 = Other 

Fish Tissue Type 

PF = Predator Fillet 

BF = Bottom Fillet 

WB= Whole Body 

WP = Whole Predator 

A= Region 1 

B = Region 2 

C = Region 3 

D= Region 4 

E = Region 5 

F = Region 6 

G= Region 7 

H= Region 8 

Y= Region 9 

J = Region 10 

*The number of samples shown on the summary 

tables in Volume I does not include the duplicate 

and confvmation samples. 

04-i 
o-4-2 
Dioxins/Furans 

Concentration Ranges 

O-43 
D-64 
Episode SCC Type Description 

lW4 DE017702 F VB Carp 

1994 DE017703 F Pf Ualleye 

lW4 00110586 L WE Carp 

1998 13285 F UB Carp 

lW8 13421 f PF Pike 

2015 DFOOlz F UB Carp 

2015 DFOOlOO2 F UP Crappie 

2016 DFOOllOl F !A Sucker 

2016 DF001102 F EF Sucker 

2017 DFOOl201 F UB Carp 

2017 DFO01202 F BF Carp 

2018 DFOO1301 F UB Sucker 

2023 DFOOl402 F PF Spotted Bass 

2023 DFO0?403 F UB Carp 

2026 DFOO1702 F YB Carp 

2026 DFOO?703 F PF White Crappie 

2027 DFO01802 F PF Lm Bass 

2027 DFOO1803 F WO Carp 

2037 DYOOOSOl F WE not available 

2037 01000502 F UP not evaileble 

2056 DEODOSOI f U0 Carp 

2057 DE000601 F UB CarD 

2059 DE000801 F UB Carp 

2060 DEOOD9Dl F LIB CsrD 

2070 DJ0009Dl F UP Rainbow Trout 

2070 DJOOO9D2 F IJB Longnose Sucker 

2070 00072186 L UP Rainbw Trout 

2098 DHOO1501 F UB not available 

2098 OftOO? F Pf not available 

2100 DHO01702 F PF Sauger 

2100 DH001703 F UB Catfish 

2100 90111086 1 UE Catfish 

2105 DHOO2201 F PF Sauger 

2105 DHOO2204 F UR Carp 

2105 PO063086 L UB Carp 

2109 OH00260l F WE not aveileble 

2109 OH002602 F BF not available 

2110 OH002710 F UP Et-am Trout 

2122 DH003901 F PF Rainbow Trout 

2122 DH0039D4 F UB Mite Sucker 

2126 DDOOo302 F WE Carp 

2126 00000303 F PF Uhite Crappie 

2126 QDO62bsb L UB Carp 

2133 ODOOlOO2 F BF Blue Catfish 

2378 

TCDO 

34.03 

ND 

29.26 

ND 

9:2 

1.43 

4.17 

1.69 

0.64 

ND 

NO 

NO 

NO 

1.17 

ND 

ND 

0.46 

NO 

:“23 

!D63 

1.76 

ND 

ND 

ND 

No 

NO 

ND 

1.65 

1.98 

ND 

ND 

ND 

0.97 

ND 

ND 

ND 

ND 

ND 

ND 

2.16 

NO 

12378 

PECDD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

1.09 

QR 13 

NO 

ND 

NO 

ND 

NO 

NO 

NO 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

DIOXIN / FURAN CDNCENTRATICWS. m/g 

123478 123678 123789 1234678 2378 12378 23478 

HXcOo 

OR 5 

OR ND 

4.01 

ND 

ND 

ND 

ND 

ND 

ND 

1.72 

ND 

PR NO 

NO 

0.76 

ND 

ND 

NO 

ND 

ND 

NO 

PR MO 

ND 

QR 2 

aR ND 

ND 

NO 

QR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

NO 

QR ND 

ND 

ND 

ND 

QR ND 

1.84 

ND 

HXCOD 

OR 61 

OR ND 

58.90 

1.91 

ND 

4.48 

ND 

2.95 

2.05 

3.32 

1.05 

PR ND 

ND 

ND 

1.35 

NO 

ND 

3.57 

NO 

ND 

OR 15 

ND 

OR 16 

OR 2 

ND 

NO 

OR NO 

ND 

ND 

ND 

7.34 

ND 

ND 

ND 

ND 

NO 

ND 

QR ND 

ND 

::48 

OR NO 

4.77 

1.97 

HXCDO 

OR 16 

PR ND 

13.47 

ND 

ND 

ND 

ND 

ND 

No 

0.74 

NO 

OR ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

NO 

OR No 

ND 

OR NO 

OR ND 

NO 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

OR ND 

ND 

ND 

1.61 

OR ND 

1.41 

ND 

HPCDD 

QR 45 

QR ND 

OR ND 

4.44 

ND 

OR 15 

OR ND 

4.04 

5.10 

OR 14 

QR 6 

OR ND 

OR 2 

3.08 

PR 5 

5.48 

OR ND 

QR ND 

ND 

QR 4 

aR 45 

8.16 

OR 22 

OR 8 

NO 

OR 3 

QR ND 

OR ND 

1.01 

ND 

OR ND 

OR NO 

1.06 

OR ND 

OR ND 

OR 14 

QR 4 

PR ND 

1.89 

4.32 

PR 23 

QR ND 

OR 23 

OR 6 

TCDF 

14.09 

0.80 

12.63 

2”“28 

4.17 

2.38 

16.61 

5.23 

1.47 

0.31 

0.74 

ND 

0.30 

0.55 

ND 

NO 

0.81 

0.29 

::39 

2.66 

4.55 

2.20 

0.50 

UD 

ND 

0.61 

NO 

ND 

0.21 

ND 

ND 

ND 

ND 

0.46 

MD 

ND 

NO 

1.09 

0.37 

ND 

ND 

ND 

PECDF 

8.19 

ND 

7.74 

0.76 

NO 

NO 

ND 

ND 

ND 

0.33 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

NLI 

0.92 

1.36 

ND 

F&l 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

PECDF 

29.32 

::.30 

1.93 

HO 

2.11 

ND 

1.11 

NO 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

1.33 

3.26 

0.91 

15.41 

ND 

NO 

NO 

ND 

ND 

NO 

NO 

ND 

1.47 

ND 

ND 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

123478 123678 123789 234678 1234678 1234789 

HXCDF* HXCDF HXCDF HXCDF HPCDF HPCOF 

OR 19 OR 6 OR NO 

OR ND OR ND PR ND 

17.04 ND ND 

NO ND ND 

MO MD ND 

OR 2 OR 1 ORND 

ND ND NO 

2.19 ND ND 

0.63 ND ND 

ND ND ND 

ND NO ND 

QR ND OR ND PR ND 

NO ND ND 

MD ND ND 

NO ND ND 

ND ND ND 

ND ND NO 

ND ND ND 

ND ND NO 

1.24 1.35 ND 

ND 1.51 MD 

NO ND ND 

OR 3 OR 1 OR ND 

0.84 ND ND 

ND ND ND 

ND ND No 

QR ND OR ND PR ND 

ND ND ND 

ND ND ND 

ND ND ND 

HD ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

OR ND OR MD OR ND 

If0 UO MD 

QR ND OR NO OR ND 

0.35 ND ND 

ND ND NO 

ND ND ND 

OR ND OR ND OR ND 

OR ND QR ND OR ND 

ND ND ND 

OR 8 OR 17 QR ND 

OR ND QR ND OR ND 

4.89 OR 17 OR ND 

ND ND ND 

ND No NO 

PR ND OR 2 OR ND 

ND OR ND OR ND 

2.05 3.09 ND 

0.81 ND ND 

ND QR ND QR ND 

MD OR ND QR ND 

OR ND OR ND OR NO 

No QR ND OR NO 

ND OR ND OR ND 

ND QR ND OR ND 

ND ND ND 

ND OR ND OR ND 

ND QR ND OR ND 

ND 1.13 ND 

NO OR ND OR ND 

NO OR 6 OR HO 

ND 1.29 ND 

OR 1 OR 4 OR ND 

0.48 OR 2 QR UD 

ND NO ND 

NO OR ND OR ND 

QR ND QR NO PR ND 

UD OR ND PR ND 

ND No No 

MD ND NO 

ND OR NQ OR ND 

ND OR ND OR ND 

ND ND ND 

NO PR ND QR ND 

ND OR ND OR ND 

OR ND OR 3 OR NO 

NO ORNO QRMD 

OR ND OR ND OR ND 

No No NO 

NO NO ND 

NO QR NO OR NO 

QR ND QR IID OR ND 

QR MD QR nD OR ND 

ND PR ND OR ND 

DPE 

TEC 

50.51 I 

0.08 

52.89 r 

0.35 Y 

0.91 Y 

6.65 Y 

1.67 

7.18 Y 

2.61 I 

1.40 Y 

0.14 

0.07 

UO 

0.14 

1.36 

0.05 

ND 

0.90 

0.04 Y 

0.97 

6.32 Y 

1.36 Y 

14.79 Y 

2.14 Y 

0.05 

ND 

ND 

0.06 

0.01 

NO Y 

2.40 Y 

2.72 

0.01 

ND 

ND 

1.02 Y 

UO 

0.E 

0.15 

0.75 

NO 

2.w 

0.20 

D-4-5 
Episode SCC Type Oescriptim 2370 

2138 WOOWM f W Redhorse Sucker 

2138 DDWlSD4 F PF 11 Bsss 

2139 DOW1601 F UB Carp 

2139 DOW1404 F PF Rainbow Trout 

2139 DDOTI486 1 PF Rainbow Trout 

2142 DDWlPOZ F HI Catfish 

2142 DOWlW3 F PF Lm Bass 

2141 00002501 F YB !GaItuster Catfish 

2148 DDW25D4 F BF Saltuatsr Catfish 

2151 WW2801 F PF Lm Bass 

2151 DDW28D3 F UB Spotted Sucker 

2152 WOW902 F PF Lm Bass 

2152 DDW29D3 F UB Lekt Chbsucker 

ZIP0 DC005101 F UB Carp 

2190 DGW5lD4 F PF t)luegill 

2191 DGW52D5 F bm Carp 

219t DGW52lM F BF Carp 

2191 DDD92406 L RF Carp 

2194 DGDO5501 F w Cam 

21% DWD5SD4 F RF Ch&nel Catfish 

2199 OCW4001 F UR Carp 

2199 0s F PF Lm Bass 

22Dl D-1 F UB Carp 

2201 DCiC&MM F PF 0o&in 

2205 DGDM601 F UB Carp 

2205 DGW6602 F BF Carp 

2210 DCW%Ol F W Catfish 

2211 DC003503 F M Rcdhorrc Sucker 

2212 DCWS602 F PF Sm Bass 

2212 OCWSfiO5 F W Hite Sucker 

2215 DCW59D2 F m Carp 

2216 DC-006002 F PF Bran Trout 

2216 DCOD6003 F llB hhhlte Sucker 

2220 DCW6401 F PF Redbreest Smfish 

222D DCW64D5 F YB Catfish 

2225 DC- F PF SI Bass 

2225 DC006905 F YB Shorthead Rcdhorsc 

2225 8101387 1 w1 Shorthead Rcdnorst 

2227 DC007102 F PF La Roar 

2227 DC007104 F 118 Channel Catfish 

2226 DCDD7201 F PF Longcar Sunfish 

2228 OCW72D4 F W Ruhorse Sucker 

2228 WWlV86 1 M Redhorse Sacker 

2231 DC007503 f U tirrord Shad 

2.01 

0.06 

WD 

2.26 

1.87 

ND 

m 

No 

nrl 

m 

110 

ND 

m 

Ro 

MD 

m 

No 

no 

ND 

L 

ND 

ND 

ND 

10 

ND 

5.61 

0.59 

ND 

2.01 

ND 

nD 

m 

UD 

ND 

!!76 

5.06 

No 

ND 

ND 

m 

no 

m 

12378 

PECDD 

1.79 

0.62 

MD 

ND 

I)[, 

0.66 

ND 

ND 

ND 

ND 

UD 

m 

MD 

MD 

10 

ND 

MD 

10 

nD 

ORND 

nD 

m 

m 

ND 

ND 

ND 

110 

ND 

m 

MD 

No 

I(0 

No 

I*) 

WD 

110 

2.93 

2.58 

m 

0.76 

m 

no 

10 

BID 

l2347B 123678 123789 1234678 2378 

DIOXIN / FURAN CDNCENTR~TIOWS, w/R 

12378 23428 

HXCDO 

ND 

ND 

PR ND 

m 

ND 

ND 

ND 

ND 

ND 

MD 

ND 

110 

ND 

MO 

m 

PRND 

wo 

No 

m 

aRnD 

no 

ND 

aRm 

QRNO 

ND 

no 

QRLY) 

ND 

ORMI 

no 

ND 

110 

ND 

No 

uo 

ND 

1.70 

1.10 

m 

ICI 

ND 

m 

ND 

IID 

4.61 

4.13 

ORND 

ND 

nD 

IID 

ND 

m 

ND 

ND 

wp 

m 

m 

m 

IID 

aR7 

m 

1.59 

4.4a 

OR)0 

1.11 

m 

m 12 

ORNO 

ND 

ND 

ORno 

0.20 

aam 

z4 

ND 

ND 

m 

2.22 

:25 

2.86 

ND 

2.77 

No 

m 

1.36 

m 

HPCDO TCDF 

15.91 13.45 

6.72 0.82 

ORND ND 

2.21 0.90 

1.67 0.73 

6.74 0.26 

No 0.10 

DR3ND 

1.60 ND 

2.06 llD 

2.04 ND 

2.62 ND 

2.55 ND 

5.98 nD 

1.80 ND 

QA 23 1.33 

DR9m 

WI wp 

QRIRI 1.16 

onm ND 

4.02 110 

:56 : 

-ND nD 

m No 0.30 

ND 0.41 

MS 0.85 

1.29 7.77 

mm ND 

4.32 13.97 

12.92 0.00 

m 

ORno E9 

E2" :42 

0.36 0.38 

6.67 44.75 

6.92 38.76 

L5 0.39 0.24 

anzu, 

no 3.81 

QR3 4.21 

on 4 a.5 

PLCOF 

1.33 

0.27 

ND 

Ml 

0.47 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

MD 

ND 

m 

0.61 

110 

m 

nD 

ND 

m 

No 

m 

lm 

m 

m 

ORm 

No 

m 

X:G 

ND 

no 

ND 

ND 

ND 

l.w 

1.54 

w 

IID 

II) 

m 

ND 

m 

PECDF 

3.69 

0.52 

:70 

0.70 

0.06 

I*, 

ND 

I(0 

ND 

ND 

m 

m 

Ml 

UD 

MD 

ND 

nD 

(I.74 

:22 

UD 

no 

uo 

n8 

UD 

QRnD 

1.40 

II) 

2.86 

1.73 

ND 

ND 

EM 

La 

3.16 

?54 

ND 

No 

0.71 

1.6 

123478 123670 123789 234670 1234678 1234709 

HXCDF' HXCDF HXCDF HXCDF HPCDF HPCDF 

DPE 

TEC 

11.3 

1.7 

ORND 

uo 

no 

Ml 

no 

ND 

no 

NO 

IQ, 

ND 

UD 

ND 

UD 

QUUD 

NO 

m 

No 

QRnD 

0.37 

ii 

No 

m 

KJ 

1.25 

1.90 

mm 

1.11 

ND 

IID 

L 

m 

110 m 

m ND 

ORWD ORND 

ND ND 

MD MD 

ND ID 

ND ND 

MD nD 

(0 ND 

nD ND 

m ND 

ND m 

m nD 

II0 Y) 

ND II) 

aRND PRWD 

ND IID 

m ND 

Ilo ND 

ORHD ORm 

MD MD 

10 II) 

ND ND 

nD m 

No IID 

MD m 

m ND 

m 10 

aRND 9(1# 

m ND 

ND MD 

MD 10 

10 10 

ND MD 

10 ItD 

m F6 m 

Ro 10 

3.aO ND m 

nD No ND 

nD m (0 

m MD ND 

o-u3 MD m 

1.67 RD # 

2.6 WD ND 

5.45 

0.60 

ORND 

ND 

m 

ND 

m 

ND 

MD 

m 

ND 

nD 

MD 

110 

ND 

ORm 

ND 

MD 

m 

aRu0 

ND 

MD 

ND 

BID 

MD 

MD 

MD 

1.56 

aRm 

ND 

110 

ND 

ND 

ND 

110 

!!I7 

4.11 

II) 

ND 

:sr 

nD 

1.0 

4.77 ND 

1.00 ND 

QR ND OR )10 

ND 

:c* ND 

1.13 ND 

ND ND 

QRND ORYD 

nD ND 

m ND 

ND ND 

ND ND 

ND ND 

m MD 

Ial ND 

QRC aRND 

DRNO OanD 

Qllm ORnD 

ORnD aam 

9RwD ORnD 

ND w 

IID No 

ORMO ORND 

ORND ORlID 

aRm QRND 

O.% m 

ORnD PRNO 

1.29 No 

aRm ORND 

IID ND 

1.44 ND 

II0 ND 

ORND aRnD 

ORno mm 

UD m 

ND 

?.03 ND 

4.49 ND 

w No 

0.61 m 

aam PRY) 

nD MD 

aRm PRY, 

am2 aRm 

0.62 r 

2.3D v 

ND 

2.72 Y 

2.34 

0.06 Y 

0.01 

0.: 

a.02 

0.02 

0.03 

0.03 

0.04 

0.02 

0.16 Y 

No Y 

0.16 Y 

0.93 

2.; Y 

iii 

0.: 

0.0s Y 

5.82 Y 

2.46 Y 

ND Y 

5.04 Y 

1.57 Y 

0.: 

0.08 

0.52 Y 

0.04 

16.W Y 

13.98 Y 

0.04 

1.12 Y 

ND 

0.52 Y 

1.08 Y 

2.01 Y 
Episode SCC Type Description 2378 12378 

Tam PECDD 

ND 

ND 

NO 

0.37 

ND 

MD 

ND 

ND 

No 

4.5 

2.6 

1.69 

ND 

ND 

ND 

ND 

ND 

:55 

28.66 

16.08 

ND 

ND 

ND 

ND 

ND 

ND 

nD 

12.89 

12.49 

2.14 

4.42 

7.97 

3.57 

23.M 

ND 

ND 

1.01 

ND 

ND 

1.26 

ND 

ND 

ND 

ND 

ND 

nD 

ND 

ND 

ND 

ND 

110 

QRND 

14.3 

0.9 

0.75 

0.35 

ND 

QRND 

ORm 

ND 

nD 

0.47 

9.40 

1.26 

ND 

nD 

ND 

ND 

ND 

ND 

ND 

110 

ND 

ND 

ND 

1.16 

NO 

ND 

ND 

QRND 

OR ND 

ND 

ND 

0.80 

m 

ND 

m 

DIOXIN / FURAN CDNCENlRATIO1(S, Pg/B 

123478 123678 123789 1234678 2378 12378 23478 123478 123678 

HXCDF* HXCDF 

123789 234678 1234678 1234709 DPE 

HXCDF HPCDF HPCDF TEC 

ND 

0.16 Y 

0.31 Y 

0.94 Y 

ND 

0.07 

0.02 

No 

30.: Y 

3.54 Y 

3.DB Y 

0.39 Y 

0.05 Y 

m 

02 

ND 

0.93 Y 

48.03 Y 

20.81 Y 

1.17 Y 

0.32 Y 

ND 

0.04 

ND 

0.36 Y 

ND 

16.63 Y 

13.48 Y 

3.21 Y 

a.57 Y 

14.03 Y 

3.80 

29.34 Y 

0.82 

ND 

1.w Y 

0.85 

0.08 Y 

3.94 Y 

2.29 Y 

1.65 Y 

ND 

HXCDD TCDF PECDF PECDF 

ND 

0.20 

ND 

ND 

nD 

ND 

ND 

ND 

No 

17.2 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::97 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

&9 

3.11 

1.46 

m 

m 

ND 

ND 

ND 

ND 

ND 

0.67 

ND 

No 

ND 

ND 

ND 

ND 

0.50 

ND 

No 

No 

ND 

ND 

15.3 

:52 

No 

ND 

MD 

ND 

ND 

ND 

722 

Ok 

ND 

ND 

ND 

ND 

756 

ND 

4.61 

?91 

5.21 

1.13 

::19 

no 

ND 

ND 

ND 

ND 

1.19 

2.03 

1.67 

ND 

2246 05002301 F BF Bridgelip Sucker 

2246 DJW2302 F UB Bridgctip Sucker 

2247 DJW2403 F EF BridBelip Sucker 

2247 DJOO2404 F VP Ikurtain Whitefish 

2280 DFDO5201 F UB Carp 

2280 OFDO F BF Charmel Catfish 

2280 PO062386 L BF Chars-d Catfish 

2283 DFOO5501 F UB Gray RFdhorse 

2283 DFWSSOZ F VP Longear Sunfish 

2290 WW3403 F LIB Spotted Sucker 

2294 WW3801 F PF 11 Bass 

2294 WW3804 F UB Carp 

2297 WOD4102 F UB Carp 

2297 WOD4103 F PF 11 Bass 

2298 WOD42Dl F UB Charmel Catfish 

229B WW4203 F UP Lm Bass 

2301 WOD4504 F UP Rock Bass 

2301 00071786 L UP Rock Bass 

2302 DDW46Dl F UB Quillback Carpsucker 

ND ND 

ND 0.52 

ND 0.58 

II) 0.57 

No ND 

ND ND 

ND ND 

ND ND 

OR ND OR ND 

ND 9.6 

ND 0.4 

ND 0.24 

ND ND 

ND ND 

OR ND ORND 

ORND aRND 

ND ND 

ND ND 

ND ND 

ND 1.82 

ND ND 

QRNO PR ND 

ND No 

QRND ORND 

m ND 

ND ND 

nD m 

nD ND 

ND 1.36 

ND ND 

ND 0.34 

ND 0.67 

ND 0.90 

ND WD 

ND M, 

nD ND 

PR ID ORND 

ORND OR ND 

OR ND OR ND 

ND ND 

ND ND 

ND nD 

ND ND 

ORND ORND 

PRND QRND 

9RnD QRND 

PR 1 OR ND 

OR1 DRND 

PRND ORND 

m ND 

ND ND 

aRND OR NO 

ORND ORND 

12.5 0.5 

0.5 ND 

0.53 nD 

ND 

:30 nD 

ORND 9RND 

ORND ORND 

PRnD ORm) 

ORND OR ND 

0.73 ND 

5.54 ND 

0.37 ND 

ORND ORND 

ORM) aRm 

ORND ORND 

QRND ORND 

OR Ho OR ND 

ND ND 

No 

FL ND 

OR 2 PR ND 

0.63 ND 

1.55 No 

2.29 No 

ORND PR ND 

ND m 

ORND OR ND 

QRND QRND 

9R ND PR ND 

OR 2 OR ND 

ND ND 

1.02 NO 

nD ND 

PRm QQND 

ORm ORND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

7.5 

:55 

ND 

No 

OR ND 

OR Iy) 

No 

OR ND 

ND 

ND 

ND 

1.30 

1.64 

ND 

0.44 

ND 

ND 

No 

loo.9 

1.2 

:47 

nD 

OR ND 

ORND 

ND 

OR ND 

110 

ND QR ND 

m PR 5 

ND QR 1 

nD OR 2 

NO QR ND 

ND 2.17 

ND 2.10 

ND OR ND 

ND QR ND 

6.7 141.2 

0.2 2.3 

0.29 4.58 

ND 1.67 

ND ND 

QR ND QRND 

QRII) ORND 

ND OR ND 

ND 

ND 

1.22 

0.99 

ND 

m 

ND 

ND 

ND 

22.0 

2.1 

ND 

1.00 

ND 

ND 

ND 

m 

ND 

ND 

ORND 

11.6 

0.7 

0.70 

ND 

ND 

QRND 

PR Ml 

ND 

ND 

0.50 

4.20 

0.20 

OR 10 

ND 

QRND 

ND 

ND 

ND 

ND 

m 

ND 

ND 

ND 

No 

No 

ND 

OR ND 

6.2 

ND 

ND 

ND 

m 

OR ND 

OR ND 

ND 

ND 

:52 

nD 

QRND 

ND 

OR ND 

ND 

ND 

Ml 

ND 

ND 

ND 

no 

0.02 

ND 

ND 

ND 

ND 

PR ND 

PRND 

ORND 

ND 

ND 

ND 

No 

QRm 

5.29 

1.51 

0.45 

nD 

&6 

aRM) OR ND 

0.21 2.60 

5.38 90.77 

0.32 2.20 

?45 

2304 DDOO4801 F UB Carp 

2304 DDW4W4 F PF ln Bass 

2309 DODD5301 F UB Carp 

2309 Woo5304 F PF 11 Bass 

2322 DBW13Dl F UB Mite Sucker 

2322 DBW13D4 F PF Ln Bass 

2322 WW2604 L PF not available 

2326 DEWl7Dl F UB Udte Sucker 

2326 DBW17D4 F PF Rock Bass 

2328 DBWl9D4 F PF Chinwk Sahmn 

2329 DBW2W4 F PF Brow Trout 

2341 WDO6DOt F PF Lm Bass 

2341 WODtUlD3 F UB Carpsucker 

2355 DAW1603 F UB white Sucker 

2356 DA001702 F PF Lm Bars 

2356 DA001703 F UB mite Sucker 

2358 DA001001 F UP ns 

2369 DAW3202 F PF Lm Bass 

2369 DA003203 F UB %i te Sucker 

2369 90030387 1 UB llhite Sucker 

2375 DAW3802 F PF Pickcrel 

2375 DAW38D3 F UB Wlite Sucker 

2376 DA003903 F UB tiitt Swktr 

2376 aDlllU!% L UB Uhite Sucker 

2379 DEOD5404 F PF Lm Bass 

11.62 

0.31 

25.98 

1.77 

49.48 

34.50 

11.67 

3.2 

:41 

ND 

m 

E9 

5.76 

4.36 

6.56 

40.59 

2.32 

43.82 

ORNO 

ND 

QR NO 

OR Wo 

ND 

ND 

ND 

No 

ND 

ND 

&5 

No 

ND 

ND 

ORND 

ORND 

QR MD 

:43 

ND 

ORm 

QRND 

DR8 

m 

PR Wo 

ORnD 

ND 

ND 

ND 

ND 

OR ND 

ND 

9Rm 

PR 110 

ND 

ND 

ND 

ND 

ND 

ND 

LO 

ND 

No 

ND 

ORND 

ORm 

ORnD 

ND 

0.24 

m 

aRND 

QRD 

OR 26 

QR 2 

OR ND 

QRND 

QRND 

8.16 

ND 

ND 

ND 

0.39 

I.% 

4.31 

QR ND 

0.72 

?76 

4.57 

OR ND 

OR 1 

QR 1 

ND 

1.77 

ND 

OR ND 

QRND 

ORND 

1.11 

OR 24 

ORND 

ORND 

9R 3 

::: 

ND 

ORND 

PRND 

ND 

?Ol 

QR ND 

PR RD 

OR 1 

0.60 

II) 

9.50 

0.51 

0.64 

12.70 

9.12 

8.16 

m 

ND 

0.88 

3.61 

ND 

ORND 

M-7 
Episode SCC Type Description 2378 

2380 DEW5501 F M Carp 

2383 DE005801 F LIB Carp 

2385 DEOtXOO2 F W uhi te Sucker 

2385 40101987 1 YB Uhite Sucker 

2387 DE006201 F l&B Carp 

2394 DE006901 F UB Carp 

2397 DEW7201 F LIB Sucker 

2397 DEW7204 F PF UoLltye 

2410 DEW8501 F L1B Cwp 

2410 DE008504 F PF Sm Bass 

2416 DEW9101 F YB Carp 

2422 DE009702 F YB Carp 

2427 DE010202 F UB Carp 

2427 DE010203 F PF Walleye 

2427 a0102887 L PF Walteye 

2429 DE010402 F LIB Carp 

2429 DE010403 F PF WelLeve 

2429 Q)OlD687 1 PF Ysllc;e 

2430 DEOlQboz F PF northern Pike 

2430 DEOfO603 F W Redhorse Sucker 

2431 DE010702 F PF Brown Trout 

2431 DE010703 F LIB Sucker 

2432 DE010710 F LIB Redhorse Sucker 

2432 DE010713 F Pf Walleye 

2435 DE011001 F MB L-e Sucker 

2435 DEOllW4 F PF Brook Trout 

2437 DE011202 F PF Ualltye 

2437 DE011203 F UB Carp 

2439 DE011401 F UB Carp 

2439 DE011402 f UP Sm Bass 

2478 DJW3901 F BF Sucker 

2478 DJW3902 f UB Sucker 

2500 DC010201 F PF Bass 

2500 DC010203 F LIB Black Buffalo 

2532 DFO19302 F PF La Bass 

2532 DFOl9303 F UB Carp 

2544 OF019202 F UB Blacktail Redhorse 

2608 DEOlb501 F PF Udleye 

2608 DE014504 F UB Carp 

2618 DE015401 F YB Carp 

2618 DE01%02 F BF Carp 

2618 DE015403 F U9 OuiLLbck 

2618 PO102088 L W Quitlback 

2651 DBOO84Dl F LIB Witc Sucker 

11.29 

17.83 

32.69 

31.72 

ND 

4.2 

Im 

ND 

23.72 

0.44 

3.74 

3.92 

8.54 

0.33 

0.42 

5.56 

ND 

0.48 

ND 

ND 

ND 

1.70 

78 

ND 

ND 

ND 

ND 

2.23 

1.75 

ND 

ND 

10.40 

ND 

0.82 

6.00 

ND 

7.07 

67.18 

3.96 

1.64 

2.10 

1.73 

0.85 

DIOXIN I FURAN CDNCERTRATIDNS, fw/g 

12378 123478 123678 123789 1234678 2378 12378 23470 

PECDD ftXCDD HXWD HPCDD TCDF PECDF PECDF 

ND 

27.64 

0.62 

0.83 

ND 

11.8 

ND 

ND 

OR 25 

OR ND 

9.47 

3.54 

19.32 

ND 

ND 

QR 14 

ND 

ND 

ND 

PR NO 

NO 

0.51 

NO 

NO 

ND 

W 

ND 

ND 

9.42 

1.58 

ND 

ND 

OR ND 

OR ND 

0.56 

6.57 

NO 

L 

12.95 

4.76 

3.11 

3.13 

ND 

ND 

ND 

ND 

ND 

ND 

2.8 

ND 

ND 

OR NO 

OR ND 

ND 

0.30 

2.67 

No 

ND 

ORND 

ND 

ND 

ND 

QR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.83 

ND 

ND 

ND 

PRND 

OR ND 

ND 

0.91 

ND 

ND 

0.86 

1.48 

ND 

ND 

ND 

ND 

ND 

ND 

0.87 

0.83 

ND 

5.9 

ND 

ND 

ND 

PR ND 

ND 

1.19 

12.13 

ND 

ND 

ND 

ND 

ND 

ND 

r.47 

ND 

ND 

ND 

ND 

ND 

NO 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

1.85 

3.26 

ND 

ND 

ND 

3.7 

No 

ND 

QRND 

QR ND 

1.40 

0.39 

4.45 

ND 

ND 

‘JR ND 

ND 

ND 

ND 

QR NO 

ND 

E 

MD 

ND 

ND 

ND 

ND 

1.66 

NO 

ND 

nD 

QRND 

QR ND 

F% 

ND 

ND 

1.80 

2.73 

ND 

ND 

0.54 

ND 

OR 29 

OR 37 

2.03 

1.85 

3.39 

27.1 

1.34 

ND 

ORND 

ORND 

pR8 

10.67 

31.31 

0.35 

0.38 

OR 25 

ND 

0.88 

ND 

QR ISD 

ND 

1.42 

ND 

ND 

ND 

1.8 

1.4 

QR 4 

OR 21 

3.42 

4.66 

OR ND 

OR 1 

OR ND 

2.14 

20.34 

0.35 

0.43 

18.10 

22.49 

8.50 

9.37 

9.46 

QR ND 

5.51 

6.81 

75.29 

74.70 

1.36 

8.0 

0.89 

ND 

14.15 

1.00 

4.07 

8.80 

34.95 

5.76 

5.93 

5.66 

2.49 

2.59 

Lo 

3:&l 

0.93 

0.6 

f :: 

74 

MD 

2.32 

2.97 

ND 

ND 

1.07 

ND 

ra1 

E 

35.27 

9.18 

2.79 

a.33 

a.43 

2.19 

Y37 

3.87 

1.44 

1.82 

1.72 

No 

1.74 

4.47 

0.71 

0.68 

ND 

1.6 

ND 

Yl3 

ND 

1.87 

0.63 

9.08 

Ea 

ND 

ND 

ND 

ND 

ND 

0.41 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ii 

ND 

NO 

ND 

To7 

ND 

:L 

1.70 

z4 

0:86 

ND 

6.43 

15.19 

2.00 

1.95 

0.24 

5.6 

ND 

ii.78 

ND 

10.11 

1.47 

20.14 

ND 

ND 

0.51 

ND 

ND 

ND 

ND 

0.56 

NO 

ND 

NO 

1.3 

ND 

ND 

ND 

3.27 

1.36 

NO 

ND 

ND 

ND 

NO 

6.41 

ND 

0.15 

3.65 

5.05 

1 .a1 

2.25 

2.37 

ND 

123478 123678 123709 234670 1234678 1234709 DPE 

RXCDF* HXCDF 

9.07 ND 

:30 ND 

1.90 110 

ND ND 

1.3 2.7 

ND ND 

ii.26 :68 

ORM) PR ND 

1.85 1.03 

1.40 0.99 

5-M) 4.84 

0.40 ND 

0.50 ND 

OR ND PR ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND No 

ND ND 

Y-53 

ND 

0.58 

2.01 ND 

ND ND 

QR NO PR NO 

ND ND 

ND ND 

0.40 

4.91 !“,a 

ND ND 

ND ND 

2.98 ND 

1.14 1 .bl 

0.33 0.62 

ND ND 

No NO 

ND ND 

UXCDF HYCDF 

ND 3.89 

ND 7.80 

ND RD 

ND ND 

ND ND 

ND 0.9 

ND ND 

ND 

ND L 

PR ND OR ND 

ND UD 

ND 1.01 

ND 2.59 

m MD 

ND ND 

QR ND QR ND 

ND ND 

ND ND 

ND ND 

110 ND 

ND ND 

No NO 

ND ND 

No ND 

ND RD 

ND ND 

NO ND 

ND no 

ND ND 

ND 1.82 

NO ND 

QRND URND 

ND ND 

NO m 

ND ND 

ND 1.45 

ND ND 

No ND 

ND 1.18 

MD ND 

ND ND 

NO ND 

ND ND 

NLl ND 

RPCDF HPCDF 

OR 13 OR ND 

PR 16 QR ND 

1.10 ND 

0.86 ND 

0.30 ND 

1.7 ND 

ND ND 

ND ND 

DRND DRND 

ORND ORND 

OR ND PR ND 

2.84 ND 

4.23 ND 

0.23 ND 

ND ND 

OR 11 OR ND 

ND ND 

ND ND 

ND ND 

QR ND OR NO 

ND ND 

0.40 ND 

ND ND 

ND RD 

ND ND 

No ND 

ND ND 

OR ND OR ND 

DR6 OR RD 

2.85 ND 

ND ND 

PII ND OR ND 

QRND PR ND 

OR ND OR ND 

ND 

L ND 

0:1a ND 

0.20 ND 

2.33 ND 

1.51 ND 

0.51 ND 

0.89 ND 

0.95 ND 

OR ND OR ND 

TEC 

16.62 Y 

30.22 Y 

42.01 Y 

40.91 Y 

0.29 Y 

13.44 

0.10 

RD 

45.12 Y 

0.54 Y 

10.67 Y 

7.06 Y 

32.93 Y 

0.95 Y 

1.06 Y 

6.38 Y 

0.25 Y 

0.75 

0.: 

0.90 Y 

1.86 Y 

0.W 

1.00 

1.w Y 

0.02 

0.05 

ND Y 

6.00 Y 

3.33 Y 

0.05 

ND 

10.51 Y 

ND 

0.94 Y 

13.95 Y 

0.10 

7.92 

75.35 

11.65 

4.21 

5.42 

5.13 

1.07 
Episode SCC Type Description 

2653 08008503 F UB Carp 

2654 00008601 F UB Carp 

2709 DE005101 F UB Catiish 

2721 DA006502 F UB Sucker 

2722 DA006601 F UB Sucker 

2725 DA006301 F UB Sucker 

2748 DYOO6505 F UB Sucker 

2748 DY006506 F BF not available 

2776 DY007101 F UB Carp 

2776 DYOO7103 F PF Trout 

3001 DE019501 F PF Walleye 

3001 DE019502 F UB mite Sucker 

3022 DA008401 F UB Llhite Sucker 

3022 DA008402 F PF Chain Pickerel 

3023 DA008501 F PF Sm Bass 

3024 DA008601 F PF Lm Bass 

3025 DA008701 F W Mite Sucker 

3025 DA008702 F PF Chain Pickerel 

3026 DA009001 F UB Catfish 

3026 DA009002 F PF Lm Bass 

3027 DA009301 F UB Sucker 

3028 DA008801 F PF Chain Pickerel 

3028 PO031787 L PF Chain Pickerel 

3034 DG025701 F UB Carp 

3034 DGO25702 F PF Lm Bass 

3035 DG025801 F UB Carp 

3035 DG025802 F PF Sm Bass 

3036 DC025901 F PF Freshwater Drus 

3036 DG025902 F UB Carp 

3036 00120287 L PF Freshuater Drum 

3037 DC026001 F UB Carp 

3037 DC026002 F PF Black Crappie 

3038 DC026101 F UB Carp 

3038 DC026102 F BF Channel Catfish 

3039 DC026201 F UB Carp 

3039 DC026202 F BF Channel Catfish 

3040 DC026301 F UB Carp 

3040 DC026302 F PF Uhite Crappie 

3041 DC026401 F BF Channel Catfish 

3041 DG026402 F UB Carp 

3041 00031588 L BF Channel Catfish 

3042 DG026501 F UB Carp 

3042 DG026502 F PF Northern Pike 

3043 DC026601 F UB Carp 

2378 

TCDD 

12378 

PECDD 

2.82 1.08 

ND ND 

::.96 )1245 

ND 16.08 To2 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

!D37 !D54 

ND ND 

ND ND 

ND ND 

1.57 1.33 

~D3.11 :“27 

2.88 0.21 

ND ND 

ND ND 

ND NO 

1.17 0.66 

ND ND 

1.76 2.29 

ND ND 

ND ND 

ND 0.39 

ND 

0.39 !“38 

ND ND 

2.90 1.68 

0.63 ND 

1.54 1.95 

::02 ::67 

ND 

ND it)72 

I!“44 !:62 

ND 1.62 

ND ND 

0.47 ND 

123478 123678 

HXCDD HXCDD 

0.78 

ND 

OR ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

OR ND 

!“21 

ND 

ND 

ND 

ND 

ND 

No 

ND 

NO 

ND 

ND 

0.65 

ND 

1.11 

ND 

NO 

ND 

ND 

ND 

ND 

1.00 

PA4 

?I71 

ND 

ND 

0.21 

0.47 

0.63 

ND 

ND 

2.04 

ND 

OR ND 

8.43 

OR ND 

9.54 

ND 

ND 

ND 

ND 

PR ND 

ND 

ND 

ND 

ND 

ND 

10.76 

ND 

8.96 

ND 

ND 

ND 

ND 

1.69 

::33 

ND 

ND 

0.69 

NO 

0.57 

::21 

1.22 

3.86 

0.88 

8.78 

ND 

0.93 

0.38 

0.85 

4.20 

ND 

1.32 

DIOXIN / FURAN CONCENTRATIONS, w/g 

123789 1234678 2378 12378 23478 

HXCDD 

ND 

ND 

OR ND 

0.71 

OR NO 

0.89 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

r83 

ND 

NO 

ND 

ND 

0.49 

ND 

ND 

ND 

ND 

0.22 

ND 

ND 

ND 

0.72 

0.32 

0.86 

!“I3 

!“17 

:“18 

0.95 

ND 

ND 

HPCDD 

7.17 

ND 

OR 5 

4.49 

PR ND 

4.72 

ND 

QR 2 

ND 

ND 

OR ND 

OR ND 

0.72 

QR NO 

0.23 

PR ND 

OR 20 

0.98 

2.39 

0.28 

QR ND 

OR ND 

ND 

6.40 

ND 

4.41 

OR ND 

ND 

2.66 

ND 

1.25 

ND 

11.09 

1.81 

14.05 

2.13 

55.10 

0.50 

1.46 

1.71 

1.52 

OR 10 

0.20 

OR 3 

TCDF 

1.16 

0.36 

3.41 

207.49 

NO 

106.82 

ND 

ND 

ND 

ND 

ND 

ND 

6.21 

ND 

0.30 

0.90 

0.85 

ND 

8.25 

6.05 

1.93 

ND 

ND 

10.60 

0.30 

l-94 

ND 

ND 

0.38 

ND 

1.10 

ND 

1.78 

ND 

1.46 

!D71 

ND 

ND 

0.26 

0.21 

1.07 

ND 

0.45 

PECDF PECDF 

0.43 

ND 

ND 

4.87 

:“,I 

ND 

ND 

ND 

ND 

ND 

ND 

0.62 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.08 

T39 

ND 

ND 

ND 

NO 

ND 

ND 

0.50 

!!I!52 

ND 

ND 

ND 

NO 

ND 

!D35 

ND 

ND 

2.36 

ND 

4.03 

6.15 

ND 

6.19 

ND 

ND 

ND 

ND 

ND 

ND 

1.36 

ND 

ND 

ND 

ND 

ND 

6.24 

0.20 

ND 

ND 

NO 

1.28 

ND 

1.16 

ND 

ND 

ND 

ND 

ND 

ND 

1.13 

0.27 

1.36 

r66 

ND 

ND 

ND 

0.36 

0.70 

NO 

ND 

123478 

HXCDF’ 

1.40 

ND 

OR ND 

1.51 

QR ND 

1.58 

NO 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.76 

ND 

PR ND 

ND 

ND 

0.42 

ND 

1.60 

ND 

ND 

ND 

!“40 

ND 

1.30 

ND 

0.51 

!“91 

ND 

0.13 

!“29 

0.45 

ND 

0.38 

123678 

HXCOF 

ND 

ND 

PR ND 

ND 

PR ND 

0.50 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

QR ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

NO 

0.62 

ND 

0.76 

ND 

0.52 

ND 

ND 

ND 

ND 

0.37 

ND 

ND 

123789 

HXCDF 

ND 

ND 

OR ND 

ND 

PR ND 

ND 

NO 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

234678 

HXCDF 

1.27 

ND 

PR ND 

ND 

OR ND 

0.33 

ND 

m 

ND 

No 

OR ND 

ND 

ND 

ND 

ND 

No 

5.27 

:29 

ND 

QR ND 

ND 

L 

ND 

1.00 

ND 

No 

ND 

ND 

ND 

!!97 

!“29 

!:76 

ND 

ND 

ND 

0.26 

ND 

No 

0.25 

1234678 1234789 

HPCDF HPCOF 

1.70 ND 

ND ND 

PR ND OR ND 

2.05 ND 

PR ND OR ND 

2.48 ND 

ND ND 

OR ND QR ND 

ND NO 

ND ND 

OR ND PR ND 

OR ND OR ND 

0.15 ND 

OR ND OR ND 

ND ND 

PR ND QR ND 

OR 8 OR ND 

ND ND 

0.94 ND 

ND ND 

OR ND OR ND 

OR ND PR ND 

ND 

:ll ND 

ND NO 

1.07 ND 

OR ND QR ND 

ND ND 

ND ND 

NO ND 

0.34 ND 

ND NO 

1.70 ND 

0.39 ND 

1.25 ND 

ND ND 

1.36 ND 

ND 

::31 ND 

0.18 ND 

0.33 NO 

QR l PR ND 

ND ND 

PR ND QR ND 

DPE 

TEC 

5.32 Y 

0.04 Y 

2.36 Y 

67.38 Y 

ND 

32.48 Y 

ND 

ND 

ND 

ND 

ND 

2.z Y 

ND 

0.03 

0.09 

3.92 Y 

0.01 

29.31 Y 

3.69 

0.19 Y 

ND 

ND 

3.75 Y 

0.03 

4.36 Y 

ND 

ND Y 

0.35 Y 

ND Y 

0.80 Y 

5.2: Y 

0.94 Y 

4.23 

0.11 

8.40 Y 

ND 

0.50 Y 

0.10 Y 

1.17 Y 

1.94 Y 

ND 

0.71 Y 

04-9 
Episode SCC Type Description 

3043 DG026602 F PF Flathead Catfish 

3043 Poll1987 L PI: FIathead Catfish 

3044 DC026701 F UB Carp 

3044 DC026702 F PF Flathesd Catfish 

3045 DGO26BOl F UB Carp 

3045 OGO26802 F PF Flathead Catfish 

3046 DGO26901 F W BiBmouth BuffaLo 

3047 DGO27001 F UB Carp 

3047 DGO2?002 F PF Sm Bass 

3048 DC027101 F UB Carp 

3048 DC027102 F PF mite Bass 

3049 DGO27201 F UB Cam 

3049 DC027202 F PF Cm&e 

3049 QolllO87 L PF Crwie 

3050 DC027301 F UB BiBmouth Buffalo 

3060 DF009101 F UB Flathead Catfish 

3060 DfOO9102 F UB Sm Buffalo 

3061 DF019105 F PF Bass 

3061 OF019106 F UB Sucker 

3062 OF024024 F M Blue Catfish 

3062 DF024324 F BF Grass Carp 

3062 9DO24324 L BF Grass Carp 

3062 0071587 L UB Blue Catfish 

3062 SF024324 F BF Grass Carp 

3063 OF023301 F UB Sea Catfish 

3063 DF023302 F PF Spotted Seatrout 

3064 DF023305 N Shellfish 

3064 OF023306 F PF Spotted Seatrout 

3065 DFO23419 F BF Bigmouth Buffalo 

3065 DFO23420 F UB Flatheed Catfish 

3065 QoO22588 L YB Flathend Catfish 

3066 DFO23503 F UB Catfish 

3066 DF023504 F PF Freshwater Drun 

3068 DFO24LJOl M Oysters 

3068 DFO24002 F PF At\. Croaker 

3069 OF024007 F UB Sea Catfish 

3069 OF024008 F PF Trout 

3070 DF024009 F UB Croaker 

3070 OF024010 F PF Sheepshed 

3071 DF024014 F UB Carp 

3072 DFO24017 F UB Carp 

3072 OF024018 F PF llhite Bass 

3072 90040788 L PF mite Bass 

3073 DFOl9221 F UB White Sucker 

2378 12378 

TCOD PECOO 

0.31 

0.27 

0.82 

0.23 

2.40 

L 

1.29 

:"69 

ND 

7.49 

ND 

:92 

ND 

1.21 

0.62 

?A6 

8.85 

9.14 

32.36 

8.99 

1.50 

ND 

ND 

ND 

1.83 

1.78 

1.79 

4.62 

No 

6.70 

ND 

0.72 

ND 

!!69 

1.07 

ND 

No 

No 

0.30 

0.21 

No 

1.09 

NO 

No 

0.42 

ND 

1.46 

:"% 

::80 

ND 

ND 

ND 

ND 

No 

1.13 

3.68 

1.21 

ND 

No 

1.17 

ND 

1.57 

ND 

ND 

ND 

0.53 

0.68 

0.67 

ND 

ND 

ND 

No 

0.81 

ND 

ND 

ND 

0.69 

ND 

ND 

ND 

No 

123478 123678 

ND 

ND 

0.68 

ND 

OR NO 

ND 

ND 

1.14 

ND 

2.26 

No 

1.79 

ND 

r40 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

0.29 

0.44 

0.71 

No 

ND 

ND 

ND 

ND 

El9 

ND 

ND 

ND 

ND 

ND 

0.39 

0.24 

ND 

0.58 

OR 4 

1.26 

0.39 

2.92 

ND 

12.37 

ND 

5.55 

ND 

ii"54 

No 

ND 

1.98 

7.94 

1.28 

ND 

ND 

1.50 

ND 

1.65 

ND 

0.26 

r86 

0.57 

0.50 

2.43 

ND 

!"49 

0.82 

ND 

0.59 

ND 

2.09 

ND 

ND 

DIOXIN / FLIRAN CONCENTRAT1ONS. W/9 

1237B9 -1234678 2378 23478 

HXCDD PPCDD TCDF 

12378 

PECDF PECDF HXCDF’ HXCDF HXCDF HXCDF HPCDF HPCDF TEC 

ND 

L 

ND 

OR ND 

ND 

No 

No 

No 

ND 

ND 

1.09 

No 

No 

ND 

ND 

ND 

1.29 

ND 

ND 

ND 

ND 

ND 

ND 

0.46 

ND 

ND 

iD30 

ND 

ND 

0.77 

ND 

ND 

ND 

ND 

ND 

0.33 

ND 

ND 

No 

No 

ND 

No 

1.07 

0.56 

7.76 

2.03 

OR 15 

2.73 

2.44 

10.76 

0.32 

PR 29 

OR ND 

25.93 

No 

No 

2.69 

OR ND 

OR ND 

5.22 

OR 15 

3.84 

2.51 

2.71 

3.72 

1.96 

3.70 

F45 

1.46 

2.50 

2.03 

1.97 

11.11 

0.85 

0.89 

ND 

1.80 

0.21 

2.46 

1.44 

4.95 

0.54 

0.25 

0.25 

0.94 

0.15 

E?9 

ND 

ND 

i"85 

3.10 

ND 

4.66 

0.51 

2.44 

0.16 

:15 

No 

4.20 

ND 

ii.07 

69.82 

69.29 

33.8 

71.92 

1.20 

1.51 

0.47 

ND 

0.18 

5.09 

4.93 

4.58 

0.28 

14.13 

1.38 

ND 

ND 

0.71 

0.31 

3.11 

0.52 

0.26 

0.30 

1.46 

ND 

ND 

0.29 

ND 

0.27 

ND 

ND 

0.64 

ND 

ND 

ND 

ND 

ND 

L9 

ND 

ND 

!!27 

0.64 

ND 

0.30 

0.61 

No 

1.09 

2.52 

ND 

ND 

ND 

0.69 

0.72 

1.31 

NO 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

No 

ND 

NO 

T47 

0.18 

ND 

ND 

No 

0.92 

::46 

ND 

2.20 

ND 

ND 

ND 

::48 

No 

::57 

0.78 

0.57 

ND 

0.50 

5.73 

ND 

ND 

r66 

1.06 

0.99 

3.09 

ND 

ND 

ND 

1.07 

ND 

ND 

ND 

1.56 

ND 

ND 

ND 

0.14 

123478 123678 123789 234678 1234678 1234789 DPE 

0.40 

w 

1.30 

No 

OR1 

No 

No 

0.85 

No 

1.65 

:65 

No 

No 

No 

ND 

No 

0.27 

ND 

1.06 

ND 

ND 

1.14 

:52 

2.00 

No 

No 

No 

0.53 

0.62 

2.05 

ND 

ND 

ND 

ND 

ND 

No 

!:42 

ND 

No 

No 

No 

No 

ND 

No 

No 

ORNO 

No 

No 

No 

No 

No 

No 

No 

No 

No 

No 

No 

ND 

No 

No 

No 

No 

ND 

No 

r31 

0.32 

No 

ND 

No 

No 

No 

0.73 

No 

No 

No 

No 

No 

ND 

!D51 

ND 

No 

No 

ND 

NO 

ND 

No 

No 

OR ND 

ND 

ND 

No 

ND 

No 

No 

No 

ND 

ND 

No 

ND 

ND 

ND 

No 

No 

ND 

ND 

w 

No 

ND 

No 

ND 

ND 

No 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

ND 

No 

No 

ND 

No 

ND 

No 

w 

No 

No 

OR 0 

No 

No 

0.37 

No 

No 

No 

1.86 

ND 

No 

1.44 

ND 

No 

:42 

NO 

ND 

ND 

No 

ND 

ND 

No 

No 

No 

ND 

0.22 

r74 

ND 

No 

No 

No 

No 

No 

No 

0.25 

ND 

No 

ND 

No 

0.68 ND 

No ND 

1.18 NO 

0.34 No 

OR ND OR ND 

No No 

No ND 

1.02 No 

No No 

ORND OR ND 

URN0 PR ND 

3.34 No 

No No 

w No 

1.71 ND 

OR ND OR ND 

9Rw ORND 

0.23 ND 

OR 1 OR ND 

No No 

No No 

ND 

r40 No 

No Nfl 

4.09 ND 

2.41 NO 

0.35 ND 

0.18 ND 

0.27 ND 

0.33 No 

0.36 110 

1.35 w 

No No 

No No 

No w 

0.21 No 

No No 

0.17 No 

0.55 ND 

0.55 No 

w LID 

No No 

w 

r20 ND 

0.53 Y 

0.30 Y 

2.02 Y 

0.40 Y 

2.41 Y 

0.36 Y 

0.81 

3.47 Y 

No 

7.99 Y 

0.05 

11.82 

0.02 

1.: 

ND 

1.87 Y 

1.59 Y 

2.69 

39.76 Y 

16.25 

16.40 

36.66 

16.24 

6.00 Y 

0.53 Y 

0.11 

0.02 Y 

2.59 

3.3a Y 

3.33 r 

7.56 Y 

0.04 

8.12 

0.19 

1.76 Y 

ND 

0.19 Y 

0.76 

2.89 Y 

0.06 

0.03 

0.03 

0.57 Y 

04-10 
Episode SCC Type Description 

3073 DF019222 F PF Sm Bass 

3073 PO121587 L UB white Sucker 

3074 OF026017 F PF Brown Trout 

3075 DF024102 F BF Sea Catfish 

3076 DF028502 F UB Channel Catfish 

3076 OF028503 F PF Spotted Bass 

3077 DFO19113 F PF Flathead Catfish 

3077 DFOl9114 F VB Rcdhorse Sucker 

3077 PO121087 1 PF Flathead Catfish 

3078 OF009118 F UB Carp 

3078 DFO23815 F UB Sm Buffalo 

3078 OF023816 F PF Black Crappie 

3078 SF009118 F UB Carp 

3079 DF019205 F PF Uhite Bass 

3079 DFOl9206 F UB Carp 

3080 DF023317 F UB Carp 

3080 DF023318 F PF Lm Bass 

3080 a0040987 L UB Carp 

3081 OF024105 F PF Uhite Bass 

3081 DF024106 F UB Catfish 

3082 DFO23401 F IdB Carp 

3082 OF023402 F PF Lm Bass 

3082 (10120787 L PF Lm Bass 

3083 OF023405 F UB Black Bullhead 

3083 OF023406 F PF Lm Bass 

3044 OF024109 F UB Channel Catfish 

3084 00072188 L bB Charnel Catfish 

3085 OF024113 F UB Sea Catfish 

3085 OF024114 F PF Black Drun 

3085 SF024113 F UB Sea Catfish 

3086 OF023409 F UB Catfish 

3086 OF023411 F PF Black Drun 

3087 OF023413 F UB Carp 

3087 DF023414 F PF tiite Crappie 

3087 DF023415 F Up Blueaill 

3087 bF023416 F Yp Lm B&i 

3087 IX1023414 L PF Uhite Crappie 

3087 Q)O72387 L UB Carp ” 

3087 SF023414 F PF White Crappie 

3087 SF023415 F UP Bluegill 

3088 OF023417 F UB Chamel Catfish 

308B DFO23418 F PF Bluegill 

3089 DFOl92W F PF Uhite Crappie 

30!39 of019210 F UB Carp 

2378 

Tam 

12378 

PECDD 

:30 :25 

ND OR ND 

ND 

0.39 ::63 

ND ND 

ND ND 

ND ND 

ND 17.91 :35 

203.64 12.62 

23.10 ND 

15.41 3.07 

ND 

k4 ND 

3.62 2.64 

1.03 ND 

3.35 3.31 

0.94 ND 

2.45 ND 

ND 1.02 

ND ND 

ND ND 

ND 0.80 

ND ND 

1.28 0.96 

1.07 0.86 

2.58 6.82 

0.66 273ItDO 

ND 2:w 

ND 117.89 ?24 

13.11 0.79 

66.70 1.93 

20.22 ND 

16.79 1.21 

114.34 7.28 

14.30 1.00 

n.98 1.91 

13.69 W 

1.4 ND 

ND ND 

ND ND 

123478 123678 

HXCDD HXCDD 

ND 

0.24 

OR ND 

:63 

ND 

ND 

ND 

ND 

2.43 

1.50 

PO0 

ND 

ND 

1.92 

:18 

ND 

1.44 

ND 

ND 

ND 

0.49 

ND 

ND 

L 

NO 

4.38 

0.82 

ND 

ND 

ND 

ND 

ND 

ND 

1.94 

ND 

ND 

ND 

ND 

ND 

ND 

!:46 

OR ND 

ND 

1.47 

ND 

ND 

ND 

:“13 

2146 

?08 

NO 

0.52 

4.88 

0.25 

6.58 

0.47 

2.20 

2.52 

ND 

ND 

0.91 

ND 

ND 

0.94 

10.50 

1.77 

11.85 

2.47 

ND 

5.88 

ND 

1.92 

ND 

0.50 

6.38 

ND 

1.24 

1.25 

ND 

ND 

0.4 

DIDXIN / FURAN CWCENTRATICUS, w/g 

123789 1234678 2378 12378 23478 12347B 

HXCDD 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.51 

0.49 

L 

ND 

ND 

1.87 

ND 

2.14 

E8 

0.40 

ND 

740 

ND 

ND 

0.31 

2.18 

::51 

ND 

ND 

2.11 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

0.57 

ND 

ND 

ND 

HPCDD 

0.19 

1.11 

OR ND 

0.51 

2.01 

0.35 

0.47 

0.75 

0.89 

27.86 

6.07 

2.14 

25.96 

0.37 

1.46 

23.95 

ND 

29.65 

1.56 

7.86 

12.89 

1.44 

0.37 

10.74 

ND 

1.83 

1.59 

9.41 

1.06 

11.05 

3.72 

ND 

12.33 

ND 

52 

0.94 

12.33 

0.46 

1.24 

4.92 

0.5 

ND 

1.4 

TCDF 

0.33 

1.27 

ND 

::24 

ND 

ND 

ND 

ND 

8.87 

21.23 

12.41 

7.23 

1.08 

0.61 

4.89 

ND 

6.95 

0.80 

?.83 

0.97 

0.99 

0.32 

ND 

0.51 

0.53 

4.62 

14.77 

5.15 

4.04 

0.32 

261.34 

81.40 

71.94 

8.74 

110.71 

253.01 

107.66 

68.81 

7.65 

2.2 

0.40 

1.4 

PECDF PECDF HXCDF* 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.51 

!“44 

ND 

0.14 

ND 

ND 

0.32 

ND 

ND 

0.88 

ND 

ND 

ND 

ND 

ND 

0.33 

7.59 

20.30 

8.75 

2.60 

0.25 

8.80 

1.65 

2.09 

:“28 

8.74 

1.67 

1.73 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND OR ND 

ND 

!D44 ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.05 

0.70 :41 

ND 

!“91 ND 

0.2032 !D30 

0.47 0.38 

ND ND 

0.75 0.54 

ND ND 

0.26 

ND !-!40 

ND ND 

ND 

?15 ND 

ND ND 

1.01 

0.92 :I8 

45.51 11.92 

11.25 6.65 

56.85 13.74 

33.25 19.98 

ND ND 

17.24 0.40 

2.46 ND 

1.59 ND 

2.09 ND 

3.21 ND 

18.36 ND 

1.92 ND 

1.40 ND 

ND ND 

ND ND 

ND ND 

0.3 ND 

f2367B 

HXCDF 

ND 

w 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

w 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

NO 

16.21 

8.19 

20.67 

ND 

ND 

1.49 

ND 

ND 

ND 

ND 

1.60 

ND 

NO 

ND 

ND 

NO 

ND 

123789 234678 1234678 1234789 DPE 

HXCDF 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.96 

ND 

1.41 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

w 

ND 

ND 

ND 

HXCDF HPCDF 

ND ND 

ND ND 

OR ND OR ND 

:61 ?58 

ND 0.18 

ND ND 

ND ND 

NO ND 

ND 0.23 

ND ND 

ND ND 

ND ND 

:“,I, :27 

0.38 0.59 

:49 ND 1.22 

ND 

ND :23 

ND 1.16 

NO ND 

ND 0.18 

ND ND 

ND ND 

ND 

E9 

1:08 

8.20 :21 

1.45 

7.01 8.95 

2.48 25.66 

ND 

I?54 ND 

ND ND 

ND ND 

ND ND 

ND 

0.53 L 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND 0.2 

HPCDF 

ND 

ND 

PR ND 

TEC 

0.03 

0.63 Y 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.26 

0.19 

1.49 

ND 

ND 

ND 

ND 

ND 

ND 

Ho 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

0.01 

1.25 Y 

0.01 Y 

ND 

0.01 Y 

0.01 

22.18 

213.05 Y 

24.36 ‘I 

18.06 

0.21 Y 

0.69 Y 

6.85 ‘I 

1.05 

7.59 Y 

1.08 

3.11 

1.41 Y 

0.11 Y 

0.10 Y 

0.79 Y 

2.2 

2.19 

34.85 Y 

10.57 

15.01 

21.52 Y 

0.04 

157.87 

22.98 

75.95 

22.17 

30.24 

154.07 

25.93 

82.18 

14.69 

1.63 

0.04 

0.35 Y 

LW-1X 
Episode SCC Type Oescriptian 

3WO DF019213 F PF Uhitc Crappie 

3090 OF019214 F UB Channel Catfish 

3091 OF019217 F UB River Carpsucker 

3091 OF019218 F PF Uhite Crappie 

3092 DFO23501 F UB Care 

3092 DFO23502 F PF Ua&th 

3093 OF024011 F PF Lm Bass 

3093 OF024118 F UB Sm Buffalo 

3093 PO080387 L UB Sm Buffalo 

3094 DC017201 F BF Channel Catfish 

3094 POW2988 L BF Chamel Catfish 

3095 DC038801 F BF Brown Bullhed 

3095 DC038802 F UB Charnel Catfish 

3096 DC035001 F BF Brow Bul I head 

3096 DC035002 F UB Chamel Catfish 

3096 C1D05248B L UB Chstnel Cotfish 

3097 DC038701 F BF Brown Bullhead 

3097 DC038702 F UB Carp 

3098 DC038601 F UB Uhite Sucker 

3098 DC038602 F PF Amsricrn Eel 

3098 PO032587 L UB Mite Sucker 

3100 DCO197Dl F PF Uhite Perch 

3100 DC019702 F UP Yinter Flouder 

3101 DC019901 F PF Brow Trout 

3103 DC036201 F UB Chamel Catfish 

3103 DC036202 F UB Carp 

3lD4 DC020001 F PF Ln Bass 

3104 DC020002 F UB Carp 

3105 OF025001 F UB Can, 

3105 DFO25002 F PF Lm bass 

3106 DE026801 F PF Uallwe 

3lW DE026802 F PF Uhite-Bass 

3107 DE026901 F UB Carp 

3108 DE027001 F Pf Ualleye 

3108 DE027002 F UB Carp 

3109 DE025001 F UB Carp 

31 W DE025002 F PF SRI Bass 

3110 DE022501 F BF Carp 

3111 OH015801 F PF UaIbye 

3111 OH015802 F UB Silver Rcdhorse 

3112 DE022401 F UB CarD 

3112 DE022402 F PF Ualieye 

3113 DE021101 F BF Channel Catfish 

3113 DE021102 F BF Carp 

2378 

TCDD 

ND 

ND 

ND 

:“ll 

ND 

r41 

ND 

1.71 

1.69 

1.24 

ND 

0.53 

4.62 

4.53 

0.81 

1.42 

24.89 

3.32 

24.02 

ND 

ND 

ND 

E% 

ND 

1.68 

0.73 

?02 

17.52 

ND 

ND 

2.68 

0.50 

0.35 

ND 

ND 

%tl 

ND 

ND 

1.49 

12378 

PECDD 

FL 

NO 

i?W 

ND 

?rn 

0.68 

2.16 

2.08 

1.23 

ND 

::33 

4.84 

:“27 

27.23 

12.46 

25.09 

0.50 

ND 

ND 

OR 2 

ND 

ND 

ND 

0.30 

ND 

Es4 

0.99 

:“W 

0.42 

ND 

0.38 

ND 

ND 

1.38 

DIOXIN / FURAN COIICENTRATIOWS. cd9 

123478 123678 123789 1234678 2378 

HXCDD HXCDD HXCDO HPCDCJ TCDF 

ND 

ND 

ND 

!D94 

ND 

ND 

0.49 

0.63 

ND 

ND 

ND 

ND 

ND 

ND 

1.10 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

r84 

0.67 

NO 

1.01 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.34 

ND 

ND 

1.12 

ND 

ND 

ND 

ND ND 

0.55 NO 

ND ND 

ND 

14.18 SD59 

ND ND 

ND ND 

1.90 0.51 

1.45 0.53 

2.1650 :33 

1.67 

4.72 r91 

0.43 ND 

5.32 ND 

4.95 1.01 

::23 0.88 ND 

7.00 6.80 

8.43 3.21 

7.14 5.90 

0.56 ND 

ND ND 

::84 ND 0.67 

0.99 ND 

!“19 

ND 

0.42 

ND ND 

ND 

!!25 ND 

::41 ND 

ND ND 

14.39 1.05 

0.74 ND 

ND ND 

1.35 0.15 

::48 ND 

2.79 1.25 

ND 

:“25 ND 

5.77 ND 

ND 0.71 

2.04 0.39 

0.49 ND 

ND 106.84 :41 

0.87 ND 

1.41 ND 

6.97 769!!55 

5.33 0.60 

6.00 0.51 

3.10 2.31 

5.70 0.86 

0.76 0.97 

4.39 0.71 

4.08 0.77 

OR ND 1.42 

ND 4.62 

27.39 5.03 

6.20 NO 

OR 26 5.18 

1.31 3.10 

1.26 2.91 

:“B7 5.49 ND 

3.76 5.72 

0.87 0.39 

5.11 2.66 

1.70 1.23 

0.53 1.32 :22 

1.43 26.57 

7.49 2.66 

ND 0.36 

42.22 2.73 

1.21 ND 

ND 1.01 

2.64 8.84 

ND ND 

:“W 5.50 142

0.26 1.01 

2.89 0.94 

14.78 3.60 

. .- 

123711 23478 

PECDF ~EcDF 

ND 

0.19 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.35 

O.TI 

:67 

0.66 

ND 

2.96 

ND 

ND 

NO 

0.69 

ND 

1.85 

0.29 

0.76 

ND 

1.69 

ND 

NO 

ND 

0.w 

0.35 

ND 

1.34 

ND 

ND 

0.74 

ND 

ND 

ND 

ND 

ND 

2.03 

Es 

ND 

ND 

ND 

ND 

ND 

ND 

0.18 

4.84 

3.58 

4.29 

9.89 

0.92 

14.01 

11.85 

2.91 

7.53 

0.92 

NO 

0.w 

2.43 

1.12 

5.92 

3.06 

1.90 

:511 

0.33 

ND 

ND 

ND 

1.55 

::44 

ND 

ND 

1.41 

ND 

ND 

ND 

ND 

1.39 

3.04 

123478 123678 123789 234678 1234678 1234789 WE 

llXCDF* HXCDF 

ND 

ND 

ND 

ND 

ND 

ND 

YD 

1.49 

ND 

0.24 

0.24 

0.49 

2.26 

ND 

2.60 

2.42 

ND 

2.92 

ND 

ND 

!“19 

ND 

ND 

1.46 

0.50 

ET1 

0.30 

ND 

ND 

ND 

ND 

ND 

7.32 

1 .Ol 

ND 

1.44 

ND 

NO 

ND 

ND 

ND 

2.30 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.63 

0.48 

0.75 

ND 

ND 

ND 

1.51 

::63 

ND 

ND 

ND 

ND 

ND 

ND 

0.31 

ND 

ND 

1.00 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

2.52 

HXWF 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.41 

ND 

ND 

ND 

ND 

ND 

ND 

:44 

ND 

ND 

ND 

NXCDF HPCDF WPCDF 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

0.23 

0.30 

ND 

ND 

1.49 

1.24 

ND 

0.53 

ND 

0.88 

1.39 

ND 

ND 

ND 

1.09 

0.31 

ND 

0.38 

ND 

ND 

ND 

ND 

2.77 

?.61 

0.60 

::36 

ND 

ND 

ND 

ND 

ND 

0.29 

ND ND 

ND 

&2 ND 

NO ND 

2.31 ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.53 ND 

0.47 ND 

0.26 ND 

ND ND 

ND ND 

ND ND 

ND ND 

PR ND PR ND 

1.71 ND 

2.66 NO 

1.45 ND 

PR 3 PR ND 

ND ND 

0.19 NO 

ND ND 

0.92 ND 

0.42 ND 

ND ND 

0.61 ND 

0.37 ND 

0.53 ND 

0.19 NO 

0.42 ND 

3.46 ND 

ND NO 

13.16 0.39 

0.94 ND 

ND ND 

0.49 ND 

ND NO 

ND ND 

1.32 ND 

ND ND 

ND 

:“OO ND 

TEC 

0.07 

0.68 Y 

0.01 Y 

ND 

9.71 Y 

0.01 

0.01 

1.27 Y 

0.82 Y 

5.63 

5.01 

4.65 

5.92 Y 

1.14 

15.38 Y 

14.25 Y 

2.41 Y 

7.97 Y 

41.15 Y 

10.88 Y 

39.02 Y 

1.96 

0.87 

3.60 

2.31 Y 

2.Bl Y 

0.05 

4.71 

1.22 Y 

0.01 Y 

7.BB Y 

20.51 Y 

2.32 Y 

0.04 Y 

10.18 Y 

0.97 Y 

0.45 

2.21 Y 

ND 

0.29 Y 

4.85 Y 

0.10 Y 

1.43 

5.59 
Episode SCC Type Description 

3114 DE021201 F BF Carp 

3115 DE021301 F UB Carp 

3115 DE021302 F BF Catfish 

3117 0E021501 F PF Lake Trout 

3117 DE021502 F PF Brown Trout 

3118 DE021601 F PF UaIleye 

3118 DE021602 F UB Carp 

3118 DE021603 F UB Carp 

3118 SE021602 F b/B Carp 

3119 DE021701 F UB Carp 

3119 DE021702 F PF Lm Bass 

3120 DE021801 F UB Carp 

3120 DE021802 F PF Bass 

3122 DE022001 F UB Carp 

3122 DE022003 F UB Redhorse Sucker 

3122 DE022004 F PF Sm Bass 

3125 DE022301 F UB Carp 

3125 DE022302 F PF Uhite Bass 

3125 OD120888 L PF Uhite Bass 

3132 DE023201 F UB Carp 

3132 DE023202 F UB Channel Catfish 

3134 DE023401 F PF Crappie 

3134 DE023403 F UB Carp 

3134 DE023405 F b/B Carp 

3134 DE023406 F UB Sucker 

3135 DE023501 F UB Carp 

3136 DE023602 F PF Ualleye 

3137 DE023701 F UB Redhorse Sucker 

3137 DE023702 F PF Ualleye 

3138 DE023801 F UB Carp 

3138 DE023802 F PF Sm Bass 

3140 DE024002 F UB Carp 

3141 DE024102 F UB Carp 

3141 DE024103 F PF Northern Pike 

3141 SE024102 F UB Carp 

3142 DE022502 F UB Carp 

3143 DE024401 F Rotten (catf) 

3143 DE024402 F PF Uhite Bass 

3143 DE024403 F UB Carp 

3144 DE024901 F UB Carp 

3145 DE026601 F UB N. Redhorse 

3145 00071988 1 UB N. Re&orse 

3146 DE026701 F UB Carp 

3146 DE026702 F PF Ualieye 

2378 12378 

TCDD PEWD 

0.72 ND 

7.00 1.84 

6.24 0.91 

3.74 8.76 

ND 2.35 

1.37 11.61 :022 

3.85 1.01 

9.39 2.22 

!!30 No 0 59 

3.07 ND 

0.73 21.01 ?22 

1.36 No 

1.37 ND 

2.15 1.43 

0.41 ND 

0.29 ND 

8.58 2.19 

14.75 2.48 

0.16 ND 

ND 0.53 

1.99 1.14 

0.59 ND 

1.22 ND 

ND ND 

NO ND 

ND ND 

4.99 OR 2 

ND ND 

1.50 ND 

20.31 22.39 

1.70 OR 1 

16.79 17.14 

2.72 5.68 

ND ND 

::91 ;:58 

1.25 0.51 

0.86 ND 

0.78 0.33 

4.56 2.78 

0.24 ND 

123478 123678 123789 1234678 2378 12378 

DIOXIN / FURAN CCMCENTRATIDNS, m/g 

23478 123478 123678 

HXWD HXCDD HXCDD HPCDD TCDF PECOF PECDF HXCOF’ HXCDF HXCOF HXCDF HPCDF HPCDF TEC 

ND 

ND 

ND 

ND 

ND 

ND 

0.69 

0.53 

0.70 

NO 

ND 

0.40 

ND 

0.96 

ND 

ND 

1.04 

ND 

k4 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

:"98 

2.34 

ND 

53 

ND 

ND 

ND 

1.87 

ND 

1.18 ND 

7.18 0.84 

3.82 0.70 

5.97 ND 

1.41 ND 

ND 

:"87 ND 

1.30 ND 

2.37 ND 

1.63 ND 

ND 

:"4, ND 

ND ND 

10.13 0.40 

ND ND 

:053 ND 

ND ND 

ND 

5.41 :92 

12.20 2:68 

ND 

?48 ND 

1.16 ND 

ND ND 

1.25 ND 

ND ND 

NO ND 

NO ND 

OR ND OR ND 

0.31 ND 

1.77 

18.52 :003 

0.87 17.26 :!54 

8.14 0.90 

ND ND 

2"74 

ND 

0.96 

0170 r96 

ND 

ND 

4.61 

39.51 

11.94 

0.98 

2.00 

ND 

4.64 

4.11 

0.87 

43.70 

4.42 

3.51 

3.32 

3.64 

ND 

0.54 

ND 

14.86 

OR ND 

OR 0 

8.19 

2.03 

1.30 

OR 7 

4.91 

ND 

1.83 

3.20 

0.58 

3.67 

ND 

0.78 

ND 

OR ND 

1.25 

4.87 

43.71 

2.12 

37.99 

10.35 

3.11 

0.62 

9.55 

5.55 

14.64 

7.53 

12.46 

0.89 

2.35 

3.34 

2.08 

16.91 

8.80 

3.95 

23.36 

7.87 

7.36 

5.63 

6.13 

0.90 

6.71 

1.75 

32.60 

3.w 

ND 

10.63 

ND 

4.30 

1.80 

1.28 

2.91 

OR 9 

0.55 

0.66 

ND 

12.69 

ND 

ND 

1.60 

0.89 

1.35 

ND 

ND 

0.38 

ND 

ND 

ND 

Y.30 

ND 

ND 

ND 

ND 

ND 

1.61 

0.76 

1.29 

NO 

ND 

ND 

ND 

OR 1 

ND 

ND 

2.59 

0.74 

2.07 

4.35 

ND 

0.45 

2.74 

0.38 

0.22 

ND 

1.12 

ND 

0.71 ND 

2.41 0.82 

1.65 ND 

25.28 2.44 

2.49 ND 

0.66 ND 

4.33 ND 

2.14 1.17 

3.86 0.29 

ND ND 

ND ND 

1.22 0.29 

ND 14.30 56 

0.20 ND 

:061 ND 1.49 

:46 ND 

6.09 Y12 

3.27 2:50 

ND ND 

7.16 0.76 

10.68 0.40 

4.37 ND 

ND ND 

ND ND 

ND ND 

ND ND 

OR ND OR ND 

0.40 ND 

1.08 

20.21 ;!I6 

1.94 ND 

15.68 3.02 

14.85 1.65 

ND ND 

0.26 ND 

2.54 1.20 

1.90 ND 

0.47 ND 

0.35 ND 

2.76 1.17 

NO ND 

ND 

ND 

ND 

4.14 

ND 

ND 

0.65 

0.44 

0.40 

ND 

ND 

ND 

ND 

1.49 

ND 

ND 

1.18 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

5.79 

:"81 

2.38 

ND 

ND 

ND 

ND 

ND 

ND 

1.76 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

1.26 

C?38 

ND 

ND 

ND 

0.20 

ND 

0.24 

ND 

1.97 

ND 

ND 

ND 

ND 

ND 

1.35 

2.61 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

13.68 “,:: 

ND ND 

20.56 

2.43 

1.22 

1.48 

47.38 

0.88 

2.48 

16.96 

1.82 

2.66 

12.10 

2.05 

15.11 

14.76 

10.22 

0.93 

OR ND OR ND 

ND ND 

ND ND 

ND 1.69 

ND ND 

ND 1.65 

ND 0.80 

ND ND 

ND ND 

NO 1.07 

ND ND 

ND ND 

ND ND 

ND 0.62 

ND ND 

I&2 

NO 

ND 

ND 

NO 

0.50 

0.77 

0.35 

ND 

ND 

0.41 

ND 

1.71 

OR ND 

OR ND 

0.82 

ND 

ND 

1.01 

2.52 

ND 

ND 

ND 

L 

ND 

ND 

ND 

OR ND 

ND 

:T126 

0.16 

4.31 

0.95 

ND 

ND 

4.19 

ND 

ND 

ND 

3.55 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

OR ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

OR ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

1.73 

10.88 

8.18 

27.16 

3.54 

2.29 Y 

16.90 

6.61 Y 

12.40 

0.60 Y 

2.53 Y 

4.38 Y 

0.94 Y 

35.03 Y 

2.34 Y 

1.76 

7.84 Y 

1.22 

1.27 

14.34 Y 

20.31 Y 

0.25 

4.74 

8.30 

6.11 

1.79 

ND 

1.07 

5.:: 

0.42 

2.39 

45.94 

2.82 

28.50 

16.63 

0.21 

0.42 Y 

5.93 Y 

2.70 

2.73 

2.68 

10.83 Y 

0.34 

123789 234678 1234678 1234789 DPE 

D4I3 
Episode SCC Type Description 2378 

TWO 

5.02 

4.31 

2.49 

3.46 

ND 

ND 

13.51 

7.87 

0.89 

8.20 

7.82 

ND 

1.52 

2.86 

5.04 

ND 

?43 

6.61 

10.79 

5.44 

ND 

1.51 

5.67 

r.66 

ND 

1.53 

0.48 

ND 

:D22 

713 

2.83 

6.72 

8.84 

2.30 

7.88 

ND 

ND 

ND 

1.40 

0.15 

ND 

010X11 / FURAN COWCENlRAllOWS, w/g 

12378 123478 123678 123789 1234678 2378 12378 23478 123478 123678 123789 234678 1234678 12347B9 DPE 

PEW0 HXWD HXWD HXWD HPCDD TWF PEWF PECDF HXWF' HXWF HXWF HXWF HPWF HPWF TEC 

3.44 

2.92 ::53 

0.52 ND 

2.42 1.17 

ND ND 

ND OR ND 

12.01 2.01 

2.89 ND 

ND ND 

2.95 ND 

0.4073 LB 

2.68 2.11 

4.61 W 

ND ND 

ND ND 

ND ND 

4.72 10.17 ?46 

15.90 4.89 

6.43 ND 

0.94 ND 

1.21 ND 

6.10 ND 

OR ND ND 

9.94 ND 

ND 

5.07 ?.52 

ND ND 

ND ND 

:59 ND 

11.5 14.3 

4.44 1.88 

11.01 11.80 

2.60 3.64 

ND 

2.56 :085 

ND Pi ND 

ND 0.39 

ND ND 

OR 1 1.63 

ND ND 

ND ND 

17.34 2.30 

14.27 1.89 

0.70 ND 

2.89 0.62 

ND ND 

OR ND OR ND 

9.25 3.92 

1.85 1.19 

ND ND 

2.15 0.59 

3.20 ND 

1.50 0.25 

3.13 0.38 

6.59 ND 

2.17 ND 

ND ND 

:58 L?# 

26.28 5.10 

34.02 6.67 

27.72 ND 

2.22 ND 

2.30 17.82 :67 

1.93 0.22 

24.87 3.53 

2.92 ND 

12.40 ND 

3.09 ND 

ND ND 

0.40 ND 

6.40 37.3Es 

7.28 

44.20 ?87 

1O.W 1.35 

ND ND 

9.51 ND 

OR ND OR ND 

0.89 0.28 

ND 

3.09 IL6 

ND ND 

ND ND 

49.70 

47.34 

2.w 

5.59 

0.57 

ND 

16.10 

3.13 

:25 

0.50 

2.14 

8.54 

5.41 

ND 

2.25 

:!48 

1.44 

1.10 

1.34 

11.10 

9.02 

8.73 

8.54 

3.54 

1.40 

21.84 

43.19 

1.67 

ND 

43.55 

81.2 

2.46 

ND 

:51 

0.90 

ND 

0.98 

4.09 

0.40 

1.40 

22.62 

9.81 

0.81 

11.05 

59.62 

145.88 

26.47 

1.09 

kKlo 

403.90 

1.32 

1.14 

0.90 

i.m 

ND 

OR ND 

6.51 

1.31 

ND 

l.w 

1.30 

::56 

ND 

w 

ND 

ND 

ORND 

0.51 

8.03 

1.64 

WI 

w 

ND 

ND 

ND 

w 

37.12 

48.32 

15.99 

1.79 

67.41 

49.18 

10.81 

L8 

99.62 

120.30 

3.70 

19.65 

z.35 

OR ND 

1.59 

El4 

ND 

ND 

ND 

ND 

1.3 

:I)03 

1.19 

ND 

0.85 

ND 

ND 

ND 

0.92 

ND 

ND 

2.50 

2.67 

2.05 

4.27 

0.43 

ND 

ND 

1.87 

0.22 

2.01 

4.35 

1.13 

3.45 

19.21 

18.12 

3.23 

ND 

13.58 

45.72 

56.37 

4.11 

6.40 

Et3 

OR-ND 

4.14 

0.33 

E 

:23 

ND 

ND 

OYD79 

2.10 

ND 

1.92 

ND 

ND 

ND 

ND 

ND 

ND 

3.09 

::36 

37.49 

45.33 

2.28 

5.80 

0.19 

19.73 

0.40 

2.41 

2.22 

6.65 

1.91 

ND 

::74 

13.8 

3.61 

1.50 

0.52 

ND 

0.33 

2.65 

2.25 

ND 

ND 

ND 

9R ND 

ND 

w 

ND 

w 

w 

r91 

4.90 

w 

2.12 

ND 

2.22 

27.93 

1.11 3.00 

15.31 206.62 

1.69 0.31 

50.79 4.61 

4.41 0.43 

14.19 4.37 

4.47 ND 

0.86 ND 

1.24 1.88 

10.52 ND 

111.9 ND 

14.49 ND 

110.12 0.34 

OR 39 14.62 

0.45 4.90 

34.26 13.94 

OR ND 2.30 

4.55 0.84 

0.59 0.49 

30.86 

2.16 

ND 

LID 

13.12 

FW 

ND 

ND 

ND 

ND 

ND 

1.21 

7.0 

ND 

5.24 

ND 

ND 

ND 

w 

w 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

w 

ND 

w 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.78 

0.50 

0.32 

0.75 

ND 

ORND 

2.57 

ND 

ND 

1.02 

ND 

:44 

ND 

ND 

ND 

ND 

:35 

3.71 

ND 

w 

ND 

No 

0.33 

ND 

1.68 

5.40 

1.12 

ND 

?92 

19.3 

4.67 

0.87 

ND 

ND 

ND 

11.64 9.69 

0.70 1.37 

ND ND 

OR ND OR ND OR ND OR ND 

ND ND ND ND 

!"22 

w ND ND 

0.30 ND ND 

ND No ND ND 

ND ND ND ND 

3.79 

3.11 

ND 

1.45 

ND 

ND 

4.03 

1.27 

0.22 

ND 

ND 

!!55 

ND 

ND 

ND 

!!93 

10.86 

13.91 

3.71 

ND 

0.35 

4.52 

0.31 

3.99 

1.66 

6.36 

1.45 

ND 

ND 

10.12 

58.3 

10.68 

9.43 

OR ND 

ND 

ND 

OR ND 

0.36 

ND 

0.23 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.49 

ND 

w 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:5 

?94 

OR ND 

ND 

no 

OR ND 

ND 

ND 

ND 

ND 

ND 

12.15 Y 

7.89 

4.94 

8.57 Y 

0.57 Y 

0.14 Y 

24.56 Y 

15.09 Y 

1.17 

15.60 

la.97 Y 

1.31 

7.03 

23.87 

29.56 

5.35 

0.11 

14.68 Y 

83.86 

106.50 

21.05 

10.39 

3.22 

55.57 

0.34 Y 

17.08 Y 

0.95 Y 

9.07 Y 

1.30 Y 

0.01 Y 

0.36 Y 

5.75 Y 

24.84 Y 

7.05 Y 

15.20 

14.36 

2.79 

11.40 

0.23 

0.29 

0.05 

3.14 

0.29 

ND 

3146 PO060288 L UB Carp 

3146 SE0267Dl F UB Carp 

3147 DC035201 F H) Carp 

3148 DE027101 F UB Carp 

3148 DE027103 F PF Ualleye 

3149 DC038501 F UB Uhite Sucker 

3150 DAOD8901 F UB tiite Sucker 

3151 DAD09101 F UB mite Sucker 

3151 DAD09102 F PF Sm Bass 

3151 00072887 L UB *ite Sucker 

3152 DA000201 F UB Uhite Sucker 

3161 DCO198Ol F BF Black Bullhead 

3161 DC019802 F YB mite Sucker 

3162 DJO22121 F UB Big Skate 

3162 DJO22122 F UB Ratfish 

3162 DJO22123 H D~eness Crab 

3162 DJD22403 F PF Ouillbsck Rockfish 

3162 DJO24DDl F UP Starry Flow&r 

3162 DJ025103 0 Hepetopancreas,Crsb 

3162 90041889 L Hepetopencreas 

3163 05022402 n Dungeness Crab 

3163 DJO22404 M Drngeness Crab 

3163 DJO24002 F UP Starry Flouufer 

3163 DJO25102 0 Hepatopancreas,Crab 

3164 DDOl5ml F PF Lm Bass 

3164 DDOl5702 F UB Carp 

3165 DDOl5703 F PF Lm Bass 

3165 DDOl5704 F UB Redhorse Sucker 

3165 00031788 L PF Ln Bass 

3166 DDO15705 F PF Ualleye 

3166 00015706 F UB Uhite Sucker 

3167 DDDl5707 f PF Let Bass 

3167 00015708 F UP Bluegill 

3167 DDO40588 L PF Lm Bass 

3167 SD015708 F UP Bluegill 

3168 00015711 F UB Carp 

3168 00015712 F PF Lm Bass 

3168 SD015711 F UB Carp 

3169 00015713 F UB Black Rcdhorse 

3170 00015715 F UB Spotted Sucker 

3171 00015717 F UB Spotted Sucker 

3172 00015719 F UB Carp 

3172 00015720 F PF Ln Bass 

3173 DDOl5Rl F PF Lm Bass 

D-1-14 
Episode SCC Type Description 

3173 00015722 F UB Chamel Catfish 

3173 a0070689 L PF Lm Bass 

3174 00015723 F PF La Bass 

3174 00015724 F YB Channel Catfish 

3175 00015601 F UB Chamel Catfish 

3175 DDOlSW2 F PF Lm Bass 

3176 DDOl58D3 F UB spotted Sucker 

3176 Do015804 F PF Lm Bass 

3177 00015805 F m Carp 

3177 DDOl58D6 F PF Lm Bass 

3178 00015807 F UB North Hogsucker 

3178 DDOlS808 F PF R&eye Bass 

3179 DDO158D9 f UB Golden Rcdhorse 

3179 DDOl5810 F PF Lm Bass 

3180 DDOl5812 F PF La Bass 

3181 00015813 F PF Lm Bass 

3181 DDO15814 f bm Carp 

3182 00015815 F PF Rock Bass 

3182 00015816 F UB Carp 

3183 00015817 F UB Carp 

3183 DDO15818 F PF Sawer 

3184 oooi5al9 F bm Carp 

3184 DDOl5820 F PF Wlite Crappie 

3185 DDOl5821 F UB Charnel Catfish 

3185 DDO15822 F PF Lm Bass 

3185 SD015821 F YB Chamel Catfish 

3186 DDO15823 F PF Spot 

3186 DOD15824 F Yp Southern Flotnder 

3187 DDOl59D2 f w Srnrrr Flouder 

3188 00015903 F UB Carp 

3188 00015904 F PF Lm Bass 

3189 DDO159D5 F LIB Carp 

3189 Do015906 F PF Lm Bass 

3190 DDOlSW7 F UB Carp 

3190 DDOl59LM5 F PF LD Bass 

3191 DJO24003 F Yp Starry Flouxkr 

3191 DJO24DD5 II Soft Shell Clems 

3192 DJO24DO7 F Up Starry Flouder 

3192 DJ024DW M Soft Shell Clams 

3192 90020789 L Soft Shell Clems 

3193 DC039001 F PF Strip4 Bass 

3193 a0039001 L PF Striped Bass 

31% DllO2OlO4 F UB Carp 

31% DllO2OlM F UB Chd 

2378 12378 

TWO PEWD 

1.39 

ND 

ND 

:31 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.31 

ND 

ND 

58 

ND 

ND 

4.38 

0.67 

3.13 

?14 

1.50 

3.97 

:18 

ND 

ND 

ND 

!!a4 

0.60 

5.35 

ND 

ND 

0.45 

ND 

!!52 

m, 

0.86 

ND 

ND 

542 

ND 

ND 

ND 

ND 

ND 

ND 

:57 

ND 

ND 

:69 

ND 

ND 

0.93 

?I3 

ND 

12.27 

1.81 

12.09 

ND 

ND 

L3 

?76 

ND 

1.02 

ND 

ND 

ND 

ND 

ND 

ND 

wo 

ND 

ND 

0.98 

123478 

HXWD 

ND 

ND 

ND 

:97 

ND 

ND 

Frn 

ND 

ND 

ND 

ND 

ND 

ND 

L4 

ND 

ND 

ND 

ND 

5.98 

P94 

0:81 

9.37 

ND 

ND 

ha 

ND 

OR .6 

ND 

1.13 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

m 

DIOXIN 

123678 123789 

HXWD 

1.69 

ND 

ND 

:50 

0.31 

2.03 

ND 

1.74 

ND 

WD 

ND 

1.36 

ND 

ND 

ND 

13.37 

0.51 

ND 

ND 

ND 

11.09 

ND 

50.77 

8.74 

51.84 

ND 

0.50 

0.67 

5.48 

ND 

OR .9 

:56 

ND 

ND 

m, 

ND 

ND 

La 

ND 

:76 

HXWD 

0.32 

ND 

ND 

ND 

1.25 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?15 

ND 

ND 

ND 

:“98 

:49 

0.99 

8.96 

ND 

L 

0.77 

ND 

OR ND 

r48 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

Ml 

/ FURAN CONCENTRATIDNS, 

1234678 2378 12378 

HPWD TWF 

2.30 1.61 

ND ND 

ND ND 

8% 0 no 28 

0.62 110 

1.63 1.54 

ND ND 

7.14 1.24 

0.75 ND 

0.74 ND 

?23 M) 1.77 

ND ND 

ND ND 

E-47 Y.23 

0.92 8.63 

3.23 23.53 

7.76 3.05 

0.59 

53.19 Ii 

ND 105.15 !?32 

22.15 0.26 

106.52 0.28 

ND ND 

1.47 0.23 

3.w ND 

11.49 4.13 

ND ND 

OR 4 1.24 

ND 10.75 :“58 

r5 

i:m 

073 Ni 

1.90 

0.69 9.W 

2.35 12.97 

2.10 13.18 

2.28 15.86 

2.82 19.28 

Y) 

7.71 

PEWF 

0.41 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.02 

1.36 

ND 

ND 

ND 

!D33 

0.49 

ND 

ND 

ND 

1.18 

ND 

110 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

P9/9 

23478 

PEWF 

1.43 

ND 

ND 

:65 

ND 

ND 

L 

ND 

ND 

ND 

ND 

ND 

ND 

2”49 

ND 

7.02 

3.83 

ND 

ND 

ND 

L9 

4.76 

ND 

ND 

!L9 

ND 

0.54 

Lo 

ND 

ND 

ND 

0.23 

ND 

Lo 

1.02 

123478 123678 

HXWF* HXWF 

ND ND 

ND ND 

ND ND 

ND ND 

1.88 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

*.*a tm 

ND ND 

ND ND 

ND ND 

4.17 1.94 

ND ND 

ND 

ED47 0.95 

NO ND 

1.79 ND 

ND ND 

16.45 2.96 

0.72 0.68 

2.70 2.67 

ND ND 

ND ND 

ND ND 

1.50 1.12 

ND ND 

OR .I) PR ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

123789 

HXWF 

ND 

ND 

ND 

ND 

m 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

m, 

234678 

HXWF 

ND 

ND 

ND 

ND 

0.79 

ND 

ND 

:92 

ND 

ND 

ND 

1.25 

ND 

ND 

ND 

2.29 

ND 

ND 

0.57 

ND 

0.81 

ND 

11.85 

ND 

1.14 

ND 

ND 

ND 

0.80 

ND 

ORND OR.6 

ND ND 

ND 0.90 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

)ID ND 

ND ND 

1234678 1234789 DPE 

HPWF 

0.25 

ND 

ND 

ND 

2.73 

ND 

ND 

ND 

1.31 

!!27 

ND 

1.25 

ND 

ND 

ND 

4.51 

ND 

ND 

1.40 

ND 

1.53 

E.41 

1.98 

7.76 

ND 

ND 

ND 

1.27 

ND 

0.78 

ND 

1.66 

ND 

ND 

0.29 

0.56 

0.49 

0.38 

ND 

ND 

0.25 

0.24 

HPWF 

ND 

ND 

WD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.69 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

TEC 

2.94 

ND 

ND 

0.03 

6.68 Y 

0.04 

0.37 Y 

0.: Y 

0.01 

0.01 

ND 

1.20 Y 

ND 

ND 

11.:: Y 

0.92 

5.95 Y 

7.62 Y 

0.68 

8.51 Y 

ND 

21.60 Y 

4.03 

13.56 

ND 

0.27 

0.13 

4.58 Y 

ND 

0.78 Y 

0.84 

2.50 Y 

5.42 

ND 

0.21 

1.48 Y 

1.33 

1.34 

2.58 

2.47 

0.02 

4.06 
Episode SCC Type Description 

31% OH020108 F UB Sucker 

3197 0H020110 F UB Sucker 

3198 DHO20111 F UB Sucker 

3199 0N020101 F UB Carp 

3199 OH020103 F UB Carp 

3200 bUO20112 F HI Sucker 

3201 DJO24012 F LIB Carp 

3203 bJ024018 F UB Carp 

3205 DJO24024 II Crayfish (whole) 

3206 DJO22301 M Crayf irh 

32W 05024102 F PF Lm Bass 

3206 05024103 F UB Sucker 

3208 05024109 F UB Sucker 

3212 DJ024121 F UB Carp 

3212 a0050388 L UB Carp 

3216 05023707 F PF Sqmtfish 

3216 bJ0237D8 F UB Sucker 

3216 QDWl688 L UB Sucker 

3217 05023709 F PF Uhitefish 

3217 DJO23710 F UB Sucker 

3218 05023711 F PF SqJawfish 

3218 DJO23712 F UB Sucker 

3219 DJ023713 F llB Uhite Sturgeon 

3219 DJO23714 F PF bihite Stur&n 

3220 05023902 F PF S+swfish 

3220 05023903 F UB Bridgelip Sucker 

3220 00012288 L PF Sqwwfish 

3221 DJO22405 F UB Carp 

3221 DJ023904 F .BF Channel Catfish 

3221 DJD23905 F b3 Sucker 

3222 05023906 F PF Sqawfish 

3222 05023907 F VB Sucker 

3223 05023717 F UP Starry Flomder 

3224 05023715 n Soft Shell Clam 

3226 05023721 n Pacific Dysters 

3227 DJO23723 n Pacific Dysters 

3231 bJ023911 F UB Carp 

3234 DUO20301 F LIP Sqmwfish 

3235 OH020303 F UB Uhite Sucker 

3236 OH020305 F UB Largescale Sucker 

3236 OH020306 F PF Brown Trout 

3237 OH020307 F PF Rainbow Trout 

3237 OH020308 F UB Largescale Sucker 

3238 DJ023918 F UP Doliy Vardrn 

2378 12378 

TWD PECDD 

ND 

ND 

1.53 

0.25 

ND 

0.56 

7.66 

2.86 

ND 

2.61 

0.74 

2.25 

:70 

0.87 

1.28 

2.57 

2.01 

4.58 

0.76 

1.73 

2.78 

2.14 

0.36 

1.48 

5.23 

1.75 

56.02 

7.92 

5.12 

1.14 

2.28 

1.57 

ND 

ND 

k9 

:33 

0.53 

ND 

ND 

ND 

ND 

0.28 

ND 

0.74 

0.46 

ND 

?83 

3.33 

Y&s 

:31 

ND 

ND 

ND 

0.95 

0.68 

0.55 

1.56 

0.27 

0.78 

ND 

ND 

r49 

0.68 

ND 

1.67 

0.34 

0.23 

::32 

NO 

ND 

ND 

ND 

1.20 

::50 

0.72 

0.91 

ND 

ND 

ND 

DIOXIN / FURAN CCUCENTRATICMS, w/g 

123478 123678 123789 1234678 2378 12378 23478 

0.16 

NO 

ND 

ND 

ND 

?93 

ND 

ND 

ND 

ND 

1.10 

ND 

ND 

ND 

ND 

ND 

:35 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.75 

ND 

ND 

ND 

ND 

0.58 

?63 

0.58 

ND 

ND 

24.79 

8.68 

ND 

10.05 

0.82 

4.06 

ND 

ND 

ND 

0.80 

0.90 

0.77 

1.79 

ND 

0.77 

0.66 

ND 

ND 

0.56 

ND 

ND 

1.34 

0.37 

ND 

0.20 

0.45 

0.42 

1.48 

ND 

ND 

2.93 

ND 

0.94 

1.00 

ND 

ND 

ND 

ND 

HXCDD HPWD TCDF PECOF PEWF 

ND 

ND 

ND 

0.25 

ND 

?36 

1.09 

ND 

1.42 

r61 

ND 

ND 

ND 

ND 

0.18 

0.19 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:41 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.26 

0.44 

1.69 

2.21 

0.74 

0.74 

91.72 

13.27 

0.49 

34.42 

0.43 

16.57 

0.56 

0.77 

ND 

0.90 

5.86 

4.66 

2.47 

0.54 

2.00 

::52 

0.37 

1.16 

2.20 

ND 

ND 

2.70 

0.33 

ND 

1.65 

2.37 

34.14 

ND 

7.49 

6.88 

0.91 

2.77 

2.80 

ND 

ND 

k9 

0.18 NO 

0.75 ND 

9.36 0.38 

0.43 ND 

ND 

Y.64 ND 

1.82 1.65 

4.10 0.57 

ND ND 

48.14 54.32 

1.09 ND 

3.35 0.91 

1.69 ND 

ND ND 

:03 0.51 ND 

11.38 0.28 

10.27 ND 

16.12 ND 

2.43 

21.63 !“29 

16.39 ND 

61.58 0.64 

8.02 20.12 :21 

28.34 0.30 

20.73 ND 

320.69 3.52 

4.97 NO 

41.78 ND 

11.95 ND 

15.95 ND 

11.58 ND 

0.49 ND 

1.29 ND 

1.74 ND 

9.14 0.65 

ND 

:“02 ND 

1.73 ND 

1.42 ND 

1.67 ND 

2.98 NO 

0.37 ND 

ND 

FM 

ND 

ND 

0.34 

4.81 

2.19 

ND 

19.02 

0.34 

2.27 

ND 

ND 

ND 

0.59 

0.44 

0.43 

0.45 

ND 

0.36 

iD33 

ND 

!!67 

0.26 

7.32 

1.09 

0.55 

0.21 

0.25 

ND 

ND 

ND 

ND 

ND 

:I)34 

0.64 

ND 

ND 

ND 

ND 

123478 

HXCDF* 

0.96 

ND 

ND 

ND 

ND 

::23 

2.88 

ND 

18.85 

::02 

ND 

ND 

ND 

ND 

ND 

ND 

0.60 

0.40 

Lo 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.20 

ND 

ND 

ND 

0.25 

ND 

742 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

123678 123789 234678 1234678 1234789 DPE 

HXCDF HXWF HXWf HPWf HPWf TEC 

ND 

NO 

ND 

ND 

ND 

?62 

0.91 

ND 

10.15 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.23 

ND 

#) 

ND 

WD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.67 

ND 

ND 

ND 

ND 

:80 

1.85 

ND 

0.87 

ND 

1.16 

ND 

ND 

ND 

ND 

ND 

ii56 

0.25 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

!“47 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.95 

ND 

ND 

0.32 

ND 

Ll 

2.88 

ND 

6.44 

0.24 

2.66 

ND 

ND 

ND 

r76 

0.65 

0.40 

ND 

ND 

0.28 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.24 

0.26 

3.06 

ND 

2.14 

0.91 

o”“20 

0.23 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.76 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.43 Y 

0.08 

3.26 Y 

0.63 

0.01 

1.10 Y 

19.02 

7.76 Y 

26.:: 

1.11 

6.61 Y 

0.17 

0.71 

0.87 

3.07 Y 

4.46 

3.68 

7.54 Y 

1.21 Y 

4.57 Y 

4.55 Y 

8.50 

1.17 

3.82 Y 

a.78 Y 

3.95 Y 

92.89 

9.20 Y 

9.71 Y 

2.46 Y 

4.22 

2.80 Y 

0.59 

0.13 

0.31 

2.80 Y 

0.01 

0.98 

1.59 

0.60 

0.17 

0.30 

0.04 
Episcde SCC Type Description 

3238 00080888 L UP Dolly Varden 

3241 DJ023924 F UP Dolly Varden 

3244 DJ023622 F UB Coast Sculpin 

3245 05023623 F UP Spotted Ratfish 

3245 05023624 F UP Flathead Sole 

3246 DJO22108 F PF Red Striped Rockfish 

3246 DJO22lW F VP Flathead Sole 

3248 DJ022502 F UB Composite Bottom 

3249 DJ0225O4 F UB Sucker 

3250 05022506 F UB Sucker 

3252 DJ02251O F UB Sucker 

3252 gDO82288 L UB Sucker 

3256 DJ022517 F PF Sm Bass 

3256 DJO22518 F UB Sucker 

3258 DC038901 F PF Spot 

3258 DC038902 F UB Croaker 

3259 08000466 F UB Goldfish 

3259 DBO69101 F UB Sucker 

3260 DBD00493 F UB Carp 

3261 DYO26002 F UB Striped Mullet 

3262 01026004 F UB Tilapia Tilapia 

3264 DY022602 F UB Hornyhead Turbot 

3266 DYD22702 F UB Channel Catfish 

3267 DY022101 F PF Rainbow Trout 

3267 DY022102 F UB Sacramento Sucker 

3267 PO020288 L PF Rainbow Trout 

3269 01022106 F UB Charnel Catfish 

3270 DY022107 F PF Squawfish 

3270 DY022108 F UB Sucker 

3270 SYO22108 F UB Sucker 

3271 01022110 F UB Sucker 

3272 DYO22111 F PF Leopard Shark 

3272 DY022112 F UB Uhite Surfperch 

3273 DYO22113 F UB Sculpin 

3273 DYO22114 F UB Surf’Smelt 

3274 DYD22116 F UB Sculpin 

3275 DYO22118 F UB Sucker 

3276 DY022119 F UB Ualleye 

3276 DY022120 F PF Brow Rockfish 

3278 01022124 F UB Sacrammto Sucker 

3281 01022205 F UB Sucker 

3282 DYD22207 F UB Carp 

3283 DYO222W F UB Carp 

3285 DY022212 F UP Stingray 

2378 

TWO 

ND 

0.53 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.58 

0.48 

0.74 

0.46 

1.52 

ND 

1.20 

1.89 

0.96 

0.76 

0.33 

4.08 

0.47 

11.74 

6.35 

11.26 

ND 

6.84 

6.45 

5.60 

0.21 

ND 

1.27 

0.63 

ND 

ND 

ND 

0.68 

ND 

ND 

ND 

!“93 

1.91 

12378 123478 123678 

ND 

ND 

ND 

ND 

0.24 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

OR 1 

ND 

ND 

ND 

:“W 

ND 

ND 

ND 

ND 

0.91 

0.83 

No 

ND 

ND 

:98 

ND 

ND 

ND 

ND 

0.43 

ND 

ND 

ND 

r78 

1.65 

HXCDD HXCDD HXCDD HPCDD TCDF PECDF PECOF HXWF’ 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.51 

!048 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

0.81 

ND 

0.57 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.40 

ND 

0.44 

ND 

ND 

ND 

0.87 

4.07 

1.37 

ND 

1.15 

0.81 

4.93 

ND 

ND 

ND 

ND 

1.33 

0.63 

ND 

ND 

0.42 

0.47 

2.46 

0.71 

ND 

ND 

ND 

0.78 

0.31 

ND 

ND 

:48 

3.15 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.46 

ND 

ND 

0.31 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.36 

ND 

ND 

ND 

NO 

0.16 

ND 

ND 

ND 

ND 

:“96 

0.77 

0.58 

1.62 

0.44 

1.59 

!D34 

2.18 

0.86 

2.25 

0.96 

0.97 

0.28 

0.73 

ND 

2.80 

5.87 

2.40 

2.91 

4.17 

15.08 

3.25 

1.22 

ND 

0.64 

1.69 

4.08 

ND 

0.62 

0.47 

1.22 

1.70 

4.84 

1.47 

0.54 

0.73 

0.32 

2.42 

3.12 

0.74 

0.72 

ND 

1.32 

8.69 

0.37 NO 

3.13 ND 

0.45 ND 

0.22 ND 

ND ND 

ND 

!D35 ND 

0.86 ND 

0.75 ND 

1.95 ND 

2.31 ND 

2.19 ND 

2.75 ND 

2.62 ND 

5.05 1.76 

!093 064 Nli 

24.73 0.96 

6.65 0.42 

3.48 0.71 

ND 

:D49 ND 

0.61 106.94 !“35 

61.40 ND 

99.67 )(o 

0.36 ND 

35.81 ND 

55.75 ND 

44.52 ND 

0.27 ND 

0.52 ND 

17.98 1.82 

0.64 0.47 

1.06 ND 

0.39 ND 

ND ND 

1.54 ND 

0.61 ND 

ND ND 

ND ND 

1.57 ND 

3.96 0.50 

12.90 2.67 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.44 ND 

ND ND 

0.23 ND 

ND NO 

ND 

:D96 ND 

ND 0.25 

2.72 0.59 

5.53 ND 

0.52 ND 

1.54 0.70 

ND ND 

2.36 ND 

0.76 ND 

0.54 ND 

ND ND 

0.60 ND 

0.73 ND 

0.54 ND 

ND ND 

0.30 ND 

ND ND 

ND 

:“W ND 

0.49 0.76 

ND ND 

ND ND 

ND 

r22 ND 

0:16 ND 

ND ND 

ND ND 

0.5395 !“22 

7.30 0.66 

DIOXIN / FURAN CONCENTRATTDNS, w/g 

123789 1234678 2378 12378 23478 123478 123678 123789 

HXCDF HXWF 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

0.51 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:42 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

234678 1234678 1234789 DPE 

HXCDF HPCDF HPWF TEC 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.33 

ND 

ND 

!“94 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.70 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.39 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.23 

ND 

0.30 

ND 

ND 

ND 

0.23 

!D40 

0.42 

0.23 

NO 

1.54 

3.48 

0.35 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.67 

ND 

ND 

ND 

0.28 

0.17 

ND 

ND 

r26 

0.46 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

0.04 

0.91 

0.06 

0.03 

0.14 Y 

0.: 

0.11 Y 

0.08 Y 

0.48 Y 

0.82 

0.87 

1.02 

0.73 Y 

4.09 

0.21 Y 

3.28 

7.39 

1.94 

2.33 Y 

E 

0192 

22.72 Y 

12.50 

21.54 Y 

1.03 

11.17 

12.03 

10.08 

0.29 

0.12 

6.97 

1.20 Y 

0.11 

0.05 

ND 

1.28 

0.20 Y 

0.01 

0.01 

0.42 

2.30 

8.50 

D-4-I 7 
Episods SCC Type Description 

32B5 DYO22213 F UB Vi@ Turbot 

3286 DY022215 F UB carp 

3287 VI022216 F W Tilspia Zilli 

3288 DY022218 F M Sucker 

3288 aOO6OlBB L W krker 

3289 DYO22219 F Up Bocsccio 

3269 01022220 F UB Sculpin 

3290 DYO22221 F PF Red& Sunfish 

3290 DY022222 F W Blackfish 

3294 DJO22111 F UP Trus Cod 

3294 DJ022113 11 Mussel 

3293 DJO22114 F w Atlmtic Salmm 

3296 DBO40101 F UB white Sucker 

3297 DBD41501 F UB Carp 

3297 DBO41504 F PC Sm Bass 

3297 SBO41501 F UB Carp 

3298 DBO41601 F bm Carp 

3298 DBO41604 F PF Lm Bass 

3298 aDll29B8 L PF Lm Bass 

3299 DBO40601 F UB Ilhite Sucker 

3299 DBD4D604 F PF Lm Bass 

3300 DBO40201 F W tiite kicker 

3JW DBO40201 F PF 9 Bass 

3300 SBO40201 F M tiite Sucker 

3301 DBO41101 F UB Carp 

3301 DBO41104 F PF Northern Pike 

3301 QDW2OM L UB Carp 

3301 SBO41101 F 1111 Carp 

3302 DBD41Wl F UB mite Bucker 

3302 08041904 F PF Lm Bass 

3303 OBD42301 F bi8 t&ire Sucker 

3304 DBO4lWl F PF Northern Pike 

3304 DBO41004 F UB Ulite Sucker 

3305 DBO42Wl F UB charnel Catfish 

3305 DBO42004 F PF Sm Bass 

3306 DBO41801 F W mite Sucker 

3307 DBD42101 F UB White Sucker 

3307 pPlOO588 L UB mite Sucker 

3308 DBD40001 F PF Northern Pike 

3308 ODO3D689 L PF Northern Pike 

3309 DBO41301 F UB Uhite Sucker 

3310 DC032701 F W Bullhead 

3310 DC032702 F PF Unlleye 

23M 

TWD 

ND 

1.59 

0.54 

a 

ND 

m, 

ND 

?39 

ND 

ND 

ND 

it40 

:“42 

3.49 

ND 

ND 

1.35 

1.24 

9.83 

2.40 

a.27 

33.70 

0.74 

35.07 

32.01 

8.76 

0.98 

1.15 

0.70 

1.70 

12.82 

ND 

1.01 

1.38 

1.30 

ND 

!:24 

1.20 

ND 

123M 

PEW0 

2.40 

1.48 

ND 

ND 

ND 

m 

m 

ND 

6.38 

ND 

N9 

)ID 

WD 

1.97 

ND 

1.86 

4.34 

ND 

10 

1.61 

0.49 

1.13 

!!W 

6.92 

r91 

6.17 

0.w 

IQ 

0.25 

WV 

0.93 

3.22 

II) 

ND 

ND 

ND 

ND 

ND 

ND 

1.38 

ND 

DIDXIN / FLIRAN COWCENTRATl0115, pa/g 

123478 1236M 123789 12346M 23M 123M 23478 

HXWD 

EW 

ND 

ND 

ND 

ND 

ND 

ND 

2.60 

ND 

ND 

ND 

ND 

ND 

m 

0.55 

0.88 

ND 

ND 

0.36 

ND 

ND 

ND 

?43 

ND 

r12 

ND 

M) 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.61 

ND 

HXWD 

2.34 

3.26 

lw) 

m 

I(D 

ND 

10 

wo 

7.92 

Ifi 

0.25 

WD 

1.63 

ND 

1.44 

5.51 

ND 

ND 

0.83 

ND 

m 

ND 

ND 

12.17 

ND 

13.07 

ii.83 

ND 

ND 

0.63 

:87 

2.07 

ND 

NO 

ND 

ND 

ND 

:42 

2.71 

ND 

HXWD 

0.63 

0.38 

ND 

ND 

ND 

ND 

ND 

ND 

1.29 

ND 

ND 

ND 

ND 

0.24 

ND 

ND 

1.21 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.57 

ND 

1.89 

ii 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.39 

ND 

HPWD TWF 

5.05 0.79 

5.33 1.81 

7.30 3.61 

0.56 1.95 

0.43 2.01 

2.74 0.76 

0.68 0.84 

1.44 ND 

15.M) 22.07 

ND 0.94 

ND ND 

i .a* 1.44 

0.42 2.00 

2.13 8.82 

0.59 m 

1.62 7.14 

17.01 2.62 

ND m 

ND ND 

0-M 4.65 

0.66 1.32 

0.58 7.33 

ND 0.70 

0.42 7.18 

17.82 7.30 

ND 1.67 

la.99 7.92 

16.97 7.37 

0.68 6.53 

0.39 ND 

4.11 9.10 

ND 0.91 

1.67 22.64 

1.57 3.00 

ND 2.43 

X:2 0.67 12.34 

ND 9.73 

ND 0.63 

ND 0.68 

4.M 1.41 

3.60 2.16 

0.42 0.69 

PEWF 

ND 

0.53 

ND 

ND 

m 

ND 

ND 

ND 

1.97 

ND 

lm 

ND 

ND 

6.39 

?83 

1:04 

lm 

F50 

0.85 

1.20 

ND 

1.02 

6.38 

:16 

5.60 

0.92 

ND 

ND 

r93 

0.57 

ND 

0.65 

ND 

0.31 

ND 

ND 

ND 

1.39 

ND 

PEWF 

1.85 

1.35 

Y) 

0.30 

0.35 

llD 

wo 

?75 

w 

Ml 

ND 

0.58 

22.67 

1.85 

20-M) 

3.89 

ND 

ii 58 

5.ia 

4.94 

ND 

4.80 

27.29 

ii.30 

26.09 

4.36 

m 

0.48 

ND 

1.88 

8.86 

ND 

2.20 

0.71 

0.75 

ND 

ND 

ND 

4.21 

ND 

1234M 

HXWF* 

ND 

ND 

ND 

ND 

II) 

ND 

18 

Y.W 

ND 

No 

ZI 

37.92 

1.34 

36.53 

1.07 

ND 

ii.77 

3.08 

1.46 

ND 

1.32 

15.44 

No 

15.98 

16.73 

0.78 

ND 

ND 

ND 

ND 

1.15 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1236M 123789 2346711 1234678 1234789 

0.63 

0.56 

ND 

ND 

10 

m 

ND 

m 

1.29 

ND 

lm 

ii 

13.B4 

0.35 

10.77 

1.B3 

ND 

M) 

1.31 

II) 

ND 

ND 

ND 

12.72 

Ia 

13.95 

10.07 

ND 

ND 

ND 

WD 

:65 

wo 

ND 

I)[) 

ND 

ND 

ND 

m 

1.00 

No 

HXWF HXWF 

ND 

ND 

m 

(0 

ND 

ND 

ND 

II) 

i .a* 

m 

ND 

: 

ND 

w 

0.85 

0.83 

ND 

ND 

1.42 

ND 

ND 

ND 

ND 

1.37 

ND 

1.54 

1.57 

ND 

ND 

m 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

HPWF 

r53 

1:35 

zl 

ND 

m 

L9 

ND 

ND 

WD 

ND 

11.76 

ND 

10.22 

3.02 

m 

ND 

6.38 

0.58 

0.32 

ND 

ND 

9.26 

ES6 

8.46 

0.56 

EW 

ND 

m 

ND 

Ei 

wo 

ND 

ND 

ND 

l.M 

ND 

ND 

HPWF 

ND 

s 

: 

ND 

M, 

m 

ND 

llD 

ND 

ii 

0.47 

ND 

IYI 

M) 

lm 

?4a 

ND 

ND 

ND 

ND 

m 

WD 

ND 

ND 

m 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DPE 

IEC 

2.61 Y 

3.M Y 

0.99 Y 

0.35 

0.38 

0.10 

0.09 

0.01 

12.33 Y 

0.09 

ND 

0.19 Y 

0.58 

25.43 

1.10 

10.30 

9.25 

ND 

28.3 

4.72 

13.81 

2.47 

lO.DB 

56.69 

0.91 

57.70 

39.87 

12.21 

0.98 

2.54 

E 

19.59 

0.24 

3-38 

2.61 

2.66 

0.06 

0.07 

0.49 

4.79 

0.07 
Episode SCC Type Description 

3311 DC032801 F bm Redhorse Sucker 

3311 DC032802 F PF Sm Bass 

3312 DC033101 F UB Rcdhorse Sucker 

3312 DC033102 F PF SI Bass 

3313 DC033201 F UB Rcdhorse Sucker 

3313 DC033202 F PF SI Bass 

3314 DC033301 F UE Chamel Catfish 

3314 DC033302 F PF tiite Bass 

3314 SC033301 F HI Channel Catfish 

3314 SC033302 F PF &it+ Bass 

3315 DC033401 F HI Carp 

3316 DC033501 F W Mite Sucker 

3316 DC033502 F PF Brow Trout 

3317 DC033601 F W rr)lite Sucker 

3317 DC033602 F W pupkinseed 

3317 SC033601 F W Wlite krker 

3317 SC033602 F Up puplrinseed 

3318 DCO33?01 F YB Unite Sucker 

3318 DCD33?D2 F PF Rock Bass 

3319 DBD41401 F Up Winter Flomder 

3319 ODlM3D88 1 UP Yinter FLouwier 

3320 DBWl412 F Yp Bluefish 

3321 08040401 F Up Winter Flouxler 

3322 DBD40412 F UP Bluefish 

3323 DBD41206 F UP Winter Flomder 

33P4 DBD41252 F UP Bluefish 

3325 DBD41218 F Up Bluefish 

3325 90082988 1 UP aluefish 

3326 DBD412D8 F UP Blusfish 

3327 08040301 F Up Bluefish 

3327 DBO40315 F UP Blmfish 

3326 ODO29111 F W Carp 

3328 Do029112 F PF Lm Bass 

3328 SD029111 F UB Carp 

3328 SD029112 F PF Lm Bass 

3329 ODOl6003 F UB Batfin 

3329 SD016003 F UB Boufin 

3330 DDO29lW F PF Stmennee Bass 

3330 DDO29110 F VB !+ottd Sucker 

3330 Do029423 F PF Black Crappie 

3331 DDOl6001 F UB Bran Bullheed 

2318 12378 123478 

TCDO PECDD HXCDD 

ND 

No 

ND 

F6S 

0.55 

56.34 

7.20 

47.10 

6.22 

No 

3:: 

58.21 

35.50 

46.57 

29.85 

1.71 

0.41 

No 

1.2 

0.75 

2.39 

1.16 

0.69 

1.74 

0.71 

0.52 

1.07 

2.92 

3.53 

30.04 

s3 

?.i4 

13.19 

11.46 

ND 

1.21 

:"% 

ND 

L 

!"41 

No 

1.02 

:91 

L9 

0.57 

No 

0.32 

m 

ND 

ND 

ND 

m 

No 

ND 

:37 

ND 

No 

No 

ND 

No 

ND 

7.75 

0.88 

En 

No 

0.65 

0.54 

No 

1.79 

No 

ND 

ND 

No 

No 

ND 

No 

ND 

No 

k4 

:42 

No 

No 

m 

No 

ND 

ND 

m 

ND 

No 

ND 

9RNo 

No 

ND 

ND 

No 

No 

m 

ND 

No 

ND 

0.54 

No 

No 

ND 

No 

No 

No 

No 

No 

No 

ND 

:41 

:37 

No 

1.95 

No 

1.16 

X"62 

0.37 

No 

0.25 

m 

No 

El8 

No 

No 

0.4 

9RNo 

0.34 

ND 

m 

m 

ND 

No 

ND 

:40 

1.11 

Es 

:71 

0.50 

ND 

1.12 

No 

0.27 

DIOXIN / FURAN CONCENTRATICW, Pg/R 

123?89 1234678 2378 12378 23478 

HXCDD HPCDD TCDF PECDF PECDF 

ND 

ND 

ND 

ND 

ND 

ND 

0.27 

ND 

No 

:25 

N9 

No 

ND 

No 

ND 

ND 

ND 

No 

ND 

No 

OR ND 

No 

ND 

ND 

ND 

No 

No 

No 

No 

ND 

ND 

No 

No 

No 

ND 

No 

No 

0.22 

ND 

No 

0.53 

ND 

1.?2 

0.42 

1.45 

0.48 

4.37 

0.37 

3.48 

No 

4.87 

1.52 

0.45 

0.37 

0.43 

II) 

0.23 

0.69 

0.38 

0.61 

0.8 

9RNo 

0.65 

ND 

IF72 

1.31 

0.60 

0.60 

0.53 

0.48 

3.64 

9-z 

0147 

:61 

6.42 0.64 

1.05 NO 

8.30 0.51 

2.18 13.51 :!23 

0.52 ND 

8.20 1.76 

5.84 0.40 

6.97 1.35 

5.24 0.33 

1.52 0.38 

30.48 1.48 

3.89 171.06 :39 

88.06 No 

144.02 0.35 

73.02 0.20 

30.70 0.31 

4.52 13.73 Y?4 

13.3 1.9 

1.93 1.06 

9.09 0.87 

0.67 0.42 

4.18 NO 

1.65 0.48 

1.27 0.42 

1.40 0.42 

1.47 0.46 

2-n 0.72 

3.20 0.84 

13.24 0.02 

1.?2 

1.35 

0.43 

1.37 

22.04 No 

10.89 m 

21.59 MD 

40.76 1.32 

39.89 1.20 

ND ND 

1.41 ND 

No ND 

1.18 ND 

0.61 

ND 

0.83 

ND 

0.71 

ho 

0.89 

5.14 

0.58 

0.63 

2.13 

0.78 

0.63 

0.28 

0.56 

0.18 

0.46 

k4 

a:7 

0.93 

1.15 

0.75 

E38 

0.72 

0.64 

0.70 

2.46 

2.59 

4.4s 

0.30 

4.05 

0.32 

2.21 

2.04 

:30 

ND 

No 

1234711 

HXCDF’ 

ND 

No 

No 

ND 

ND 

ND 

1.00 

0.22 

0.93 

No 

!!48 

0.28 

No 

No 

ND 

ND 

ND 

ND 

No 

No 

No 

ND 

No 

ND 

ND 

ND 

N9 

ND 

ND 

ND 

ND 

L 

:a? 

1.02 

ND 

No 

ND 

ND 

123678 123?89 234618 1234678 1234789 DPE 

HXQ)F HXCDF HXCDF HPCDF HPCDF TEC 

ND 

No 

No 

No 

No 

ND 

0.59 

ND 

ND 

No 

Es 

No 

ND 

No 

No 

No 

ND 

No 

No 

No 

No 

No 

ND 

ND 

No 

No 

ND 

ND 

No 

m 

No 

No 

No 

No 

1.55 

1.39 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

No 

No 

No 

m 

m 

m 

No 

ND 

ND 

m 

No 

ND 

No 

No 

ND 

m 

ND 

ND 

No 

ND 

m 

ND 

No 

No 

m 

No 

ND 

No 

m 

ND 

ND 

ND 

ND 

m 

No 

ND 

ND 

No 

ND 

No 

ND 

0.27 

No 

ND 

ND 

No 

No 

ND 

ND 

No 

ND 

ND 

ND 

ND 

NLi 

No 

ND 

ND 

ND 

m 

ND 

ND 

ND 

No 

ND 

ND 

No 

m 

ND 

:32 

ND 

ND 

ND 

No 

No 

ND 

ND 

ND 

ND 

ND 

b9 

ND 

ND 

No 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

9R ND 

No 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

No 

ND 

1.20 

1.D8 

ND 

ND 

ND 

ND 

ND 0.98 

No 0.10 

ND 1.51 

ND 0.22 

ND 5.62 

ND 0.61 

0.50 61.07 

ND 8.27 

ND 48.97 

No 6.84 

No 0.96 

No 10.40 

No 4.36 

m 75.84 

ND 44.45 

No 61.07 

ND 37.19 

IKJ 5.05 

ND 0.87 

No 1.19 

ND 3.02 

9R ND 1.46 

No 4.14 

ND 1.62 

ND 1.11 

m 2.38 

m 1.23 

LID 1.02 

ND 1.60 

ND 4.46 

ND 5.31 

m 34.27 

ND 11.14 

m 25-n 

No 9.43 

No 19.12 

m 16.09 

No 0.02 

ND 2.14 

No No 

ND 6.12 

D419 
Episode SCC Type Descriptia, 

3331 DD016002 F PF Ln Bass 

3331 00016007 F W Carp 

3331 DDOl6008 F RF Uhite Catfish 

3331 SD016008 F RF Mite Catfish 

3332 DDOl6009 F W Spotted Drrn 

3332 DO016010 F PF Crevrlle Jock 

3333 DDOl6011 F PF Bluefish 

3333 DDOl6012 F UB Sea Catfish 

3333 DDO29108 F PF Ueakfish 

3333 CJDl215&38 1 PF Bluefish 

3334 DDOl6013 F UR Sea Catfish 

3334 DDOlbolC F EF Striped Mullet 

3335 DDOl6015 F UP Spot 

3335 DDOl6016 F PF Spotted Bass 

3335 DDO29101 F W Red Drm 

3335 Do029102 F UR Southern Flander 

3335 00029103 F W Sheepshead 

3335 a0081588 L UP Southern FLou-der 

3335 SD016015 F W Spot 

3336 00016004 F W Black Drun 

3336 00016005 F PF Striped Mullet 

3336 00016006 F UP Sheepshead 

3336 DD016017 F UP Red Drun 

3336 DDOl6018 F PF Spotted Seetrout 

3336 a0092288 L PF Spotted Seatrwt 

3337 DDOl6019 F UR Spotted Sucker 

3337 DD016020 F PF Lm Bass 

3337 90051388 L UR Spotted Sucker 

3338 DDOl6021 F PF Lm Bass 

3338 00016022 F UR Spotted Sucker 

3338 DO029107 F PF Chain Pickerel 

3339 00016023 F UR Carp 

3339 DDOl6024 F PF Uhite Bass 

3339 00016023 L UB Carp 

3340 00029113 F PF Ln Bass 

3340 00029114 F UR Channel Catfish 

3340 SD029114 F UR Channel Catfish 

3341 DD016103 F PF Lm Ross 

3341 DO016104 F UR Catfish 

3341 a0092788 L PF Lm Bass 

3341 SD016103 F PF LR Bass 

3341 SD016104 F UR Catfish 

3342 DDOl6105 F UR Spotted Sucker 

3342 DD016106 F PF Bluegill 

2378 12378 

TCDD PECDD 

4.37 ND 

24.04 1.17 

8.94 0.55 

8.10 0.61 

0.63 1.12 

ND ND 

0.77 0.70 

3.13 0.54 

ND 

bfl 

E 4:04 

::.01 ::41 

ND ND 

0.82 ND 

0.71 0.39 

40.25 2.57 

D-70 0.36 

20.11 2.08 

ND 

:“?O ND 

3.53 1.32 

ND ND 

ND ND 

::62 ND 1.93 

0.88 

4.88 ::23 

ND ND 

1.72 1.85 

0.83 ND 

4.75 1.84 

1.42 0.28 

4.48 1.74 

3.77 ND 

98.88 3.52 

82.72 3.33 

7.75 34.40 Yoo 

6.10 ND 

6.68 ND 

31.20 3.44 

2.70 0.94 

ND ND 

DIOXIN / FURAN CDNCENTRATIONS, w/9 

123478 123678 123?89 1234678 2378 12378 23478 

HXCDD IIXCDD HXCDD HPCDD TCDF PECDF PECDF 

ND 

ND 

No 

:23 

ND 

ND 

0.24 

ND 

ND 

1.24 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.18 

ND 

1.61 

ND 

ND 

ND 

1.40 

ND 

1.60 

ND 

1.42 

ND 

ND 

2.28 

ND 

ND 

1.83 

0.91 

ND 

ND 

ND 

0.76 

0.68 

0.90 

ND 

No 

1.06 

ND 

0.81 

8.02 

:053 

ND 

ND 

ND 

1.52 

0.75 

1.66 

0.43 

ND 

ND 

ND 

ND 

ND 

2.53 

::36 

ND 

7.08 

::15 

0.25 

3.04 

ND 

3.70 

3.12 

!&4 

ND 

ND 

9.51 

3.13 

ND 

ND 

0.37 

0.18 

if29 

ND 

:25 

ND 

ND 

1.55 

E?l 

ND 

0.29 

ND 

:32 

0.59 

0.23 

ND 

0.24 

ND 

ND 

ND 

0.86 

ND 

0.99 

ND 

0.40 

ND 

0.68 

ND 

ND 

ND 

0.98 

0.67 

!i”?s 

ND 

ND 

3.07 

0.37 

ND 

1.09 

13.42 

1.68 

0.w 

1 .co 

:69 

1.06 

ND 

0.72 

5.05 

52 

0.45 

1.12 

2.42 

3.76 

2.47 

2.25 

1.66 

1.07 

1.00 

0.29 

0.72 

0.58 

5.34 

0.90 

5.41 

ND 

11.03 

ND 

20.03 

1.79 

17.57 

ND 

5.38 

4.94 

ND 

23.44 

ND 

ND 

18.72 

5.05 

0.44 

0.58 ND 

7.84 0.40 

1.48 m 

1.5, ND 

2.95 0.30 

ND 

Co No 

1.62 ND 

No 

!%I ND 

0.71 ND 

ND No 

40.03 4.52 

1.00 0.65 

4.99 3.20 

0.84 ND 

9.21 1.40 

0.92 39.06 ::61 

0.90 ND 

11.62 ND 

4.88 ND 

0.75 ND 

ND ND 

ND ND 

8.09 ND 

0.X ND 

8.89 ND 

::87 ND 

!!46 

ND 

2.91 iD40 

6.79 0.86 

0.31 ND 

10.19 0.21 

10.28 ND 

14.90 0.23 

18.06 ND 

10.92 ND 

12.81 ND 

15.82 ND 

24.54 0.72 

ND ND 

ND 

ND 

0.27 

0.21 

0.50 

ND 

0.34 

0.43 

ND 

0.40 

No 

:“I5 

ND 

ND 

k6 

ND 

4.90 

ND 

ND 

ND 

ND 

ND 

ND 

0.50 

ND 

0.75 

ND 

1.04 

ND 

2.18 

0.74 

2.15 

ND 

1.93 

1.83 

0.31 

3.25 

0.26 

ND 

2.80 

1.16 

ND 

1234M 123678 

HXCDF* HXCDF 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.41 

ND 

0.26 

ND 

0.71 

ND 

1.43 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.28 

ND 

1.13 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

0.30 

ND 

No 

ND 

ND 

No 

No 

ND 

ND 

ND 

ND 

No 

ND 

No 

l.D9 

ND 

ND 

ND 

0.49 

&? 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.86 

ND 

0.75 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

123789 234678 1234678 1234789 DPE 

HXCDF HXCDF HPCDF HPCDF TEC 

No 

ND 

ND 

ND 

No 

ND 

No 

ND 

LID 

No 

ND 

m 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.10 

ND 

No 

No 

No 

ND 

ND 

ND 

ND 

No 

:97 

ND 

0.23 

ND 

0.71 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.23 

ND 

ND 

ND 

0.19 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.75 

ND 

ND 

ND 

No 

ND 

No 

No 

ND 

ND 

:39 

ND 

ND 

QR ND 

ND 

No 

0.30 

0.21 

ND 

ND 

ND 

ND 

ND 

0.36 

ND 

0.27 

ND 

0.89 

ND 

0.74 

ND 

0.78 

ND 

0.39 

ND 

ND 

ND 

ND 

ND 

k8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

No 

No 

OR ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.44 

25.74 Y 

9.61 

8.61 

1.91 

1.: 

3.94 

1.: 

6.72 

32.: 

0.14 

1.57 

1.01 

45.94 

1.10 

26.02 

0.17 

3.87 

4.71 

0.08 

0.01 

0.01 

7.16 Y 

0.92 

7.91 Y 

ND 

4.62 

0.83 

8.37 

2.28 

7.98 

3.80 

103.32 

85.75 

9.41 

41.62 

7.32 

7.96 

35.38 

b.?? Y 

ND 

04-20 
Episode SCC Type Description 

3343 DD016107 F VB Uhite Sucker 

3343 DDOl6108 F PF Redbreast Sunfish 

3344 DDD16lW F UB Carp 

3344 DD016110 F PF Lm Bass 

3344 SD016100 F UB Carp 

3345 DD016111 F UB Redhorse Sucker 

3345 DD016112 F PF Lm Bass 

3345 SD016111 F UB Redhorse Sucker 

3346 DO016113 F UB Creek Chubsucker 

3346 ODD16114 F PF Lm Bass 

3346 00042088 L WE Creek Chdwcker 

3346 SD016113 F UB Creek Chdsucker 

3346 SD016114 F PF Lm Boss 

3347 DDOl6115 F UEi Csrp 

3347 DD016116 F PF Lm Bass 

3347 SD016115 F UE Cerp 

3348 DDOl6117 F PF Uhite Perch 

3348 DD016118 F WE Blue Catfish 

3348 ODO72888 L UB Blue Catfish 

3348 SDDl6117 F PF Uhite Perch 

3348 SD016118 F UB Blue Catfish 

3349 DDDl6119 F W Carp 

3349 DD016120 F PF Lm Bass 

3350 DD016121 F WB Carp 

3350 00016122 F PF Ln Bass 

3350 PO052688 L IiE Carp 

3351 DD016123 F PF Rock Bass 

3351 DD016124 F UB Carp 

3351 9DO21888 L UB Carp 

3352 DF023?23 F PF Crappie 

3352 DFO23?24 F WE Carp 

3352 a0091388 L UE Carp 

3353 DF024121 F BF Blue Catfish 

3353 OF024 22 F WE Sm Buffalo 

3353 a0024 21 L BF Blue Catfish 

3354 Or022 101 F UE Csrp 

3354 Or022 i02 F PF Lr Boss 

3355 DYO22 ;03 F UB Carp 

3355 DYO22 Xl4 F PF Ln Bass 

3355 SYO22 103 F W Carp 

3356 DE030 !Ol F I(B Carp 

3356 SE030 !Ol F UB Carp 

3357 DYD22 !23 F PF Sqwf ish 

3357 DYO22 !24 F UB Sacramento Sucker 

2378 12378 123478 123678 

TCDD PECDD HXCDD HXCDD 

7S.70 

12.01 

22.30 

0.93 

20.94 

5.50 

1.44 

5.78 

143.32 

18.24 

157.50 

156.34 

20.88 

15.31 

3.17 

12.58 

18.20 

104.13 

107.02 

15.73 

87.26 

9.10 

1.17 

3.97 

0.48 

3.83 

0.17 

22.07 

21.04 

ND 

1.31 

1.23 

5.53 

5.17 

4.83 

1.07 

ND 

13.38 

ND 

15.0 

6.55 

5.50 

0.80 

3.47 

2.64 

ND 

2.32 

:060 

6.71 

1.00 

7.69 

1.34 

ND 

1.53 

1.44 

0.20 

2.29 

0.32 

1.80 

1.65 

12.48 

12.19 

1.33 

10.81 

1.51 

ND 

4.58 

::40 

ND 

2.49 

1.95 

ND 

2.55 

2.41 

0.92 

E 

3:m 

0.49 

53.95 

ND 

58.9 

9.35 

X:E 

0.90 

ND 

ND 

1.76 

ND 

1.68 

ND 

ND 

2.44 

ND 

ND 

!“2s 

ND 

2.39 

ND 

1.80 

ND 

1.11 

1.16 

!D93 

0.97 

ND 

1.35 

ND 

1.47 

ND 

1.91 

2.48 

ND 

5.39 

4.45 

ND 

1.06 

ND 

2.62 

ND 

37.56 

ND 

40.0 

3.00 

2.28 

ND 

ND 

ND 

0.33 

6.80 

:26 

7.08 

1.14 

8.34 

ND 

ND 

!“6? 

ND 

:34 

4.82 

0.22 

2.25 

2.25 

ND 

1.59 

3.02 

ND 

6.82 

z3 

:033 

4.44 

K2 

5.77 

1.82 

1.62 

1.47 

7.54 

0.43 

89.08 

0.89 

113.5 

7.77 

6.69 

0.44 

1.40 

DIOXIN / FURAN CONCENTRATIDXS, w/g 

123789 1234678 2378 12378 23478 123478 

HXCDD HPCDD TCDF PECDF PECDF HXCDF* 

0.51 

ND 

1.51 

ND 

1.23 

2.69 

ND 

3.44 

ND 

ND 

ND 

0.17 

ND 

0.95 

ND 

0.65 

!“?I 

0.81 

ND 

ND 

0.95 

ND 

1.08 

ND 

0.91 

!OS2 

ND 

ND 

1.88 

1.68 

0.54 

0.53 

0.47 

1.68 

ND 

24.76 

ND 

24.9 

1.73 

1.20 

ND 

ND 

4.43 143.88 7.20 

1 .Ol 5.94 ND 

33.06 3.34 0.49 

ND ND ND 

35.39 2.84 0.59 

17.20 93.71 ND 

2.45 1.39 ND 

22.01 105.13 ND 

1.74 194.74 1.25 

0.28 20.10 ND 

1.18 207.38 1.31 

2.00 194.16 1.48 

0.37 

32.23 

0.95 

27.62 

1.85 

4.59 

4.57 

1.18 

3.81 

16.84 

0.81 

14.12 

ND 

13.42 

ND 

13.53 

13.36 

1.10 

37.95 

32.45 

5.21 

5.08 

4.74 

25.82 

1.47 

249.06 

1.24 

283.1 

12.44 

11.91 

Ll3 

23.20 

4.11 

2.12 

3.42 

48.49 

26.15 

27.48 

48.32 

21.03 

10.43 

0.56 

4.32 

ND 

3.65 

ND 

16.09 

16.89 

!“96 

0.86 

2.87 

19.91 

2.74 

3.44 

ND 

1.03 

ND 

1.2 

5.33 

5.27 

3.71 

35.79 

0.21 

0.33 

ND 

0.28 

1.97 

4.17 

4.47 

1.43 

3.53 

0.53 

ND 

0.93 

ND 

0.97 

ND 

i:: 

ND 

ND 

ND 

ND 

0.33 

ND 

1.24 

La 

Fs 

3.35 

2.63 

ND 

0.24 

8.23 1.40 

ND ND 

ND 2.07 

:“28 

ND 

0.63 

0.68 0.36 

ND ND 

1.00 ND 

9.18 ND 

D.48 ND 

10.32 ND 

12.08 ND 

0.64 ND 

ND 0.39 

ND ND 

1.51 0.37 

1.99 ND 

16.58 ND 

16.76 0.42 

1.60 ND 

13.10 ND 

2.03 ND 

:“os ND 2.09 

ND ND 

1.93 1.85 

::47 ND 

3.65 ::3 

ND ND 

ND No 

:33 No 

0.49 ND 

::37 ND 1.85 

ND ND 

17.07 19.67 

ND ND 

19.6 16.5 

24.81 2.37 

21.67 2.31 

0.23 NO 

1.25 NO 

123678 123789 

HXCDF HXCDF 

1.34 

ND 

ND 

::83 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

Lo 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.84 

ND 

0.60 

ND 

1.15 

0.94 

ND 

No 

m 

No 

ND 

ND 

1.85 

ND 

13.14 

ND 

14.3 

3.30 

2.33 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

110 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

No 

No 

No 

No 

No 

No 

No 

ND 

No 

ND 

m 

No 

No 

uo 

No 

ND 

ND 

No 

234678 1234678 1234789 DPE 

HXCDF HPCDF HPCDF TEC 

0.61 

ND 

1.89 

::27 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.29 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.39 

No 

1.41 

::03 

3.48 

ND 

No 

No 

No 

No 

ND 

ND 

L 

ND 

2.8 

1.29 

0.99 

ND 

ND 

0.85 

ND 

2.92 

ND 

1.35 

0.48 

ND 

uo 

ND 

ND 

ND 

ND 

ND 

1.48 

0.13 

1.31 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.79 

No 

1 .ss 

::83 

3.53 

ND 

ND 

No 

ND 

No 

No 

3.46 

z.42 

ii.7 

2.43 

2.01 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

UQ 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

No 

UQ 

No 

ND 

No 

ND 

No 

No 

No 

No 

No 

No 

No 

No 

No 

2.57 

F.7 

No 

m 

ND 

No 

96.32 Y 

12.65 

25.58 Y 

0.93 Y 

23.27 

19.76 Y 

2.22 Y 

20.83 

168.13 Y 

20.49 

184.24 Y 

177.88 

23.39 

17.62 

3.59 

14.33 

25.01 

121.94 

124.98 

21.53 

96.54 

12.60 

1.23 

9.28 Y 

0.48 

8.80 Y 

0.17 

28.27 Y 

27.02 Y 

0.01 

4.44 

4.04 

6.73 

8.63 

5.72 

6.05 Y 

0.30 

71.02 Y 

0.10 Y 

54.7 

26.43 

13.41 

1.50 

8.30 

04-21 
Episode SCC Type Description 

3360 Do029117 F UB Carp 

3360 Do029118 F PF 11 Boss 

3360 aoO223B9 L w carp 

3375 DDOl6305 F UB Carp 

3375 DO016306 F PF Lm Boss 

33?5 QDlOll88 1 YB Carp 

3376 DD01630f F m Carp 

3376 DDOl6308 F PF Lm Boss 

3376 00050389 1 PF Lm 8055 

337? DDOl6309 F YB Carp 

33?? Do016310 F PF Lm Boss 

3377 SD016309 F m Carp 

3378 Do016311 F YB Bpotted Sucker 

3378 DDO16312 F PF Lm Boss 

3378 DDO29115 F UB Grevfin Suker 

33?8 DDO29116 F BF &net Cotfish 

3385 DDOl6401 F UB Rcdhorse Sucker 

33% 00016421 F W Rcdkorse Sucker 

33% 00016422 F PF Lm Boss 

33% SD016421 F UB Redhorse Sucker 

3401 DDD16509 F lls Corr, 

3401 00016510 F PF Lr ;eoss 

3403 DDOl6513 F UB River Corpsuker 

3403 00016514 F PF La Boss 

3406 DDDl6515 F UB Carp 

5401 DDD16516 F PF Lm Boss 

3404 50016515 F YB Carp 

3409 DBO40?01 F bB Cwp 

3409 DBO40?06 F PF Lm Boss 

3411 08040501 F UB Rcclhorse Suker 

3412 DBO40901 F PF Sn Boss 

3412 DBO40907 F UB Carp 

3412 58040907 F H1 Carp 

3414 DC036203 F PF Bm Boss 

3414 DC036204 F BF Chmnel Catfish 

3415 DC036205 F PF Ba Boss 

3415 DC036206 F BF Channel Catfish 

3416 OF025210 F BF Chend Cotfish 

3416 OF025211 F BF Carp 

3416 OF025212 F PF Lm Boss 

3418 OF025007 F BF Blue Cotfish 

3419 DC036207 F H) mite Bucker 

3419 DC036208 F PF Freshwater DrLn 

3420 DC036209 F PF Greenfish 

2378 12378 

TcDD PECDD 

1.00 0.52 

ND 

:18 La 5.43 

0.83 ND 

5.34 5.78 

7.15 10.55 

110 Ito 

ND ND 

7.15 12.38 

ND ND 

0’:: ND 12.28 

L6 EC9 

ND ND 

29Y9 Lb4 

5.48 ND 

45.04 2.56 

3.35 1.09 

K9 

No 

6.61 

1.002.20 &a 

0.67 ND 

9.70 4.06 

2.32 4.75 

ND No 

1.10 0.70 

1.30 

28.30 :94 

24.40 5.52 

NO 

!!65 NO 

ND No 

1.85 1.00 

3.14 ND 

6.46 NO 

ND No 

1.40 ND 

ND No 

ND ND 

23.86 0.79 

123478 123671) 123?B9 

DIDXIY / FURAN CI.WCENTRAllOS, w/g 

1237B 23418 

HXCDD HXCDD HXCDD 

1234678 23?B 

HPCDD TCOF PECDF PECDF HXCDF* HXCOF UXCOF HXCDF HPCDF HPCDF 

ND 

No 

?.a8 

Y.21 

7.53 

UD 

r.29 

r93 

ND 

!!30 

ND 

ND 

No 

m 

!!?4 

ND 

1.38 

ND 

1.11 

ND 

1.14 

3.55 

No 

ND 

ND 

1.25 

1.21 

II0 

No 

!I!"42 

No 

No 

ND 

ND 

ND 

ND 

ND 

1.37 ND 

!!28 

No 

20.42 :68 

0.59 No 

22.47 2.?3 

41.95 5.84 

uo II0 

ND No 

47.29 7.77 

g-11 

ND 

10.50 

ND ND 

No 

&a m 

m ND 

0.55 ND 

2.11 0.43 

No No 

1.56 ND 

2.06 0.43 

10.67 NO 

3.07 0.70 

Lo 

ND 

1.05 

ND ND 

4.89 0.85 

13.63 2.54 

ND No 

1.12 ND 

ND ND 

6.50 0.86 

4.54 0.65 

MD ND 

1.10 ND 

ND ND 

1.28 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.07 ND 

4.?3 2.49 

:74 :91 

93.06 6.97 

0.05 1.69 

102.97 7.59 

138.06 5.56 

1.22 nD 

ND 

171.02 ifor 

ND 0.43 

161.29 6.99 

1.91 

!!31 

No 

1.60 

4.81 

0.71 

4.13 

11.70 

:59 

i!Sl 

0.87 

7.70 

34.76 

0.34 

1.38 

ND 

8.76 

7.67 

ND 

2.48 

Y?l 

2.19 

2.61 

ND 

ND 

No 

ND 

4.11 

9.05 

No 

7.13 

:92 

2IJ.81 

10.96 

245.?5 

12.00 

1.00 

19.71 

2.51 

6.29 

1.10 

6.66 

9.19 

1.01 

4.83 

1.16 

2.83 

2.57 

L 

ND 

1.43 

1.611 

2.97 

2.16 

0.65 

6.85 

ND 

19.22 

ND 

ND 

ND 

2.OB 

:35 

2.46 

UD 

MD 

3.09 

??? 

ND 

ND 

ND 

ND 

UD 

4.21 

&a 

1.05 

ND 

1.82 

ND 

0.76 

ND 

0.58 

1.95 

ND 

ND 

ND 

1.89 

1.70 

ND 

ND 

!D4? 

ND 

No 

ND 

ND 

ND 

ND 

0.60 

0.50 

:59 

5.93 

0.42 

6.6B 

7.16 

uo 

ND 

10.21 

L4 

0.46 

ES6 

ND 

0.19 

5.15 

No 

4.65 

2.04 

:47 

No 

1.97 

ND 

1.76 

11.86 

ND 

0.98 

ND 

20.91 

16.80 

0.26 

2.73 

::30 

ND 

ND 

No 

ND 

ND 

ND 

0.34 

12347B 1236?B 1237B9 2346?B 12346111 12347B9 

ND 

No 

ND 

1.97 

:24 

4.59 

UD 

ND 

4.20 

ND 

4.52 

No 

ND 

ND 

No 

ND 

: 

ND 

ND 

ND 

0.59 

," 

ND 

No 

1.65 

ND 

0.24 

ND 

8.50 

8.82 

No 

ND 

No 

No 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

m 

:37 

ND 

4.18 

5.51 

uo 

El? 

No 

5.73 

ND 

m 

m 

m 

ND 

0.31 

No 

ND 

m 

:37 

m 

ND 

: 

3.19 

No 

ND 

No 

5.80 

4.35 

ND 

ND 

No 

No 

ND 

No 

No 

ND 

ND 

No 

ND 

No 

No 

ND 

No 

No 

No 

No 

No 

m 

No 

No 

UD 

No 

No 

ND 

ND 

ND 

II) 

ND 

ND 

m 

ND 

m 

II) 

ND 

ND 

No 

ND 

m 

m 

No 

No 

ND 

ND 

No 

No 

No 

No 

ND 

ND 

No 

ND 

No 

ND 

No 

ND 

ND 

1 .Ol 

No 

1.23 

2.03 

uo 

ND 

2.48 

%? 

No 

m 

m 

No 

m 

ND 

ND 

ND 

ND 

No 

0.51 

ND 

No 

ND 

?99 

No 

No 

ND 

0.85 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

No 

No 

No 

No 

No 

No 

7.58 

ND 

7.96 

15.53 

UD 

ND 

16.35 

m 

26.74 

no 

ND 

ND 

No 

m 

ND 

m 

0.32 

0.34 

m 

1.84 

L? 

L 

3.15 

:31 

L 

2.62 

ND 

ND 

ND 

m 

No 

No 

ND 

ND 

No 

ND 

0.24 

ND 

No 

No 

0.65 

No 

0.83 

0.91 

No 

ND 

0.97 

W 

ND 

No 

ND 

No 

ND 

UD 

ND 

110 

ND 

No 

No 

0.50 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

No 

ND 

ND 

ND 

ND 

No 

ND 

No 

No 

No 

ND 

DPE 

TEC 

2.03 

ND 

1.22 

15.91 

1.28 

17.17 

24.97 

0.01 

ND 

28.90 

0.04 

18.7? 

1.58 

1.g 

m 

1.94 

81.21 

6.58 

71.77 

6.61 

1.17 

14.95 

1.25 

17.12 

0.79 

12.91 

14.58 

0.10 

2.58 

1.42 

45.11 

29.67 

0.13 

2.21 

4.2 

3.33 

6.78 

0.22 

1.47 

0.69 

26.: 

m-22 
Episode SCC Type Description 2378 

3420 DC036210 F llB Csrp 

3421 DC036211 F PF Mite Perch 

3421 DC036212 F UB Carp 

3421 SC036212 F UB Carp 

3422 DC036213 F PF lm Boss 

3422 DC036214 F UB Yellow Bullhead 

3423 DC036215 F PF Ubite Perch 

3423 DC036216 F UB Uhite Cotfish 

3424 DC036217 F PF Shortnose Car 

3424 DC036218 F UB White Cotfish 

3425 OF025005 F W Carp 

3425 OF025012 F BF Chemel Cotfish 

3425 90031389 1 BF Channel Cetfish 

3426 08069102 F PF Bluefish 

3427 DE069103 F PF BLuefish 

3428 DE069104 F PF Bluefish 

3429 DBD69105 F PF Ueskfish 

3430 DBD69106 F UB mite Cstfish 

3431 00069109 F UB Red Snspper 

3432 DE069111 F BF Red Snepper 

3433 08069112 F UP Flcuder 

3433 PO021689 L up Floudcr 

3434 DBO4OBOl F Up Flouder 

3435 DDOl6601 F PF Uhite Boss 

3435 00016602 F UB Bigmouth Buffdo 

3437 DJO22302 M Crayfish 

3438 DJ022303 H D~eness Crab 

3439 DJO22304 F UB Uhite Sturgerm 

3439 QOO62289 L UB mite Sturgeon 

3440 DJO22305 F UB Mite Sturgeon 

3441 DJO22306 F UB Uhite Sturgeon 

3442 OF024301 F BF Chmnel Cotfish 

3442 00081089 1 BF Channel Cotfish 

3444DDOl6603 F m Carp 

3444 Do016604 F BF theme1 Cstfish 

3444 00029512 F PF Lm Boss 

3444 00091289 L W Carp 

3445 00029513 F UB Flouder 

3445 DDO29514 F u8 Hardhead Cotfish 

3446 DDOl6605 F PF Striped Boss 

3446 DDOl6606 F UB Corpsucker 

3446 Do020511 F ba Carp 

3446 aOW2089 1 llB Carp 

3450 DYO223(w F PF mite Croeker 

40.32 

5.45 

54.09 

43.96 

1 .cs 

1.84 

0.83 

2.46 

1.07 

1.94 

160.36 

52.90 

43.41 

0.85 

1.26 

ND 

No 

0.75 

ND 

No 

4.45 

4.37 

6.29 

58 

T97 

La 

1.06 

ii 

No 

3.51 

3.n 

No 

4.01 

r91 

21.55 

E 

2:26 

1.02 

123?8 

PECDD 

1.64 

ND 

1.77 

1.78 

ND 

No 

ND 

2.71 

ND 

1.05 

9.43 

i:E 

ND 

ND 

ND 

ND 

ND 

1.19 

T94 

r97 

Ts2 

ND 

No 

No 

ND 

No 

No 

No 

Lo 

3.54 

Lo 

No 

2.40 

ND 

ND 

No 

No 

No 

123478 

ND 

No 

No 

0.40 

ND 

ND 

ND 

ND 

ND 

LB 

ND 

No 

No 

ND 

No 

No 

ND 

No 

No 

ND 

ND 

No 

ND 

ND 

ND 

ND 

No 

No 

ND 

No 

ND 

s”29 

1:16 

L2 

ND 

No 

ND 

No 

No 

ND 

No 

123670 

HXCDD 

2.67 

ZD43 

3.43 

ND 

ND 

P91 

0.99 

iD.98 

1.29 

ND 

ND 

ND 

ND 

ND 

0.68 

ND 

ND 

0.92 

1.19 

1.70 

Y22 

ND 

1.22 

ND 

No 

No 

No 

ND 

No 

22.88 

7.68 

ND 

25.53 

ND 

5.57 

ND 

No 

1.03 

1.45 

ND 

DIOXIN / FURAN COWCENTRATIDNS, w/g 

123789 1234678 2378 12378 23478 

HXCDD 

0.51 

i!?6 

0.45 

ND 

ND 

rw 

L&2 

2:89 

0.58 

0.55 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

FL 

No 

ND 

No 

No 

No 

No 

No 

No 

4.00 

1.45 

No 

5.04 

Fo2 

ND 

ND 

ND 

ND 

No 

HPCDD TCDF 

5.86 12.57 

ND 10.86 

2.40 60.25 

2.10 50.75 

No 0.67 

1.62 0.60 

1.84 4.68 

5.75 3.32 

1.36 2.33 

3.60 3.60 

21.60 62.46 

4.05 4.92 

3.14 4.23 

ND 1.90 

ND 2.23 

ND 1.80 

ND No 

0.89 1.14 

ND 1.43 

59 No 1.37 

0.63 1.47 

0.69 1.26 

::68 8.29 2.2 

3.33 

L! 

:i!L 

22.05 

0.84 20.94 

b2 22.15 17.75 

ND ND 

No 131.65 751 

10.03 ND 

ORNO NO 

150.84 1.45 

2.63 ND 

5.90 No 

ND 3.62 

784 

4:61 

0.68 1.42 

1.38 

ND ND 

PECDF 

0.69 

:Dos 

2.48 

ND 

ND 

ND 

0.67 

ND 

ND 

4.15 

ND 

ND 

:41 

ND 

k3 

0:71 

ND 

ND 

ND 

No 

ND 

1.66 

ND 

ND 

Es2 

ND 

No 

ND 

ND 

1.14 

ND 

No 

1.26 

ND 

ND 

ND 

No 

ND 

ND 

ND 

PECDF 

3.03 

ND 

!“34 

ND 

ND 

:“W 

iD74 

10.45 

2.34 

1.R 

0.42 

0.63 

0.98 

ND 

1.39 

1.71 

ND 

1.90 

2.21 

3.12 

ND 

1.70 

if!43 

ND 

NO 

ND 

ND 

No 

No 

2.28 

1.02 

ND 

2.67 

No 

ND 

1.?8 

ND 

1.76 

1.92 

m 

123478 123678 123789 234678 1234678 1234789 DPE 

HXCDF* 

ND 

ND 

0.40 

0.46 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

FL 

ND 

ND 

No 

No 

ND 

ND 

No 

!&s 

No 

:?6 

ND 

ND 

No 

&I 

0.92 

No 

HXCDF 

ND 

m 

No 

ND 

ND 

No 

No 

No 

ND 

No 

1.54 

UD 

No 

No 

m 

ND 

ND 

ND 

No 

M 

No 

ND 

ND 

m 

ND 

No 

No 

ND 

No 

ND 

No 

# 

No 

5.63 

ND 

m 

5.88 

ND 

No 

No 

ND 

ND 

No 

No 

HXCDF 

ND 

ND 

ND 

ND 

ND 

No 

No 

ND 

ND 

ND 

ND 

UD 

ND 

ND 

No 

ND 

ND 

m 

ND 

ND 

No 

110 

No 

ND 

ND 

ND 

No 

No 

No 

ND 

No 

ND 

No 

ND 

No 

ND 

ND 

ND 

ND 

No 

m 

No 

No 

No 

HXCDF 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

No 

ND 

No 

ND 

ND 

ND 

1.26 

0.36 

uo 

1.91 

ND 

No 

ND 

ND 

ND 

No 

ND 

HPCDF 

No 

No 

No 

ND 

No 

No 

ND 

No 

No 

Ii!47 

No 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

ND 

No 

7.w 

No 

ND 

ND 

ND 

No 

No 

ND 

No 

13.76 

1.20 

9RNo 

13.43 

No 

ND 

No 

No 

ND 

No 

No 

HPCDF 

ND 

No 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

No 

ND 

No 

No 

No 

No 

No 

No 

ND 

No 

ND 

ND 

ND 

No 

No 

m 

ND 

ND 

No 

GRNO 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

TEC 

44.32 

7.04 

61.74 

50.08 

1.52 

1.92 

1.32 

5.66 

1.42 

3.28 

1800.32 

56.33 

45.99 

1.25 

l.B2 

0.67 

ND 

1.67 

1.63 

6.: 

5.75 

8.64 

0.23 

6.66 

0.21 

f :E 

3.01 

5% 

No 

m 

15.27 

7.23 

ND 

17.M 

0.03 

2.93 

22.M 

1.97 

4.47 

3.64 

1.02 

D-623 
Episods SCC Type Description 

3450 DYO223W F PF Mite Croaker 

3451 DYO22310 F PF Wlitc Croaker 

3451 DIO22314 F PF White Croaker 

3452 OF025218 F US Sm Buffalo 

3452 OF025219 F BF Blue Catfish 

3452 OF025220 F PF Flathead Catfish 

3452 PO103189 L w Sm Buffalo 

2378 

TCDD 

12378 

PECDD 

2.24 ND 

1.93 ND 

1.22 ND 

9.01 ND 

40.73 1.06 

2.26 ND 

9.03 ND 

123478 

HXCDD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

123678 

HXCDD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DlDXlN / FURAN CDNCENTRATIWS, w/g 

123789 1234678 2378 12378 23478 

HXCDD HPCDD TCDF PECDF PECDF 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND 17.37 ND 

ND ND 10.98 ND 

ND ND ND ND 

ND ND 16.85 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

123478 123678 123789 234678 1234678 1234789 DPE 

HXCDF* HXCDF HXCDF HXCDF HPCDF HPCDF TEC 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 2.24 

ND ND 1.93 

ND ND 1.22 

ND ND 10.75 

ND ND 42.36 

ND ND 2.26 

ND ND 10.72 

D4-24 
Dioxins/Furans 

Detection Limits 

D+25 
04-26 
Episode SCC Type Description 

1994 DE017702 F UR Carp 

lW4 DE017703 F PF Welleye 

1994 90110586 1 U8 Carp 

1998 13285 F UB Carp 

1998 13421- F PF Pike 

2015 DFOOlOOl F UR Carp 

2015 DFOOlDO2 F UP Crappie 

2016 DFOOllOl F UR Sucker 

2016 DFOOllO2 F 8F Sucker 

2017 OF001201 F u8 Carp 

2017 OF001202 F 8F Carp 

2018 OF001301 F US Sucker 

2023 OF001402 F PF Spotted Bass 

2023 OF001403 F Ull Carp 

2026 OF001702 F Ug Carp 

2026 OF001703 F PF Uhite Crappie 

2027 OF001802 F PF Lm Bass 

2027 DFOOlJM3 F UR Carp 

2037 DYOOO501 F UR not available 

2037 DY000502 F UP not available 

2056 DE000501 F UR Carp 

2057 DEOOD601 F VB Carp 

2059 DE000801 F U8 Carp 

2060 DEODWDl F UB Carp 

2070 DJOOO9Dl F UP Rainbow Trout 

2070 DJOOWOZ F UR Longnose Sucker 

207OQDO72186LUP Rainbow Trout 

2098 DN001501 F UR not available 

2098 OH001504 F PF not available 

2100 DNOOl702 F PF Sauger 

2100 DHOOl703 F YB Catfish 

2100 a0111086 L UR Catfish 

2105 OH002201 F PF Sauger 

2105 OH002204 F U8 Carp 

2105 ODD63086 L Id8 Carp 

2100 DN002601 F UR not available 

2109 OH002602 F RF not available 

2110 OH002710 F UP 8roun Trout 

2122 OH003901 F PF Rainbow Trout 

2122 OH003904 F UR Uhite Sucker 

2126 00000302 F MI Carp 

2126 DDODO303 F PF Uhite Crappie 

2126 CUM2686 F U8 Carp 

2133 DDDOlOD2 F RF Blue Catfish 

2138 00001501 F UB Redhorse Sucker 

2138 00001504 F PF lm Bass 

2139 DDOOl601 F VB Carp 

2378 

TCOO 

2.:: 

3.:: 

WA 

MA 

WA 

WA 

MA 

MA 

1.13 

1.99 

0.60 

0.67 

MA 

1.94 

0.74 

1.:: 

2.35 

3.:: 

WA 

2.:: 

0.50 

0.50 

8:: 

1.69 

WA 

0.:: 

0.58 

0.40 

0.2: 

0.27 

0.39 

0.81 

6.49 

0.93 

MA 

1.45 

WA 

1.:: 

12378 

PECDD 

30.99 

2.15 

112.58 

5.18 

1.43 

6.04 

1.70 

f :3"7 

4.90 

1.24 

3.09 

0.52 

0.72 

1.52 

2.52 

0.75 

2.07 

1.94 

5.33 

6.33 

NA 

3.:: 

6.64 

1.33 

1.16 

1.17 

0.65 

1.35 

8.80 

8.12 

1.14 

1.75 

1.29 

7.28 

1.23 

0.97 

0.92 

1.74 

9.79 

0.77 

7.44 

5.42 

WA 

2.g 

DIOXIN / FURAN DETECTlOW LIMITS, w/g 

123478 123678 123789 1234678 2378 12378 

HXCDD HXCDD HXCDD HPCDD TCDF PECDF 

3.:: 

WA 

1.00 

1.65 

4.70 

1.28 

0.97 

1.70 

2.:: 

3.37 

1.17 

MA 

1.35 

3.37 

0.90 

::?I 

3.31 

1.69 

0.78 

2.: 

13.32 

3.61 

2.23 

1.50 

1.47 

::: 

2.94 

0.73 

1.45 

0.79 

2.00 

1.02 

1.w 

0.84 

0.78 

6.14 

1.30 

WA 

1.57 

3.52 

2.44 

2.69 

MA 

3.02 

WA 

WA 

2.89 

WA 

1.28 

MA 

WA 

WA 

3.:: 

0.78 

1.62 

MA 

3.37 

0.90 

2.:; 

5.80 

7.:: 

WA 

13.:: 

3.61 

2.23 

1.50 

0.73 

2.58 

23.:; 

0.73 

1.45 

0.79 

12.01 

1.02 

1.96 

0.84 

0.78 

MA 

1.30 

WA 

WA 

WA 

MA 

3.02 

WA 

1.00 

1.65 

3.13 

1.28 

2.93 

1.27 

1.:: 

3.37 

0.78 

1.08 

1.35 

3.37 

0.90 

1.15 

1.50 

2.48 

3.95 

0.78 

1.25 

2.09 

13.32 

3.61 

2.23 

1.50 

0.73 

1.72 

2.29 

2.94 

0.73 

1.45 

0.79 

2.00 

1.02 

1.96 

0.84 

0.78 

1.: 

WA 

1.57 

WA 

2.:; 

MA 

4.19 

99.13 

3.: 

2.:: 

WA 

WA 

MA 

MA 

6.04 

MA 

WA 

WA 

WA 

5.31 

41.78 

6.96 

WA 

MA 

WA 

MA 

WA 

19.59 

MA 

6.12 

4.00 

5.: 

8.87 

6.35 

WA 

5.16 

3.58 

MA 

#A 

4.91 

WA 

WA 

3.: 

WA 

MA 

MA 

MA 

6.49 

WA 

MA 

WA 

6.02 

MA 

WA 

MA 

WA 

WA 

MA 

WA 

1.2 

MA 

WA 

0.60 

0.23 

MA 

WA 

0.89 

WA 

WA 

HA 

WA 

MA 

0.30 

1.75 

0.2: 

0.74 

0.:: 

0.40 

0.48 

0.20 

MA 

0.91 

0.20 

1.18 

WA 

0.:: 

0.85 

0.35 

MA 

HA 

0.59 

WA 

0.98 

WA 

MA 

1.23 

2.45 

0.61 

1.29 

0.70 

WA 

0.37 

0.93 

0.25 

0.31 

0.48 

1.21 

0.33 

0.56 

0.93 

MA 

WA 

0.77 

7.27 

2.:: 

0.58 

0.87 

0.51 

0.30 

0.42 

0.50 

1.02 

0.63 

0.90 

0.37 

0.58 

0.49 

0.36 

0.47 

0.88 

0.44 

0.32 

0.64 

0.59 

WA 

MA 

O.TI 

23478 123478 123678 

PECDF HXCDF' HXCDF 

WA 

0.98 

MA 

#A 

1.05 

1.:: 

1.; 

1.82 

0.37 

0.93 

0.25 

0.77 

0.48 

1.21 

0.33 

0.74 

0.62 

MA 

MA 

WA 

3.:: 

2.58 

0.58 

0.87 

0.51 

0.30 

0.42 

2.83 

0.2 

0.90 

0.37 

0.58 

0.49 

0.36 

0.47 

1.17 

0.73 

0.32 

0.81 

0.59 

MA 

0.: 

MA 

1.50 

2.: 

0.90 

MA 

0.60 

WA 

1.:: 

0.51 

1.65 

0.36 

0.46 

0.69 

1.63 

0.41 

1.05 

0.78 

MA 

10.11 

0.28 

WA 

WA 

4.51 

1.41 

0.94 

0.66 

0.34 

0.69 

1.60 

1.18 

0.79 

1.46 

0.67 

0.85 

0.86 

0.96 

WA 

1.19 

0.39 

0.54 

0.47 

0.80 

MA 

MA 

1.31 

WA 

1.50 

10.18 

0.38 

0.90 

MA 

0.60 

1.11 

0.47 

0.61 

0.51 

1.65 

0.36 

0.46 

0.69 

1.63 

0.41 

0.52 

0.78 

WA 

WA 

0.28 

MA 

1.82 

4.51 

1.41 

0.94 

0.66 

0.34 

0.69 

0.w 

1.18 

0.79 

1.46 

0.67 

0.85 

0.43 

0.96 

0.59 

1.19 

0.59 

0.54 

0.47 

!iE 

2.02 

1.31 

123789 234678 1234678 1234789 

HXCDF HXCDF HPCDF HPCDF 

3.07 

1.50 

1.78 

X:E 

0.74 

0.60 

0.24 

0.47 

0.41 

0.51 

1.65 

0.36 

0.46 

0.69 

1.63 

0.41 

0.52 

0.78 

0.77 

0.79 

0.28 

0.58 

1.04 

4.51 

1.41 

0.94 

0.66 

0.34 

0.69 

0.96 

0.89 

0.79 

1.46 

0.67 

0.85 

0.43 

0.96 

0.59 

1.19 

0.39 

0.54 

0.47 

ia: 

2:75 

1.31 

MA 

1.50 

1.:: 

0.90 

1.87 

0.90 

MA 

0.2: 

0.51 

1.65 

0.36 

0.46 

0.69 

1.63 

0.41 

0.52 

0.78 

2.72 

3.72 

0.28 

MA 

MA 

4.51 

1.41 

0.94 

0.66 

0.34 

0.69 

0.96 

0.89 

0.79 

1.46 

0.67 

0.85 

0.43 

0.96 

0.59 

1.19 

0.39 

0.54 

0.47 

0.80 

WA 

MA 

1.31 

2.2 

3.:: 

1.82 

1.2 

3.:: 

1.21 

1.25 

4.23 

MA 

MA 

1.34 

4.74 

MA 

MA 

WA 

6.57 

MA 

WA 

MA 

WA 

6.82 

2.13 

4.00 

MA 

1.: 

2.79 

2.79 

1.27 

4.13 

2.87 

IA 

1.20 

2.2: 

1.51 

MA 

MA 

1.:: 

MA 

3.: 

8.18 

2.94 

5.14 

0.77 

1.82 

1.57 

1.26 

0.39 

0.87 

0.80 

1.25 

4.23 

MA 

MA 

1.34 

3.16 

WA 

WA 

1.12 

::9"; 

9:: 

3.35 

6.82 

2.13 

4.00 

WA 

14 

2.79 

2.79 

1.27 

4.13 

2.87 

2.52 

1.20 

WA 

1.20 

3.77 

MA 

MA 

1.:: 

0427 
Episode SCC Type Description 

2139 00001604 F PF Rsinbou Trout 

2139 PO071486 F PF Rainbow Trout 

2142 WOO1902 F UB Cotfish 

2142 WOO1903 F PF Lm Boss 

2146 DOW2501 F UB Saltweter Cotfish 

2148 WOO2504 F BF Saltwater Catfish 

2151 WW2t3Dl F PF LIM Bass 

2151 pOW2803 F UB Spotted Sucker 

2152 DO002902 F PF Lm Boss 

2152 DOW2903 F UB lake Chubsucker 

2100 DGW5101 F UB Carp 

2100 DCOG5104 F PF Blucgill 

2191 DGOD52D5 F UB Carp 

2191 DCW5206 F EF Carp 

2191 oOW2486 1 BF Carp 

2194 DGW5501 F NB Carp 

21% DGW5506 F BF Charnel Catfish 

2199 DG006001 F W Carp 

2199 DGW6004 F PF Lm Boss 

2201 DGOO6201 F m Carp 

2201 DGOO6204 F PF Bowfin 

220s DG006601 F UB Carp 

2205 DGW6602 F SF Carp 

2210 DC005401 F W Cotfish 

2211 DC005503 F UB Rcdhorse Sucker 

2212 DCW56D2 F PF Sm Boss 

2212 DCDO%G5 F UB Uhite Sucker 

2215 DCW5W2 F W Carp 

2216 DC006002 F PF Broun Trout 

2216 DCOO6003 F UB Uhite Sucker 

2220 DC006601 F PF Redbreast Sunfish 

2220 DC006405 F UB Catfish 

2225 DC006902 F PC Sm Boss 

2225 DC006903 F UB Shorthead Rcdhorse 

2225 40101387 L UB Shorthead Redhorsc 

2227 DC007102 F PF Lm Boss 

2227 DC007104 F UB Channel Catfish 

2228 DC007201 F PF Longeor Sunfish 

2228 DCW7204 F UB Rcdhorse Sucker 

2228 a0070286 L blB Rcd?orse Sucker 

2231 DCW7503 F UB Gizzard Shad 

2246 DJW2301 F SF Bridgelip Sucker 

2246 DJW2302 F UB Sri&clip Sucker 

2247 DJW2403 F SF Brid~elip Sucker 

2247 DJOO2404 F I(p Hovltain *mitefish 

22BO DFOD52Gl F YB Carp 

2280 OF005204 F SF Channel Cotfish 

DIOXIN / FURAN DETECTlOW LIHITS, w/g 

2378 12318 123478 123678 

TCDO PECDD HXCDD HXCDD 

WA 

WA 

1.60 

1.02 

1.85 

E 

0.33 

0.70 

0.51 

1.12 

0.82 

1.59 

1.06 

1.00 

2.46 

0.40 

WA 

1.14 

6.01 

1.28 

1.12 

0.66 

WA 

WA 

1.80 

WA 

2.75 

0.34 

0.37 

0.70 

1.10 

1.31 

WA 

MA 

0.97 

1.65 

0.62 

2.81 

3.40 

2.70 

0.41 

2.20 

0.98 

0.:; 

0.93 

1.50 

1.11 

MA 

0.92 

1.61 

0.99 

1.13 

1.03 

1.17 

1.53 

1.87 

0.67 

4.28 

2.37 

0.84 

0.56 

1.65 

3.11 

1.13 

13.63 

1.53 

1.74 

l.f2 

10.44 

1.21 

2.74 

1.62 

4.19 

0.70 

0.63 

1.51 

2.62 

0.96 

WA 

MA 

0.90 

MA 

0.97 

2.62 

3.11 

5.30 

0.92 

5.07 

0.94 

3.59 

1.88 

1.08 

1.04 

0.89 

2.47 

2.46 

1.27 

0.77 

0.54 

0.73 

1.55 

0.75 

1.83 

1.20 

2.20 

1.68 

1.12 

0.33 

1.04 

i:Fi 

18.77 

2.38 

1.94 

0.78 

4.78 

2.47 

2.26 

0.20 

3.93 

0.72 

0.71 

1.35 

1.46 

2.47 

MA 

2.:: 

2.46 

1.51 

1.23 

1.47 

1.20 

1.00 

1.35 

0.86 

1.18 

1.25 

0.67 

1.74 

z 

1:84 

1.27 

0.77 

0.54 

0.73 

3.10 

0.75 

3.20 

1.20 

WA 

5.06 

MA 

3.:: 

I.! 

2.2 

1.94 

0.78 

7.97 

2.:: 

1.66 

0.: 

1.06 

3.39 

WA 

1.85 

WA 

1.:: 

MA 

1.51 

4.30 

6.:: 

1.00 

8.78 

WA 

MA 

1.25 

WA 

123789 1234678 

HXCDD HPCDD 

2378 12378 23478 123478 123678 123789 

TCDF PECDF PECDF HXCDF* HXCDF HXCDF 

1.04 

0.89 

1.38 

1.37 

1.27 

0.77 

0.54 

0.73 

1.55 

0.75 

1.83 

1.20 

2.20 

:-E 

0133 

0.69 

0.88 

1.17 

11.55 

2.38 

1.94 

0.78 

4.78 

1.38 

2.26 

0.20 

3.93 

0.72 

0.71 

1.35 

0.97 

1.38 

MA 

1.44 

1.35 

MA 

1.51 

1.23 

1.47 

1.90 

1.00 

1.35 

0.86 

1.18 

1.25 

0.67 

MA 

MA 

1.:: 

MA 

WA 

MA 

MA 

MA 

WA 

WA 

MA 

WA 

MA 

WA 

1.60 

4.62 

MA 

4.70 

MA 

9.92 

7.29 

5.54 

WA 

3.: 

WA 

WA 

4.45 

2.72 

MA 

MA 

MA 

WA 

WA 

1.96 

MA 

MA 

11.91 

MA 

MA 

9.77 

MA 

WA 

5.: 

WA 

WA 

MA 

MA 

MA 

0.90 

0.26 

0.25 

0.55 

0.47 

0.58 

0.90 

0.20 

MA 

1.23 

1.20 

WA 

0.20 

1.20 

0.45 

1.44 

0.29 

WA 

MA 

WA 

WA 

0.86 

MA 

WA 

0.20 

02 

MA 

MA 

WA 

WA 

WA 

MA 

0.47 

MA 

MA 

MA 

0.36 

5.06 

WA 

0.: 

MA 

1.11 MA 

MA MA 

0.99 WA 

0.77 0.85 

0.81 0.81 

0.43 0.43 

0.41 0.41 

0.48 0.48 

0.75 0.75 

0.51 0.51 

0.79 0.53 

0.46 0.46 

MA 2.65 

0.56 0.56 

0.49 0.74 

0.20 MA 

0.27 0.27 

0.20 MA 

0.25 0.25 

1.08 1.08 

0.67 0.67 

0.61 0.61 

0.31 0.31 

1.50 2.26 

0.96 MA 

1.21 1.51 

MA WA 

MA MA 

0.35 0.35 

0.30 0.30 

0.87 0.87 

0.52 MA 

0.78 0.85 

WA WA 

MA WA 

0.76 0.83 

0.77 WA 

0.75 0.75 

1.51 2.65 

1.41 WA 

3.00 WA 

0.40 0.40 

MA 2.03 

0.32 1.62 

0.30 WA 

0.34 0.34 

0.39 0.58 

0.58 

0.45 

2.84 

2.83 

1.20 

0.65 

0.82 

0.68 

1.78 

0.74 

0.66 

1.32 

1.13 

0.65 

0.44 

0.20 

0.41 

MA 

0.37 

1.83 

0.79 

1.21 

0.50 

1.38 

WA 

1.00 

MA 

2.37 

0.42 

0.39 

1.: 

2.84 

MA 

MA 

f :E 

1.17 

MA 

WA 

WA 

0.46 

MA 

2.59 

0.44 

0.76 

0.37 

0.58 0.39 

0.45 0.45 

2.85 2.78 

2.84 2.TT 

1.20 1.20 

0.65 0.65 

0.82 0.82 

0.68 0.68 

0.71 0.71 

0.74 0.74 

0.88 0.44 

0.53 0.53 

1.13 1.13 

0.65 0.65 

0.44 0.44 

0.20 0.20 

0.41 0.41 

0.39 0.39 

0.37 0.37 

1.83 1.83 

0.79 0.79 

1.21 1.21 

0.50 0.50 

i*E 

l:oo 

i-E 

l:oo 

WA 0.20 

E 

0:39 

:-l-l 

0:39 

0.67 0.67 

0.50 0.50 

2.85 2.78 

2.83 2.76 

2.84 2.77 

2.79 2.72 

2.83 2.76 

0.78 0.78 

0.68 0.68 

0.68 0.68 

0.60 0.60 

0.46 0.46 

0.50 0.50 

0.47 0.47 

0.44 0.44 

0.51 0.51 

0.37 0.37 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

0.58 

0.45 

1.96 

1.96 

1.20 

0.65 

0.82 

0.68 

0.71 

0.74 

0.44 

0.53 

1.13 

0.65 

0.44 

0.20 

0.41 

0.39 

0.37 

1.83 

0.79 

1.21 

0.50 

1.38 

WA 

1.00 

0.22 

1.58 

0.42 

0.39 

0.67 

0.50 

1.96 

MA 

MA 

1.92 

1.95 

0.78 

MA 

0.68 

MA 

0.46 

MA 

MA 

MA 

0.51 

0.37 

1.26 

MA 

WA 

1.44 

3.48 

1.31 

0.99 

1.23 

2.:: 

WA 

MA 

2.:: 

1.35 

0.43 

1.30 

0.75 

0.76 

5.33 

2.52 

2.11 

MA 

4.40 

MA 

2.81 

0.52 

0.: 

0.98 

WA 

MA 

1.45 

WA 

WA 

1.42 

WA 

rnA 

WA 

MA 

MA 

1.11 

4.57 

MA 

WA 

0.: 

0.63 

0.91 

2.62 

2.61 

3.48 

1.31 

C.W 

1.23 

MA 

1.36 

WA 

MA 

2.89 

2.37 

1.35 

0.43 

1.30 

0.50 

0.76 

5.33 

2.52 

2.11 

0.87 

4.40 

2.62 

2.81 

0.19 

2.70 

0.80 

0.98 

WA 

WA 

2.62 

2.60 

2.61 

2.56 

2.60 

nA 

WA 

WA 

1.30 

1.11 

1.82 

0.93 

0.93 

MA 

0.58 

D-4-28 
Episode SCC Type Description 

2280 ClDO62386 1 SF Chsmel Catfish 

2283 DF005501 F UB Gray Rcdhorse 

2283 OF005502 F UP l-ear Sunfish 

2290 00003403 F UB Spatted Sucker 

2294 DD003801 F PF lm Boss 

2294 DD003BO4 F WB Carp 

2297 00004102 F UB Carp 

2297 DD004103 F PF lm Boss 

2298 DD0%201 F UB Chemel Cetfish 

2298 00004203 F UP lm Boss 

2301 DD004504 F UP Rock Boss 

2301 DDO71786 1 UP Rock Boss 

2302 00004601 F UB DuiLLback Carpsucker 

2304 DD004BOl F UB Corn 

2304 DD004BO4 F PF lm boss 

2309 DD005301 F UB Carp 

2309 00005304 F PF lm Boss 

2322 OS001301 F UB Uhite Sucker 

2322 OS001304 F PF lm Boss 

2322 a0082686 1 PF not evailable 

2326 DBODl701 F NB Uhite Sucker 

23 

23 

23 

23 

:: 

23 

23 

23 

23 

23 

:: 

23 

:: 

:: 

23 

23 

23 

23 

:: 

23 

24 

;26 DBOO17D4 F PF Rock Boss 

;28 DBOO1904 F PF Chinook Salmon 

Z9 DBOD2004 F PF Brow Trout 

41 WOO6002 F PF lm Boss 

841 DD006003 F UB Carpsucker 

~55 DA001603 F UB White Sucker 

156 DA001702 F PF lm Bass 

156 DA001703 F UB Uhite Sucker 

~58 DA001901 F VP ns 

69 DA003202 F PF lm Boss 

69 DA003203 F UB Uhite Sucker 

69 ODO30387 F UB Mite Sucker 

75 DA003802 F PF Pickerel 

75 DA003803 F WB Uhite Sucker 

176 DAM)3903 F UB White Sucker 

876 GD111886 L UB Uhite Sucker 

~79 DE005404 F PF lm Boss 

880 DE005501 F UB Cerp 

'83 DE005BOl F UB Carp 

J35 DE006002 F UB Uhite Sucker 

185 MI101987 F UB Uhite Sucker 

#ET DE006201 F UB Carp 

#% DE006901 F UB Carp 

~97 DE007201 F UB Suker 

'97 DE007204 F PF Ualleye 

10 DE008501 F UB Csrp 

2378 12378 

TCDD PECDD 

0.40 

0.20 

0.30 

MA 

WA 

1.:: 

1.08 

0.41 

0.07 

0.96 

1.49 

WA 

WA 

MA 

2.39 

1.20 

0.20 

0.36 

0.68 

0.42 

1.17 

MA 

MA 

WA 

WA 

WA 

WA 

3.:: 

1.84 

1.: 

0.51 

3.: 

2.85 

1.39 

MA 

WA 

MA 

MA 

1.04 

1.: 

0.33 

WA 

0.96 

0.62 

1.40 

WA 

WA 

WA 

0.:: 

2.29 

0.26 

2.74 

2.99 

WA 

WA 

MA 

4.74 

0.30 

0.75 

1.75 

1.23 

4.05 

1.85 

5.85 

3.87 

1.12 

2.02 

0.: 

6.24 

7.07 

2.35 

2.01 

0.94 

0.60 

MA 

4.44 

5.40 

2.18 

19.70 

33.59 

WA 

0.: 

0.:; 

0.69 

55.12 

DIOXIN / FURAN DETECTION LIMITS, w/9 

123478 123678 123789 1234678 

HXCDD HXCDD HXCDD 

2378 

TCDF 

12378 

PECDF 

1.32 

1.10 

1.13 

2.:: 

2.2; 

2.47 

1.60 

0.20 

2.47 

2.87 

2.45 

WA 

5.:: 

1.00 

0.83 

1.39 

1.96 

1.46 

1.25 

1.36 

1.89 

2.47 

2.46 

MA 

0.86 

1.62 

6.62 

4.02 

1.46 

0.70 

0.69 

4 

2.41 

2.40 

WA 

2.:; 

2.46 

2.47 

MA 

0.73 

0.53 

1.10 

1.13 

MA 

WA 

3.17 

WA 

::: 

0.20 

3.71 

2.87 

2.09 

WA 

MA 

2.:: 

0.83 

1.39 

1.30 

5.36 

3.49 

1.36 

1.89 

WA 

MA 

1.:: 

MA 

MA 

4.02 

MA 

1.:: 

WA 

2: 

2.40 

38.31 

WA 

MA 

MA 

1.85 

1.:: 

0.80 

#A 

0.53 

1.10 

1.13 

WA 

MA 

1.:: 

1.38 

1.60 

0.20 

2.47 

2.87 

MA 

MA 

MA 

1.94 

1.00 

0.83 

1.39 

1.30 

1.46 

1.25 

1.36 

1.89 

1.38 

1.37 

0.: 

1.62 

6.62 

4.02 

OX 

0.69 

WA 

1.70 

2.41 

2.40 

10.10 

13.12 

1.38 

1.38 

1.38 

1.3 

0.80 

9.10 

WA 

3.10 

7.36 

MA 

WA 

MA 

WA 

1.28 

15.47 

1.28 

19.27 

12.94 

MA 

WA 

MA 

WA 

MA 

1.54 

2.66 

4.86 

WA 

10.70 

3.60 

3.09 

MA 

WA 

2.:: 

WA 

3.:: 

3.69 

WA 

WA 

8.22 

6.05 

4.28 

MA 

MA 

MA 

WA 

WA 

WA 

WA 

0.73 

106.38 

WA 

0.42 

0.41 

MA 

MA 

MA 

WA 

MA 

0.42 

0.20 

3.:: 

WA 

MA 

WA 

WA 

3.: 

WA 

0.73 

2.81 

1.95 

WA 

WA 

WA 

MA 

WA 

MA 

MA 

MA 

0.52 

MA 

WA 

MA 

MA 

WA 

0.:; 

WA 

MA 

WA 

WA 

MA 

WA 

MA 

0.20 

WA 

0.29 

0.25 

0.52 

MA 

0.77 

1.16 

0.77 

0.78 

1.03 

0.20 

0.82 

0.76 

40:27 

WA 

0.44 

0.30 

0.30 

0.32 

0.36 

1.13 

0.59 

0.87 

1.02 

MA 

WA 

0.:: 

3.73 

1.78 

1.04 

0.47 

0.36 

0.30 

OX 

1.04 

0.69 

WA 

WA 

MA 

MA 

0.78 

0.;: 

0.25 

WA 

23478 123478 123678 123789 234678 1234678 1234789 

PECDF HXCDF' HXCDF HXCDF HXCDF HPCDF I HPCDF 

0.44 

0.25 

0.52 

MA 

0.93 

1.:: 

0.85 

1.03 

0.20 

0.82 

0.76 

0.84 

MA 

WA 

1.79 

0.30 

0.30 

0.32 

0.36 

WA 

0.59 

MA 

0.61 

WA 

WA 

0.:; 

MA 

1.78 

1.04 

0.62 

0.36 

0.30 

WA 

MA 

WA 

0.69 

WA 

MA 

MA 

MA 

WA 

0.:: 

0.25 

MA 

0.28 

0.52 

0.78 

WA 

WA 

2.:: 

2.83 

0.96 

0.20 

1.30 

1.13 

MA 

MA 

WA 

0.92 

0.50 

0.45 

0.56 

0.61 

0.53 

0.72 

WA 

MA 

WA 

WA 

0.2 

0.54 

I.2 

0.93 

MA 

0.35 

WA 

8.; 

1.17 

29.: 

WA 

2.: 

WA 

0.47 

0.32 

MA 

0.28 

0.52 

0.52 

MA 

2.83 

2.85 

2.83 

2.85 

0.96 

0.20 

1.30 

1.13 

2.83 

2.: 

0.92 

0.50 

0.45 

0.56 

0.61 

0.53 

8-67 

1:01 

2.85 

2.:: 

0.35 

0.54 

2.64 

1.98 

0.93 

0.61 

0.35 

2.83 

0.90 

1.72 

1.17 

5.17 

11.67 

2.85 

::: 

0.:: 

0.32 

MA 

0.28 

0.52 

0.52 

2.73 

2.76 

2.78 

2.76 

2.77 

0.96 

0.20 

1.30 

1.13 

2.76 

2.79 

2.77 

0.92 

0.50 

0.45 

0.56 

0.61 

0.53 

0.72 

0.67 

1.01 

2.78 

2.76 

2.76 

0.35 

0.54 

2.64 

1.98 

0.93 

0.61 

0.35 

2.76 

0.90 

1.72 

1.17 

0.79 

i:: 

f:Z! 

2.77 

0.31 

0.32 

1.33 

0.28 0.46 0.46 

0.52 

0.52 52::: ::Gj 

MA MA WA 

WA MA 2.61 

1.; 1.:: 

2.62 

2.60 

1.96 2.62 

0.96 3.:: 3.81 

0.20 0.36 0.36 

1.30 6.61 2.64 

1.13 8.89 5.92 

1.95 MA 2.60 

WA MA 2.63 

1.96 WA 2.61 

0.92 6.06 2.42 

0.50 1.40 1.40 

0.45 1.52 1.52 

0.56 2.10 2.10 

0.61 2.30 1.53 

0.53 2.05 1.02 

0.72 1.40 1.40 

3.:: 

#A 1.37 

MA 2.75 

MA MA 2.62 

MA MA 2.61 

WA WA 2.60 

0.35 1.13 1.13 

0.54 1.82 1.82 

2.64 36.36 9.09 

1.98 2.75 2.75 

1.86 3.64 3.64 

0.61 

0.35 0.: 

1.57 

0.72 

1.95 

2.40 2.: 

2.61 

1.37 

1.72 3.59 3.59 

1.17 3.00 3.00 

WA MA 2.67 

2.:: 

WA 2.74 

MA 2.62 

1.96 WA 2.61 

1-w MA 2.62 

MA 

0.31 0.: 

2.61 

0.71 

0.32 0.74 0.74 

WA 42.82 4.50 

0429 
Episode SCC Type Description 2378 

2410 DE008504 F PF Sm Boss 

2416 DEW9101 F UB Carp 

2422 DE009702 F UB Carp 

2427 DE010202 F UB Carp 

2427 DE010203 F PF Uatieye 

2427 00102887 1 PF Walleye 

2429 DE010402 F UB Carp 

2429 DE010403 F PF Ualleye 

2429 BDOlD6B7 1 PF Ualleye 

2430 DE010602 F PF Worthtrn Pike 

2430 DE010603 F UB Redhorst Sucker 

2431 DE010702 F PF Broun Trout 

2431 DE010703 F UB Suktr 

2432 DEOlD710 F UB Redhorse Sucker 

2432 DE010713 F PF Yolleye 

2435 DE011001 F UB longnose Sucker 

2435 DE011004 F PF Brook Trout 

2437 DE011202 F PF Udleye 

2437 DE011203 F UB Csrp 

2439 DE011401 F UB Carp 

2439 DE011402 F UP Sm Boss 

2478 DJW3Wl F SF Sucker 

2478 DJW3902 F SF Sucker 

2500 DC010201 F PF Bass 

2500 DC010203 F UB Black Buffalo 

2532 OF019302 F PF lm Bass 

2532 OF019303 F UB Carp 

2544 OF019202 F UB Blscktsil Redhorse 

2608 DE014501 F PF Uolleye 

2608 DE014504 F UB Carp 

2618 DE015401 F UB Carp 

2618 DE015402 F SF Carp 

2618 DE015403 F UB OuilLback 

2618 DD102OB8 F UB Ouillback 

2651 OS008401 F UB Uhitt Sucker 

2653 DBDOB503 F UB Carp 

2654 DBOOB601 F UB Carp 

2709 DB005101 F UB Cetiish 

2721 DA006502 F UB Sucker 

2722 DA006601 F UB Sucker 

2725 DA006301 F UB Sucker 

2748 DYOO6505 F UB Sucker 

2748 DY006506 F SF not available 

2776 DYOOflOl F UB Carp 

2776 DYDD7103 F PF Trout 

3001 DE019501 F PF Udleye 

3001 DE019502 F UB Uhitt Sucker 

WA 

WA 

MA 

WA 

WA 

MA 

1.x 

WA 

0.99 

0.49 

1.70 

WA 

0.58 

MA 

0.58 

0.58 

0.58 

0.58 

WA 

WA 

0.39 

0.37 

WA 

1.62 

WA 

WA 

1.40 

WA 

WA 

WA 

MA 

WA 

WA 

WA 

WA 

1.88 

7.87 

WA 

1.39 

MA 

0.55 

0.81 

0.72 

1.19 

0.10 

0.28 

DIOXIN / FURAN DETECTION LIMITS, w/g 

12378 123478 123670 

PECDD HXCDD HXCDD 

0.95 

17.66 

NA 

WA 

0.97 

0.92 

13.65 

1.16 

1.25 

0.92 

1.19 

1.: 

z 

1.75 

1.75 

::; 

10.82 

4.54 

1.48 

1.06 

1.38 

1.71 

1.11 

WA 

0.93 

0.95 

NA 

WA 

MA 

MA 

WA 

1.35 

1.)15! 

4.80 

MA 

2.73 

WA 

1.01 

1.11 

1.69 

0.98 

0.37 

0.93 

0.64 

NA 

MA 

2.2: 

2.46 

17.25 

0.63 

0.68 

2.46 

1.88 

2.46 

2.46 

1.45 

1.45 

1.45 

1.45 

1.45 

1.45 

MA 

0.81 

1.40 

1.51 

2.70 

2.92 

2.45 

MA 

2.10 

2.46 

MA 

WA 

2.47 

2.62 

WA 

1.00 

WA 

1.13 

2.79 

2.43 

3.12 

2.46 

1.28 

1.55 

1.97 

0.71 

0.60 

0.90 

0.64 

WA 

MA 

1.: 

1.84 

WA 

0.63 

1.03 

1.84 

1.88 

1.84 

MA 

1.45 

1.45 

1.45 

1.45 

1.45 

1.45 

WA 

1.:: 

1.51 

2.70 

2.92 

MA 

MA 

1.57 

1.84 

MA 

WA 

WA 

MA 

WA 

1.33 

WA 

2.26 

5.59 

MA 

3.12 

WA 

1.28 

1.55 

1.97 

0.71 

0.60 

1.21 

123789 1234678 

HXCDD HPCDD 

0.64 

6.65 

MA 

WA 

1.34 

1.37 

5.07 

0.63 

0.68 

1.37 

1.88 

1.37 

1.37 

1.45 

1.45 

1.45 

1.45 

1.45 

1.45 

MA 

0.81 

1.40 

1.51 

2.70 

2.92 

1.37 

1.s 

1.37 

MA 

MA 

1.45 

1.68 

1.57 

0.66 

1.35 

1.13 

2.79 

3.:: 

MA 

1.28 

1.55 

1.97 

0.71 

0.60 

0.60 

4.15 

WA 

WA 

WA 

WA 

WA 

2.: 

MA 

I.34 

3.28 

1.49 

WA 

5.16 

5.16 

5.16 

WA 

WA 

WA 

MA 

WA 

5.:; 

WA 

4.00 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

MA 

8.;: 

3.: 

WA 

MA 

8.07 

MA 

4.60 

MA 

5.89 

2.99 

1.21 

4.22 

2378 12378 23478 123478 \23678 \23789 

TCDF PECDF PECDF HXCDF* HXCDF HXCDF 

WA 

NA 

WA 

MA 

WA 

MA 

WA 

WA 

MA 

0.53 

WA 

MA 

MA 

WA 

WA 

MA 

0.48 

WA 

0.48 

WA 

WA 

0.29 

0.97 

WA 

0.45 

1.34 

MA 

WA 

MA 

WA 

WA 

WA 

WA 

WA 

WA 

MA 

WA 

WA 

WA 

1.11 

WA 

0.26 

0.32 

1.59 

1.62 

0.51 

2.25 

0.31 

WA 

MA 

WA 

0.75 

WA 

4.54 

0.31 

0.55 

0.77 

0.39 

0.: 

o":z 

0.90 

0.w 

0.90 

0.90 

1.91 

0.99 

0.41 

0.46 

1.03 

0.56 

0.80 

WA 

0.63 

0.77 

WA 

WA 

1.13 

MA 

WA 

0.69 

WA 

0.24 

1.86 

MA 

0.76 

WA 

0.50 

0.43 

0.72 

0.32 

0.20 

0.41 

0.42 

WA 

WA 

MA 

1.06 

1.09 

WA 

0.74 

0.78 

0.85 

0.39 

l.El 

0.90 

0.90 

0.: 

8:: 

WA 

WA 

0.41 

0.46 

1.03 

0.56 

1.07 

WA 

0.74 

NA 

MA 

WA 

WA 

WA 

MA 

0.34 

WA 

0.59 

WA 

MA 

0.76 

WA 

0.50 

0.43 

0.72 

0.64 

0.20 

0.31 

0.29 

UA 

MA 

WA 

UA 

35.: 

0.66 

0.30 

2.83 

0.74 

2.83 

2.83 

1.46 

1.46 

1.46 

1.46 

1.46 

1.46 

WA 

WA 

0.58 

2.08 

0.64 

1.07 

WA 

2.x 

2.88 

WA 

WA 

2.: 

2.83 

0.33 

WA 

0.30 

4.43 

WA 

1.39 

0.:: 

0.65 

1.04 

0.38 

0.21 

0.39 

0.29 

WA 

MA 

2.5 

2.84 

1.84 

0.39 

0.30 

2.64 

0.74 

2.84 

2.84 

1.46 

1.46 

1.46 

1.46 

1.46 

1.46 

0.:; 

0.58 

0.69 

0.64 

1.07 

2.82 

WA 

f :Z 

4.42 

#A 

MA 

2.85 

2.84 

0.33 

2.78 

0.30 

1.32 

2.81 

1.39 

WA 

0.63 

0.65 

1.04 

0.38 

0.21 

0.26 

0.29 

2.18 

2.77 

2.76 

2.70 

2.77 

1.84 

0.26 

0.30 

2.77 

0.74 

2.77 

2.77 

1.46 

1.46 

1.46 

1.46 

1.46 

1.46 

0.46 

0.37 

0.58 

0.69 

0.64 

1.07 

22 

2.44 

2.77 

2.76 

2.76 

2.78 

2.78 

02:z 

2.71 

0.30 

1.32 

2.74 

1.39 

2.77 

0.63 

0.65 

El 

0.21 

0.26 

234678 123467s 1236709 

HXCDF HP& HPCDF 

0.29 

2.45 

MA 

WA 

1.90 

1.96 

1.84 

0.26 

0.30 

1.96 

0.74 

::; 

1.46 

1.46 

1.46 

1.46 

1.46 

1.46 

10.41 

WA 

0.58 

0.69 

0.64 

1.07 

1.94 

1.: 

1.95 

2.:: 

1.96 

1.96 

1.96 

0.33 

MA 

0.30 

1.32 

2.51 

1.39 

WA 

0.63 

0.65 

1.04 

0.30 

0.21 

0.26 

1.13 

4.61 

WA 

MA 

1.:: 

0.: 

0.61 

1.44 

2.37 

1.44 

MA 

4.13 

4.13 

4.13 

4.13 

4.13 

4.t3 

MA 

WA 

1.28 

:-ii 

4:06 

1.45 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

1.33 

0.: 

WA 

WA 

3.77 

WA 

1.37 

1.99 

WA 

WA 

0.71 

1.38 

1.13 

2.30 

2.61 

2.60 

2.54 

2.61 

6.69 

0.64 

0.61 

2.61 

2.37 

2.61 

2.61 

4.13 

4.13 

4.13 

4.13 

4.13 

4.13 

1.06 

0.70 

1.28 

1.80 

2.24 

4.06 

2.59 

2.57 

2.18 

2.61 

2.61 

2.60 

2.62 

2.62 

2.61 

1.33 

2.56 

0.73 

2.:; 

3.77 

2.61 

1.37 

1.99 

MA 

0.: 

0.92 

01-30 
Episode SCC Type Description 

3022 DA008401 F UB mite Sucker 

3022 DA008402 F PF Chain Pickerel 

3023 DA008501 F PF Sm Bass 

3024 DA008601 F PF lm Bass 

3025 DA008701 F UB Uhite Sucker 

3025 DA008702 F PF Chsin Pickerel 

3026 DA009001 F UB Cetfish 

3026 DA009002 F PF lm Boss 

3027 DA009301 F UB Sucktr 

3028 DA008801 F PF Chain Pickerel 

3028 00031787 1 PF Chain Picktrtl 

3034 DG025701 F UB Csrp 

3034 06025702 F PF lm Bass 

3035 DC025801 F UB Carp 

3035 DG025802 F PF Sm Boss 

3036 DC025901 F PF Freshwater Drun 

3036 06025902 F UB Carp 

3036 GD120287 1 PF Freshwater Drun 

3037 DG026001 F UB Carp 

3037 06026002 F PC Black Crappie 

3038 DC026101 F UB Csrp 

3038 06026102 F BF Channel Catfish 

3039 DC026201 F UB Carp 

3039 DG026202 F SF Channel Cstfish 

3040 06026301 F UB Carp 

3040 DG026302 F PF tiitt Crappie 

3041 DGO26401 F SF Channel Catfish 

3041 DG026402 F UB Carp 

3041 90031588 L SF Channel Catfish 

3042 DC026501 F UB Carp 

3042 DGO26502 F PF Northern Pike 

3043 06026601 F UB Carp 

3043 DGO26602 F PF Flathtad Cetfish 

3043 GD111987 1 PF Flathead Catfish 

3044 DG026701 F UB Cerp 

3044 06026702 F PF Flathead Catfish 

3045 DGO26BOl F UB Csrp 

3045 DC0261102 F PF Flathead Cetfish 

3046 06026901 F UB BiBmouth Buffalo 

3047 DC027001 F UB Carp 

3047 DC027002 F PF Sm Boss 

3048 DG027101 F UB Carp 

3048 DC027102 F PF Uhitt Bass 

3049 DC027201 F UB Carp 

3049 DGO27202 F PF Crappie 

3049 a0111087 F PF Crappit 

3050 DGO27301 F UB Bigmuth Buffalo 

2378 

TCDD 

WA 

0.10 

0.99 

0.20 

WA 

0.12 

WA 

WA 

1.19 

0.11 

0.11 

WA 

1.01 

0.2 

0.99 

1.26 

0.99 

#A 

0.16 

MA 

MA 

MA 

1.16 

1.:: 

1.31 

1.03 

WA 

1.30 

0.99 

WA 

MA 

WA 

WA 

MA 

MA 

0.73 

WA 

MA 

1.00 

0.: 

WA 

1.01 

1.13 

MA 

DIOXIN / FURAN DETECTlOW LIMITS. pB/B 

12378 123478 

PECDD HXCDD 

0.:: 

O.% 

0.40 

WA 

0.32 

WA 

MA 

0.50 

0.29 

0.19 

0.:: 

MA 

0.25 

0.92 

MA 

0.92 

WA 

0.20 

WA 

1.50 

WA 

0.95 

WA 

0.98 

WA 

1.23 

WA 

MA 

0.92 

2.39 

0.: 

MA 

1.04 

6.27 

MA 

0.94 

0.: 

MA 

0.32 

0.2 

0.92 

1.22 

MA 

::: 

3.42 

0.76 

E 

2.47 

0.80 

0.87 

0.22 

2.:: 

0.: 

2.46 

2.49 

2.47 

2.46 

0.22 

2.:; 

2.:: 

2.2: 

2.46 

MA 

MA 

2.2: 

0.30 

2.46 

2.45 

2.::: 

1.04 

0.22 

2.45 

2.2: 

02 

2.2: 

2.47 

WA 

123678 123789 1234678 

HXCDD 

23i8. 

TCDF 

i2378 

PECDF 

1.82 

1.04 

1.84 

1.14 

WA 

0.68 

WA 

1.85 

3.61 

0.87 

0.91 

MA 

1.84 

0.:: 

1.84 

MA 

1.84 

WA 

0.22 

WA 

WA 

MA 

WA 

MA 

1.85 

MA 

WA 

WA 

1.2 

WA 

MA 

2.:: 

WA 

MA 

WA 

WA 

1.:: 

WA 

0.44 

MA 

1.84 

1.84 

WA 

1.36 

1.04 

1.38 

1.14 

0.50 

0.68 

MA 

1.38 

0.80 

0.87 

0.22 

1.:: 

1.55 

0.38 

1.37 

,.:"a 

1.37 

0.22 

MA 

NA 

WA 

1.38 

WA 

1.38 

WA 

1.38 

MA 

WA 

1.37 

0.73 

1.37 

1.37 

MA 

1.38 

2.79 

0.22 

1.37 

1.38 

1.38 

5.18 

0.44 

1.;; 

1.38 

1.38 

WA 

3.08 

MA 

5.03 

WA 

WA 

MA 

4.2 

5.09 

3.95 

WA 

1.26 

0.:: 

1.31 

MA 

1.26 

MA 

2.29 

WA 

WA 

WA 

WA 

MA 

MA 

WA 

MA 

WA 

WA 

WA 

WA 

MA 

WA 

WA 

MA 

HA 

MA 

WA 

WA 

WA 

1.:; 

1.:: 

1.26 

MA 

MA 

0.20 

WA 

MA 

WA 

0.20 

MA 

WA 

0.:: 

0.20 

MA 

MA 

MA 

0.97 

0.49 

MA 

0.49 

WA 

0.20 

WA 

0.49 

WA 

0.49 

0.:: 

0.51 

WA 

MA 

WA 

0.48 

MA 

0.:: 

0.2 

1.97 

WA 

MA 

WA 

0.51 

WA 

MA 

MA 

WA 

0.55 

WA 

WA 

0.28 

0.77 

0.37 

0.26 

0.21 

1.85 

0.78 

0.20 

0.19 

0.20 

0.: 

0.2 

0.77 

0.78 

0.77 

0.77 

0.20 

WA 

0.78 

0.: 

0.87 

0.78 

0.77 

0.78 

0.77 

0.: 

WA 

0.77 

0.77 

WA 

0.78 

MA 

0.20 

0.77 

0.: 

2.78 

0.20 

1.32 

0.77 

0.78 

MA 

23478 123478 123678 123789 

PECDF HXCDF* HXCDF HXCDF 

0.:t 

0.85 

0.37 

0.26 

0.32 

WA 

1.:: 

0.19 

0.20 

MA 

0.85 

WA 

0.20 

0.85 

0.85 

0.85 

0.85 

0.20 

WA 

WA 

WA 

0.85 

WA 

0.85 

1.17 

0.89 

MA 

MA 

0.84 

0.90 

0.85 

0.84 

MA 

MA 

1.51 

0.93 

0.84 

WA 

0.85 

MA 

0.20 

MA 

0.85 

0.85 

1.10 

2.80 

0.42 

2.83 

0.51 

0.26 

0.37 

MA 

2.84 

0.34 

0.30 

0.20 

2.: 

0.:: 

2.83 

2.86 

2.83 

WA 

0.20 

MA 

2.84 

2.: 

2.: 

MA 

2.B4 

WA 

2.: 

WA 

2.; 

WA 

2.84 

0.:: 

2.82 

2.:; 

MA 

0.22 

2.: 

2.83 

2.83 

2.81 

0.42 

2.84 

0.34 

0.39 

0.37 

2.85 

2.85 

0.34 

0.30 

0.20 

3.42 

2.84 

2.83 

0.19 

2.84 

2.87 

f :: 

0.20 

2.: 

2.: 

MA 

2.85 

2.83 

2.85 

2.B3 

2.: 

MA 

:-ii 

2:85 

2.85 

0.70 

0.20 

2.83 

2.85 

I-it 

0:22 

3.06 

2.74 

0.42 

2.77 

0.34 

0.26 

0.37 

2.78 

2.78 

0.34 

0.30 

0.20 

2.77 

2.77 

2.76 

0.19 

2.77 

2.80 

2.77 

2.77 

0.20 

2.77 

5:: 

2.77 

2.75 

2.7B 

2.76 

2.78 

2.76 

0.20 

2.76 

0.20 

2.77 

2.76 

2.78 

2.78 

0.28 

0.20 

2.76 

2.78 

2.79 

0.20 

0.22 

f:T: 

2.77 

2.77 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

1.94 

0.42 

1.96 

0.34 

MA 

0.37 

MA 

1.96 

0.34 

0.30 

0.20 

1.2 

MA 

0.19 

1.0s 

1.98 

1.w 

1-W 

0.20 

#A 

1.w 

1.: 

1.2 

1.95 

1.96 

0.: 

1.95 

WA 

1.95 

::: 

1.96 

0.:: 

1.95 

1.: 

2.81 

0.22 

12 

1.96 

MA 

1.:;: 

1.45 

0.79 

3.:: 

1.2: 

1.53 

0.70 

0.27 

1.:: 

MA 

0.44 

1.44 

1.46 

1.45 

WA 

0.35 

MA 

WA 

WA 

1.44 

1.:: 

MA 

MA 

MA 

MA 

1.44 

1.20 

I.2 

MA 

6.: 

0.81 

1.44 

1.:: 

8.87 

0.59 

1.:: 

1.45 

WA 

2.59 

1.28 

2.61 

X:E 

0.71 

2.62 

2.62 

1.02 

0.70 

0.27 

2.62 

2.61 

2.60 

0.44 

2.61 

2.64 

2.61 

2.61 

0.23 

2.61 

2.62 

2.60 

2.61 

2.59 

2.62 

2.61 

2.62 

2.60 

0.22 

2.60 

0.20 

2.61 

2.60 

2.62 

2.62 

1.09 

0.20 

2.60 

2.62 

2.63 

0.42 

0.59 

2.61 

2.61 

2.62 

2.62 

D-4-31 
Episode SCC Type Description 

3060 OF009101 F UB Flathead Cetfish 

3060 DFOG9102 F UB Sm Buffalo 

3061 DFOl9lDS F PF Bass 

3D61 OF019106 F UB Sucker 

3062 OF024024 F UB Blue Cotfish 

3062 OF024324 F SF Gross Carp 

3062 90024324 1 SF Gross Garb 

3062 00071587 F UB Blue Catfish 

3062 SF024324 F SF Gross Cerp 

3063 OF023301 F UB Sea Catfish 

3063 OF023302 F PF Spotted Statrout 

3064 OF023305 H Shellfish 

3064 OF023306 F PF Spotted Sestrout 

3065 OF023419 F SF BiBmouth Buffalo 

3065 OF023420 F UB Flrthtad Catfish 

3065 00022588 1 UB Flsthtad Cstfish 

3066 OF023503 F UB Cstfish 

3066 OF023504 F PF Freshwster Drus 

3068 OF024001 R LIysters 

3068 OF024002 F PF Ail. Croaker 

3069 DFO24W7 F UB Ses Catfish 

3069 DFD24OD8 F PF Trout 

3070 OF024009 F UB Croaker 

3070 OF024010 F PF Sheepshead 

3071 OF024014 F UB Carp 

3072 OF024017 F UB Carp 

3072 OF024018 F PF Uhite Bass 

3072 DDO407BB 1 PF blhite Bass 

3073 OF019221 F NB Uhitt Sucker 

3073 OF019222 F PF Sm Boss 

3073 PO121587 1 UB Nhite Sucker 

3074 OF026017 F PF Brown Trout 

3075 OF024102 F SF Ser Cstfish 

3076 DFO2B502 F UB Charnel Catfish 

3076 OF028503 F PF Spotted Bass 

3077 OF019113 F PF Flathtad Cstfish 

3077 OF019114 F UB Rcdhorse Sucker 

3077 DD121087 1 PF Flsthead Catfish 

3078 DF009118 F IJB Carp 

307B OF023815 F UB Sm Buffslo 

3078 OF023816 F PF Block Croppit 

307B SFW9118 F UB Carp 

3079 OF019205 F PF Uhite Bass 

3079 OF019206 F MB Carp 

3080 OF023317 F HI Carp 

300 OF023318 F PF lm Boss 

3OBO GDD409B7 1 YB Carp 

DIOXIN / FURAN DETECTlOW LIMITS. w/B 

2378 12378 123478 123678 

TCDD PECDO HXCDD HXCDD 

0.40 

MA 

2.:: 

WA 

MA 

WA 

MA 

WA 

I.2 

1.15 

0.99 

WA 

WA 

WA 

MA 

0.99 

1.:: 

MA 

1.00 

1.07 

WA 

WA 

1:: 

1.19 

WA 

1.10 

0.: 

1.00 

0.: 

0.99 

1.09 

0.99 

WA 

WA 

WA 

1.:: 

MA 

WA 

WA 

WA 

0.30 

2.19 

WA 

WA 

WA 

1.03 

0.93 

WA 

0.35 

0.; 

0.92 

0.96 

WA 

WA 

12 

0.92 

1.06 

0.91 

0.: 

0.92 

1.16 

2.:: 

0.92 

0.92 

1.05 

0.92 

MA 

0.48 

0.92 

WA 

0.93 

0.92 

0.99 

0.92 

WA 

WA 

1.47 

MA 

0.91 

1.08 

04 

WA 

0.38 

0.43 

3.18 

0.27 

2.46 

2.47 

2.46 

2.46 

1.37 

2.59 

2.45 

2.46 

2.45 

2.46 

WA 

MA 

2.:: 

2.45 

2.46 

2.69 

2.47 

2.46 

2.2: 

2.47 

2.47 

2.47 

2.47 

2.47 

IA 

0.65 

2.47 

2.:: 

2.44 

2.45 

2.45 

NA 

2.:: 

2.:: 

2.46 

MA 

0.20 

WA 

0.38 

3.92 

WA 

WA 

MA 

1.04 

1.B4 

0.1; 

MA 

1.83 

WA 

1.83 

WA 

WA 

WA 

WA 

l.B4 

1.97 

WA 

WA 

1.85 

1.:: 

1.: 

1.85 

1.85 

WA 

1.85 

WA 

0.65 

1.85 

1.: 

1.83 

1.83 

1.83 

WA 

WA 

1.85 

WA 

1.83 

MA 

WA 

MA 

MA 

123789 1234678 

HXCDD HPCDD 

23i8 

TCDF 

i2378 23478 123478 123678 123789 

PECDF PECDF HXCDF" HXCDF HXCDF 

0.38 

0.43 

WA 

0.27 

1.44 

1.38 

1.37 

1.37 

1.98 

WA 

1.37 

1.37 

1.37 

WA 

1.38 

1.36 

WA 

1.38 

1.37 

1.37 

1.38 

1.38 

MA 

1.37 

1.37 

1.38 

1.38 

1.38 

1.38 

1.38 

1.38 

0.65 

1.38 

1.37 

1.38 

1.37 

1.37 

1.37 

WA 

WA 

1.37 

WA 

1.37 

1.37 

MA 

0.20 

MA 

0.89 

8.35 

MA 

WA 

WA 

WA 

MA 

WA 

WA 

WA 

1.58 

WA 

WA 

MA 

WA 

WA 

WA 

WA 

WA 

l.BO 

MA 

MA 

WA 

MA 

MA 

MA 

WA 

MA 

WA 

WA 

1.:: 

WA 

WA 

WA 

MA 

MA 

WA 

#A 

MA 

WA 

MA 

WA 

WA 

3.:: 

WA 

0.41 

MA 

0.60 

1.17 

WA 

WA 

WA 

WA 

WA 

WA 

MA 

0.:: 

MA 

WA 

WA 

MA 

MA 

MA 

0.:; 

0.49 

MA 

WA 

WA 

WA 

MA 

WA 

MA 

WA 

WA 

0.20 

0.49 

WA 

0.49 

0.48 

0.86 

0.48 

MA 

WA 

MA 

WA 

MA 

WA 

1.: 

MA 

0.20 

0.72 

0.77 

WA 

WA 

0.77 

MA 

MA 

0.45 

WA 

WA 

o":E 

0.77 

WA 

MA 

WA 

0.77 

0.77 

0.99 

0.77 

0.78 

0.77 

0.77 

0.95 

0.78 

0.78 

0.78 

0.78 

0.78 

0.77 

0.20 

0.78 

0.77 

0.77 

85 

0.77 

0.77 

MA 

1.03 

0.: 

WA 

MA 

0.28 

WA 

0.20 

MA 

0.99 

1.27 

WA 

WA 

MA 

0.84 

WA 

0.: 

E 

MA 

MA 

WA 

MA 

0.85 

1.08 

0.84 

MA 

0.85 

0.84 

0.84 

0.: 

0.85 

0.85 

MA 

0.85 

0.87 

0.20 

0.85 

0-i; 

0.86 

0.84 

0.84 

WA 

MA 

0.85 

WA 

WA 

MA 

0.:: 

NA 

0.20 

1.27 

MA 

2.73 

2.:; 

2.82 

MA 

0.97 

WA 

2.: 

2.81 

2.82 

WA 

WA 

MA 

2: 

2.83 

2.83 

2.84 

2.82 

2.81 

WA 

I:$ 

2.84 

2.84 

::: 

0.23 

::: 

2.83 

2.81 

2.81 

2.81 

2.83 

2.: 

0.87 

2.81 

WA 

0.: 

WA 

0.20 

0.20 

2.84 

1.10 

2.84 

2.116 

2.83 

2.84 

1.21 

MA 

MA 

f 12 

2.83 

2.84 

2.82 

WA 

I:: 

2.84 

2.84 

2.85 

2.83 

2.83 

WA 

2.85 

2.85 

2.85 

2.85 

2.85 

2.B4 

0.23 

2.85 

2.84 

2.114 

2.82 

2.82 

2.82 

2.84 

2.81 

2.84 

::2 

5:E 

0.20 

0.68 

0.20 

0.20 

2.77 

0.22 

2.77 

2.77 

2.76 

2.77 

1.40 

::s1: 

2.76 

2.75 

2.76 

f:35 

2.77 

2.77 

2.76 

f:Z 

2.78 

2.76 

2.76 

2.77 

::E! 

2.78 

2.78 

2.78 

2.77 

0.23 

2.78 

5:; 

2.75 

2.75 

2.75 

2.77 

2.74 

2.77 

ST 

f:Z 

0.20 

0.20 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

0.20 

0.20 

1.96 

WA 

2.07 

1.96 

1.95 

1.99 

1.57 

2.14 

1.95 

::E 

1.95 

WA 

1.94 

WA 

::ii 

::: 

1.97 

1.95 

1.95 

1.: 

1.96 

1.96 

1.96 

1.96 

1.96 

0.23 

1.96 

1.; 

1.94 

1.96 

::Fz 

1.95 

1.95 

0.86 

1.95 

WA 

WA 

0.20 

WA 

0.49 

0.47 

MA 

WA 

1.48 

1.45 

1.44 

0.; 

WA 

MA 

WA 

WA 

WA 

MA 

MA 

WA 

1.45 

1.44 

1.44 

WA 

1.45 

MA 

WA 

WA 

1.45 

1.45 

1.45 

1.:: 

1.45 

0.77 

1.45 

WA 

MA 

1.43 

1.44 

1.44 

1.2"; 

1.44 

0.66 

1.44 

MA 

0.5 

WA 

0.49 

0.47 

2.61 

9:: 

2.61 

2.60 

2.61 

1.66 

2.61 

2.60 

2.61 

2.60 

:z 

2:59 

2.62 

2.61 

2.60 

2.61 

2.61 

2.62 

2.61 

2.60 

2.61 

2.62 

2.62 

2.62 

2.62 

2.62 

2.61 

0.77 

2.62 

2.61 

2.61 

2.59 

2.59 

2.60 

2.61 

2.59 

2.61 

::z 

2.61 

0.24 

0.20 

0.26 

D-432 
Episode SCC Type Description 

3081 OF024105 F PF Uhitt Bass 

3081 DFO241W F UB Catfish 

3082 OF023401 F UB Carp 

3082 OF023402 F PF Lm Bass 

3082 a01207117 1 PF lm SOS; 

3083 OF023405 F UB Black Bullhead 

3083 OF023406 F PF lm Bass 

3084 OF024109 F UB Channel Catfish 

3084 PO072188 1 UB Channel Catfish 

3085 OF024114 F PF Black Drun 

3086 OF023409 F NB Cetfish 

3086 OF023411 F PF Block Drun 

3087 OF023413 F UB Carp 

3087 OF023414 F PF Uhite Croppie 

3087 OF023415 F UP Bluegill 

3087 OF023416 F UP lm Boss 

3087 ODO23414 1 PF Uhite Croppie 

3087 00072387 F UB Carp .. 

3087 SF023414 F PF Uhite Cracoie 

3087 SF023415 F UP BlueBill " 

3088 OF023417 F UB Chamel Catfish 

3088 OF023418 F PF Blusgill 

3089 OF019209 F PF Uhite Crappie 

3089 OF019210 F UB Carp 

3090 OF019213 F PF Uhitt Crappie 

3090 OF019214 F UB Chsmel Catfish 

3091 OF019217 F UB River Cerpsurker 

3091 OF019218 F PF Uhitt Crappie 

3092 OF023501 F UB Carp 

3092 OF023502 F PF Uarmouth 

3093 OF024011 F PF la Boss 

3093 OF024118 F UB Sm Buffalo 

3093 4oOBO387 L UB Sm Buffalo 

3094 DC017201 F SF Chamcl Cstfish 

3094 PO092988 1 SF Channel Cstfish 

3095 DC038801 F SF Broun Bullhead 

3095 DC038802 F UB Channel Cetfish 

3096 DC035001 F SF Brown Bullhead 

3096 DC035002 F UB Channel Catfish 

3096 00052488 F UB Channel Catfish 

3097 DC038701 F SF Brow Bullhead 

3097 DC038702 F UB Csrp 

3098 DC038601 F UB Uhite Suktr 

3098 DC038602 F PC Americsn Eel 

3098 00032587 1 UB Uhite Suktr 

3100 DC019701 F PF Uhitt Perch 

3100 DC019702 F UP Uinter Flounder 

2378 

TCDD 

MA 

MA 

1.43 

1.04 

1.12 

1.08 

0.11 

MA 

WA 

WA 

4.32 

0.99 

WA 

WA 

MA 

MA 

WA 

WA 

MA 

WA 

WA 

II A 

0.99 

1.05 

0.98 

1.27 

0.99 

0.98 

MA 

0.98 

1.01 

WA 

1.07 

WA 

WA 

5.:: 

WA 

MA 

WA 

WA 

MA 

WA 

WA 

WA 

12378 

PECDD 

5.39 

2.89 

WA 

0.93 

1.01 

0.2 

WA 

WA 

1.46 

MA 

0.92 

MA 

WA 

MA 

1.97 

MA 

WA 

WA 

0.; 

0.94 

0.98 

1.04 

0.91 

0.: 

0.91 

WA 

0.94 

0.92 

MA 

MA 

MA 

WA 

WA 

4.92 

1.07 

MA 

WA 

4.78 

MA 

MA 

WA 

MA 

1.:: 

DIOXIN / FURAN DETECTION LlHIfS, w/g 

123478 123678 123789 1234678 2378 12378 

HXCDD HXCDD 

0.76 

WA 

3.57 

2.43 

2.43 

WA 

0.20 

2.47 

2.47 

2.46 

2.2: 

4.93 

2.45 

2.46 

2.46 

2.46 

WA 

1.11 

1.36 

2.46 

2.46 

2.45 

2.46 

2.44 

2.46 

2.46 

2.44 

2.:: 

2.46 

WA 

2.:: 

2.46 

2.46 

3.37 

2.46 

3.69 

18.:: 

2.47 

4.01 

2.73 

0.29 

2.47 

2.56 

WA 

MA 

WA 

1.82 

1.81 

0.2 

2.51 

WA 

MA 

WA 

1.84 

WA 

1.83 

WA 

1.97 

MA 

0.: 

WA 

1.2 

1.83 

MA 

1.82 

I.2 

1.82 

1.: 

1.84 

WA 

WA 

MA 

MA 

MA 

MA 

WA 

MA 

6.:; 

MA 

WA 

WA 

WA 

MA 

1.91 

0.68 

MA 

WA 

1.36 

1.35 

0.2 

1.38 

WA 

1.41 

1.55 

1.37 

WA 

1.37 

1.37 

1.38 

1.37 

2.94 

1.32 

1.98 

1.: 

1.37 

1.38 

1.36 

1.:: 

1.36 

1.:: 

1.37 

MA 

WA 

1.37 

WA 

1.38 

MA 

1.37 

2.12 

3.:: 

MA 

0.44 

NA 

WA 

1.38 

1.43 

HPCDD TCDF PECDF 

WA 

MA 

MA 

MA 

WA 

2.:: 

MA 

WA 

NA 

WA 

1.32 

WA 

1.25 

2.37 

WA 

MA 

WA 

WA 

WA 

MA 

NA 

1.29 

1.:: 

WA 

IA 

1.25 

MA 

WA 

WA 

WA 

WA 

MA 

MA 

MA 

MA 

WA 

#A 

24.:; 

15.14 

MA 

WA 

WA 

MA 

MA 

WA 

0.50 

MA 

MA 

WA 

0.:: 

WA 

WA 

WA 

MA 

MA 

MA 

WA 

WA 

MA 

WA 

WA 

WA 

WA 

WA 

MA 

WA 

WA 

MA 

0.:: 

0.48 

MA 

0.48 

0.48 

0.86 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

WA 

MA 

WA 

0.20 

MA 

WA 

MA 

0.20 

0.77 

MA 

0.77 

0.76 

0.77 

0.20 

0.87 

MA 

WA 

WA 

MA 

MA 

MA 

MA 

0.96 

WA 

MA 

MA 

0.: 

0.77 

0.77 

0.77 

0.76 

0.: 

0.76 

0.77 

0.77 

0.77 

0.77 

0.77 

8:: 

MA 

NA 

0.85 

WA 

WA 

1.87 

MA 

0.51 

0.20 

0.43 

WA 

1.14 

23478 123478 123678 123789 

PECDF HXCOF' HXCDF HXCDF 

0.44 

WA 

1.76 

0.84 

0.83 

0.:: 

MA 

MA 

WA 

WA 

0.84 

WA 

MA 

WA 

MA 

MA 

MA 

WA 

0.: 

8% 

0.: 

0.: 

0.84 

1.53 

0.84 

0.84 

MA 

IA 

#A 

WA 

MA 

WA 

MA 

MA 

MA 

WA 

WA 

0.2 

WA 

WA 

WA 

0.20 

2.82 

MA 

2.80 

2.79 

2.83 

0.20 

2.84 

MA 

WA 

2.:: 

WA 

2.81 

2.83 

2.83 

2.82 

2.94 

0.94 

0.96 

2.83 

5-E 

2:83 

2.81 

2.82 

2.83 

2.80 

2.89 

2.82 

2.83 

2.: 

MA 

WA 

MA 

MA 

2.83 

MA 

MA 

1.71 

WA 

0.21 

0.20 

1.21 

WA 

2.94 

0.20 

2.83 

3.19 

2.81 

2.80 

2.M 

0.20 

2.85 

2.85 

3.: 

2.83 

2.: 

2.84 

2.84 

2.84 

MA 

1.18 

1.20 

2.84 

2.83 

2.83 

I:2 

2.83 

2.84 

2.82 

2.04 

2.83 

2.84 

3.70 

2.84 

WA 

MA 

3.: 

2.84 

3.82 

WA 

0.85 

0.:: 

0.20 

0.30 

2.85 

2.95 

0.20 

2.76 

2.76 

2.74 

2.73 

2.T7 

0.20 

2.78 

2.77 

2.TI 

2.77 

2.76 

2.76 

2.75 

2.TI 

2.77 

2.76 

2.78 

1.07 

1.40 

2.77 

2.76 

2.76 

::55 

2.76 

2.77 

2.74 

2.77 

2.76 

2.77 

3.29 

2.77 

2.77 

2.77 

2.76 

2.77 

2.77 

2.77 

2.78 

0.51 

2.78 

0.20 

0.20 

0.21 

f :E 

234678 1234678 1234789 

HXCOF HPCDF HPCDF 

0.20 

1.95 

2.16 

1.93 

1.93 

1.95 

0.20 

1.96 

1.96 

MA 

WA 

1.95 

1.; 

1.96 

1.96 

1.95 

1.::. 

1.57 

1.96 

1.95 

1.95 

1.96 

1.94 

1.95 

2.14 

1.94 

1.96 

1.95 

1.96 

3.23 

1.95 

1.96 

MA 

3.2 

1.96 

MA 

0.2 

2.:: 

MA 

1.2 

2.03 

0.32 

WA 

WA 

1.46 

WA 

1.44 

0.27 

1.45 

WA 

WA 

WA 

1.44 

1.76 

1.44 

1.44 

1.44 

1.44 

0.: 

0.70 

1.44 

1.44 

1.44 

1.:: 

1.76 

MA 

1.43 

MA 

1.44 

1.44 

1.45 

1.57 

WA 

MA 

2.:: 

1.44 

3.25 

2.81 

1.37 

WA 

MA 

MA 

WA 

1.45 

WA 

0.20 

2.60 

2.61 

2.58 

2.57 

2.61 

0.20 

2.62 

2.62 

MA 

2.61 

::: 

2.60 

2.61 

2.61 

2.61 

2.61 

1.65 

2.07 

2.61 

I:: 

2.61 

2.59 

f :: 

2.59 

2.61 

5:: 

2.62 

2.61 

2.61 

2.61 

Z 

2.61 

2.61 

2.62 

0.91 

2.62 

0.35 

0.20 

0.40 

2.62 

2.71 

0433 
Episode See Type Description 

3101 DC019901 F PF Brom Trout 

3103 DC036201 F UB Channel Catfish 

3103 DC036202 F W Csrp 

3104 DC020001 F PF ln Boss 

3104 DCO2WO2 F W Carp 

3105 DFO25Wl F UB Cerp 

3105 DFO25W2 F PF lm Boss 

3106 DE026801 F PF Uolleyt 

3106 DE026802 F PF Uhfte.Bass 

3107 DE026901 F W Car0 

3100 DE027001 F PF Uolieye 

3108 DE027002 F W Carp 

3109 DEO25Wl F W Corn 

3109 u lO25002 F PF Sm ioss 

3110 I: LO22501 F SF Carp 

3111 0 1015BOl F PF Urlleye 

3111 D 1015802 F UB Sflvtr Redhorst 

3112 0 1022401 F m Carp 

3112 U iO22402 F PF Ualleyt 

3113 0 iO21101 F SF Chsnne~ Catfish 

3113 0 LO21102 F SF Carp 

3114 c iD21201 F SF Carp 

3115 u :021301 F W Carp 

3115 0 iO21302 F SF Catfish 

3117 0 iO21501 F PF Lekt Trout 

3117 0 iO21502 F PF Brow Trout 

3118 0 iO21601 F PF UdLeye 

3118 0 iO21602 F UB Carp 

3118 D iO21603 F HI Carp 

3118 s iO21602 F W Carp 

3119 D 1021701 F W Csrp 

3119 0 iO21702 F PF lm Boss 

3120 DE021801 F W Carp 

3120 DE021802 F PF Boss 

3122 DE022001 F W Carp 

3122 DE022003 F W Rtdhorst Sucker 

3122 DE022004 F PF Sm Bass 

3125 DE022301 F W Carp 

3125 DE022302 F PF Ubitc Bass 

3125 OD1208B8 1 PF Uhitt Boss 

3132 DE023201 F W Carp 

3132 DE023202 F UB Channel Catfish 

3134 DE023401 F PF Croppit 

3134 DE023403 F W Cork 

3134 DE023405 F W CarD 

3134 DE023406 F W Sucker 

3135 DE023501 F W Carp 

2378 

TCDD 

1.88 

3.67 

MA 

1.24 

MA 

MA 

0.99 

MA 

NA 

2.38 

0.98 

MA 

WA 

WA 

1.67 

0.09 

1.16 

MA 

1.26 

1.60 

MA 

MA 

WA 

WA 

MA 

2.44 

WA 

WA 

MA 

MA 

4.64 

MA 

WA 

MA 

MA 

MA 

WA 

WA 

MA 

MA 

MA 

WA 

MA 

3.71 

MA 

WA 

MA 

12378 

PECDD 

1.00 

1.:: 

0.95 

2.99 

WA 

0.91 

0.98 

WA 

WA 

1.03 

WA 

MA 

0.97 

MA 

0.23 

2.64 

1.t 

WA 

MA 

1.35 

MA 

MA 

WA 

MA 

1.73 

WA 

MA 

WA 

MA 

::: 

1.53 

MA 

0.22 

0.24 

WA 

1.02 

0.92 

WA 

0.; 

MA 

1.:: 

1.49 

DIOXIN / FURAN DETECTIOll ~~ __.~.~ LIFIITS, w/g 

123478 123678 123789 1234678 2378 12378 

HXCDD HXCDD HXCDD HPCDD TCDF PECDF 

2.46 

WA 

MA 

2.44 

,.a: 

2.45 

2.46 

2.46 

2.45 

2.45 

2.47 

2.43 

2.44 

WA 

0.29 

0.20 

2.:: 

2.45 

2.46 

::: 

2.46 

2.45 

2.52 

2.47 

WA 

MA 

WA 

0.59 

0.24 

WA 

0.89 

MA 

0.32 

0.32 

2.:; 

2.46 

2.:: 

2.49 

2.43 

2.45 

2.46 

2.47 

1.84 

MA 

WA 

1.83 

MA 

2.05 

1.83 

WA 

2.53 

MA 

1.83 

MA 

IA 

1.83 

NA 

0.29 

MA 

WA 

1.84 

MA 

WA 

MA 

WA 

WA 

#A 

1.: 

MA 

NA 

MA 

2.:: 

MA 

0.89 

WA 

1.51 

0.32 

MA 

1.85 

1.84 

#A 

MA 

1.86 

WA 

MA 

1.84 

MA 

1.37 

MA 

1.37 

1.36 

WA 

1.37 

1.37 

1.37 

1.37 

1.36 

1.36 

MA 

1.36 

1.36 

MA 

0.29 

0.20 

WA 

1.37 

1.37 

1.72 

1.38 

WA 

1.: 

1.41 

1.38 

1.37 

1.37 

1.22 

1.31 

0.24 

0.20 

0.89 

0.:: 

0.32 

1.38 

1.38 

1.38 

WA 

1.:: 

1.36 

1.37 

1.38 

1.38 

1.27 

MA 

WA 

MA 

MA 

MA 

WA 

MA 

NA 

WA 

1.25 

MA 

MA 

1.25 

WA 

2.26 

2.57 

MA 

MA 

MA 

WA 

WA 

MA 

MA 

MA 

1.:: 

WA 

WA 

WA 

MA 

111.71 

3.:: 

2.:: 

MA 

WA 

MA 

MA 

MA 

WA 

1.27 

MA 

MA 

MA 

WA 

WA 

0.70 

MA 

MA 

MA 

MA 

0.48 

MA 

NA 

WA 

WA 

0.:; 

MA 

WA 

0.28 

MA 

WA 

MA 

WA 

MA 

WA 

MA 

MA 

WA 

MA 

MA 

WA 

WA 

WA 

MA 

MA 

WA 

WA 

MA 

WA 

MA 

MA 

WA 

WA 

WA 

MA 

MA 

MA 

WA 

MA 

WA 

MA 

WA 

WA 

0.77 

0.: 

0.77 

0.77 

NA 

0.: 

0.: 

0.78 

WA 

0.20 

0.31 

1.20 

0.77 

1.08 

MA 

MA 

WA 

0.95 

1.:: 

0.98 

WA 

WA 

0.; 

0.37 

0.:: 

1.98 

0.31 

0.30 

WA 

0.88 

0.83 

1.62 

1.45 

0.78 

MA 

WA 

WA 

0.78 

23478 123478 123678 123789 

PECDF HXCDF* HXCDF HXCDF 

MA 

WA 

MA 

0.84 

MA 

02 

0.89 

1.94 

WA 

0.84 

1.:: 

1.03 

WA 

0.20 

0.63 

1.80 

0.84 

MA 

WA 

MA 

WA 

MA 

MA 

WA 

MA 

MA 

WA 

1.:: 

1.17 

MA 

0.60 

MA 

0.2 

MA 

1.26 

WA 

MA 

WA 

0.86 

MA 

MA 

WA 

1.47 

2.82 

WA 

MA 

2.80 

WA 

2.: 

2.83 

3.01 

3.72 

2.81 

WA 

2.:: 

MA 

0.20 

0.20 

3.39 

2.83 

2.81 

2.:: 

MA 

3.04 

2.: 

2.B3 

2.82 

WA 

MA 

1.25 

0.20 

WA 

0.57 

MA 

0.20 

0.20 

MA 

2.84 

2.83 

WA 

WA 

2.86 

WA 

2.: 

2.84 

2.83 

MA 

2.84 

2.82 

2.:: 

2.83 

5:: 

2.81 

2.82 

3.29 

2.80 

2.82 

2.81 

0.20 

0.20 

2.85 

2.84 

2.82 

MA 

2.84 

2.89 

2.84 

MA 

2.84 

2.85 

MA 

WA 

WA 

0.57 

0.20 

0.58 

0.20 

0.2 

0.20 

2.: 

2.84 

2.91 

2.82 

2.87 

2.80 

2.82 

2.84 

2.85 

2.76 

2.77 

2.n 

2.75 

2.74 

2.76 

2.76 

2.n 

2.77 

2.: 

2.78 

2.73 

2.75 

2.74 

0.20 

0.20 

2.: 

2.75 

2.77 

2.77 

2.76 

2.77 

2.76 

2.77 

2.78 

2.76 

2.n 

0.88 

0.20 

0.20 

0.20 

0.20 

2.76 

0.20 

0.20 

2.m 

2.78 

2.77 

2.76 

2.75 

2.80 

2.73 

2.75 

2.77 

2.m 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

1.95 

MA 

WA 

1.94 

MA 

::: 

1.w 

1.99 

WA 

1.94 

WA 

MA 

1.94 

MA 

0.20 

0.20 

2.32 

1.96 

1.95 

WA 

1.96 

1.95 

1.96 

WA 

1-W 

MA 

::2 

0.86 

WA 

0.28 

MA 

0.20 

0.:: 

0.20 

2.13 

1.96 

1.96 

WA 

1.: 

2.06 

1.95 

2% 

1.44 

MA 

MA 

1.43 

MA 

MA 

WA 

MA 

MA 

1.:: 

WA 

WA 

1.43 

MA 

0.28 

0.26 

WA 

1.44 

1.44 

WA 

1.45 

MA 

2.13 

1.44 

1.44 

1.48 

WA 

MA 

WA 

1.36 

0.72 

WA 

0.73 

WA 

0.25 

0.25 

MA 

1.45 

1.47 

MA 

1.:: 

1.59 

1.46 

1.45 

MA 

2.60 

2.61 

2.61 

2.59 

2.59 

2.60 

2.60 

2.61 

2.61 

2.59 

2.60 

2.:: 

2.59 

2.59 

0.28 

0.26 

2.61 

2.61 

2.60 

2.61 

2.61 

2.60 

2.61 

2.60 

2.61 

2.62 

2.60 

2.61 

1.65 

0.27 

0.36 

0.21 

0.48 

2.61 

0.25 

0.25 

2.62 

2.62 

2.65 

2.60 

2.59 

2.64 

2.57 

2.60 

2.61 

2.62 

D-434 
Episode SCC Type Description 2378 

3136 DE023602 F PF 

3137 DE023701 F W 

3137 DE023702 F PF 

3138 DE023801 F W 

3138 DE023802 F PF 

3140 DE024002 F W 

3141 DE024102 F UB 

3141 DE024103 F PF 

3141 SE024102 F W 

3142 DE022502 F W 

3143 DE024401 F 

3143 DE024402 F PF 

3143 DE024403 F W 

3144 DEO24Wl F UB 

3145 DE026601 F W 

3145 D00719BB F UB 

3146 DE026701 F UB 

3146 DE026702 F PF 

3146 00060288 1 W 

3146 SE026701 F W 

3147 DC035201 F UB 

314B DE027101 F UB 

3148 DE027103 F PF 

3149 DC038501 F W 

3150 DA008901 F UB 

3151 DA009101 F W 

3151 DA009102 F PF 

3151 90072887 F UB 

3152 DA009201 F m 

3161 DCO19B01 F SF 

3161 DCO19B02 F UB 

3162 DJD22121 F W 

3162 05022122 F W 

3162 05022123 R 

3162 DJO22403 F PF 

3162 DJO24Wl F W 

3162 OJO25103 0 

3162 90041889 0 

3163 05022402 M 

3163 05022404 W 

3163 DJ024002 F LIP 

3163 DJD25102 0 

3164 00015701 F PF 

3164 00015702 F UB 

3165 00015703 F PF 

3165 00015704 F UB 

3165 DDO317BB 1 PF 

Walleye 

Redhorst Sucker 

Ualleye 

Cerp 

Sm Bass 

Carp 

Carp 

Northern Pike 

Carp 

Carp 

Rotten (cetf) 

Uhite Boss 

Carp 

Carp 

N. Rcdhors 

N. Redhorst 

Carp 

Ual leyt 

Carp 

Carp 

Carp 

Carp 

Ualltye 

Uhitt Suktr 

Uhite Suktr 

Uhitt Sucker 

Sm Bass 

Uhite Sucker 

Uhitt Suktr 

Black Bullhtad 

Uhitt Sucker 

Big Skate 

Rstfish 

Dvlgeness Crab 

Quillbck Rackfish 

Starry Flounder 

Hepatopancreas,Crab 

Htpatopancreas 

Dun~eness Crab 

D~eness Crab 

Starry Fhnder 

Nepatopancreas,Crsb 

lm Boss 

Carp 

Lm Bass 

Rcdhorse Sucker 

lm Boss 

0.97 

1.35 

1.00 

1.:: 

MA 

MA 

MA 

WA 

1.:: 

1.00 

MA 

MA 

WA 

WA 

MA 

MA 

WA 

MA 

MA 

1.: 

0.51 

MA 

MA 

WA 

WA 

1.: 

MA 

MA 

1.:: 

1.12 

MA 

MA 

MA 

MA 

2.24 

WA 

1.: 

I.2 

WA 

MA 

12378 

PECDD 

0-w 

1.29 

0.92 

WA 

1.22 

1.35 

WA 

MA 

MA 

1.:: 

0.99 

MA 

#A 

1.09 

MA 

WA 

0.97 

MA 

WA 

WA 

WA 

0.91 

0.52 

WA 

4 

WA 

MA 

WA 

WA 

WA 

1.03 

1.81 

1.04 

MA 

WA 

MA 

MA 

WA 

MA 

64.:; 

1.: 

MA 

1.86 

DIOXIN / FURAN DETECTlOW LIMITS, w/B 

123478 123678 123789 1234678 

2.41 

2.45 

2.47 

3.21 

2.46 

2.95 

6.72 

2.47 

MA 

2.:: 

2.47 

2.:: 

2.46 

2.47 

2.:; 

2.46 

2.:: 

2.:: 

0.81 

2.2; 

2.45 

2.73 

2.45 

WA 

2.:: 

2.45 

2.74 

2.45 

2.47 

WA 

2.1: 

2.45 

2.47 

2.47 

2.46 

2.46 

2.46 

2.:: 

1.80 

1.83 

1.85 

2.41 

MA 

MA 

WA 

WA 

MA 

MA 

3.93 

1.85 

WA 

2.32 

WA 

WA 

MA 

1.84 

IA 

WA 

MA 

WA 

::fi 

MA 

MA 

1.83 

WA 

WA 

WA 

WA 

MA 

3.:: 

1.83 

WA 

MA 

WA 

MA 

MA 

WA 

MA 

WA 

WA 

WA 

WA 

WA 

HXCDD HPCDD 

1.34 

1.37 

1.38 

1.88 

1.37 

1.38 

1.:: 

WA 

WA 

1.37 

1.38 

WA 

1.37 

1.37 

1.38 

3.58 

1.38 

MA 

MA 

1.38 

WA 

1.37 

0.81 

WA 

MA 

1.37 

1.:: 

WA 

1.: 

1.37 

1.56 

1.37 

MA 

MA 

5.K 

1.40 

1.38 

MA 

WA 

1.:: 

2.13 

1.38 

1.23 

MA 

1.34 

1.26 

WA 

MA 

MA 

WA 

MA 

WA 

WA 

WA 

HA 

MA 

MA 

MA 

MA 

MA 

MA 

WA 

WA 

MA 

0.: 

WA 

MA 

1.25 

WA 

WA 

MA 

MA 

2.: 

l.z: 

MA 

MA 

WA 

WA 

WA 

MA 

MA 

WA 

#A 

WA 

WA 

WA 

2378 12378 23478 123478 

TCOF PECDF PECDF HXCDF* 

0.50 

#A 

0.55 

WA 

MA 

WA 

MA 

WA 

WA 

MA 

WA 

MA 

WA 

WA 

MA 

WA 

MA 

WA 

WA 

MA 

WA 

MA 

MA 

MA 

WA 

NA 

WA 

WA 

WA 

WA 

MA 

MA 

WA 

MA 

MA 

WA 

MA 

WA 

MA 

MA 

WA 

NA 

MA 

WA 

WA 

0.2 

0.76 

0.89 

0.78 

0.:: 

0.87 

#A 

WA 

WA 

MA 

1.34 

WA 

WA 

WA 

0.2 

0.: 

WA 

MA 

WA 

MA 

0.77 

0.25 

MA 

0.; 

WA 

MA 

WA 

MA 

MA 

WA 

1.:: 

MA 

MA 

WA 

WA 

0.2 

4.:: 

0.: 

0.: 

0.83 

1.29 

0.85 

7.13 

MA 

WA 

WA 

HA 

WA 

1.:: 

WA 

MA 

MA 

MA 

WA 

WA 

0.85 

WA 

WA 

WA 

WA 

WA 

0.25 

2.23 

WA 

IA 

WA 

IA 

WA 

MA 

MA 

MA 

0.: 

WA 

MA 

MA 

WA 

MA 

MA 

,93.z 

WA 

WA 

WA 

MA 

2.77 

2.82 

2.84 

2.83 

2.82 

2.83 

2.: 

WA 

2.: 

2.04 

2.: 

2.83 

2.83 

2.: 

MA 

MA 

IA 

2.tl: 

3.33 

MA 

2.: 

WA 

2.: 

WA 

MA 

WA 

2.: 

MA 

WA 

MA 

WA 

WA 

WA 

MA 

WA 

MA 

MA 

WA 

MA 

123678 123789 234678 1234678 1234789 

2.78 

2.83 

2.85 

2.84 

2.84 

2.84 

2.: 

WA 

2.: 

2.85 

3.82 

2.84 

2.84 

2.85 

2.2 

MA 

2.: 

3.50 

2.B3 

0.33 

4.61 

2.85 

2.B2 

2.84 

2.B3 

2.61 

MA 

3.: 

2.; 

MA 

WA 

MA 

7.:; 

2.85 

2.2 

2.2 

3.31 

2.85 

2.71 

2.76 

2.78 

2.77 

2.76 

2.77 

2.77 

2.78 

0.89 

2.76 

2.76 

2.78 

2.Ts 

2.77 

2.77 

2.77 

2.77 

2.77 

2.77 

i:: 

2.74 

2.76 

0.33 

2.: 

2.75 

2.77 

2.76 

2.74 

5:: 

2.76 

2.77 

2-n 

2.77 

2.77 

2.77 

2.77 

2.76 

2.77 

5:; 

2.77 

2.77 

2.77 

2.78 

HXCDF HPCDF HPCDF 

1.91 

1.9s 

1.96 

1.96 

1.95 

1.96 

MA 

1.96 

WA 

WA 

1.0s 

1.96 

1.: 

1.96 

1.96 

WA 

1.w 

WA 

MA 

MA 

1.; 

0.33 

2.:: 

1.95 

1.: 

1.98 

MA 

1.w 

1.95 

1.w 

1.94 

2.19 

MA 

WA 

1.98 

1.95 

1.96 

2.54 

WA 

3.08 

MA 

MA 

WA 

1.41 

1.44 

1.45 

1.44 

1.44 

1.45 

MA 

MA 

WA 

WA 

1.45 

1.45 

MA 

::: 

1.45 

1.:: 

WA 

1.:: 

I.2 

0.51 

WA 

MA 

2.: 

1.59 

1.83 

2.2 

1.44 

::: 

MA 

WA 

MA 

MA 

1.79 

MA 

MA 

WA 

WA 

WA 

MA 

MA 

2.55 

2.60 

2.62 

2.61 

2.61 

2.61 

2.61 

2.62 

1.81 

2.60 

2.60 

2.62 

2.59 

2.61 

2.61 

2.62 

2.62 

2.62 

2.61 

::: 

2.59 

2.60 

0.51 

2.:: 

2.60 

2.61 

2.60 

2.59 

2.62 

2.61 

2.61 

2.61 

2.59 

2.61 

2.62 

2.61 

2.61 

f :E 

2.61 

2.61 

2.61 

2.61 

2.61 

2.62 

0435 
Episode SCC Type Description 

3146 00015705 F PF Uolleye 

3166 WO157D6 F W uhitt Sucker 

3167 00015707 F PF lm Boss 

3167 DDO15708 F VP Bluegill 

3167 pOO405BB 1 PF lm Bass 

3167 sOO157OB F UP Bluegill 

3168 WO15711 F W Carp 

3166 WO15712 F PF la bass 

3168 SD015711 F W CsrD 

3169 DDO15713 F W St&k Redhorse 

3170 00015715 F W Spotted Sucker 

3171 00015717 F W Spotted Sucker 

3172 00015719 F W Csrp 

3172 00015720 F PF lm Boss 

31TJ W015721 F PF lm Boss 

3173 00015722 F W Channel Cetfish 

3173 a0070689 1 PF ln Bass 

3174 00015723 F PF lm Bass 

3174 00015724 F W Channel C&fish 

3175 00015801 F UB Chsnnel Catfish 

3175 00015802 F PF lm Boss 

3176 DDO15BO3 F W Spotted Sucker 

3176 00015804 F PF lm Boss 

3177 00015805 F W Csrp 

3171 DDO158w F PF lm Boss 

3178 00015807 F W North Hogsucker 

3118 WOl5808 F PF Redeye Boss 

3179 WO15M)o F W Golden Redhorse 

3179 00015810 F PF Lm Bass 

3180 WO15812 F PF lm Boss 

3181 ODD15813 F PF lm Bass 

3181 WO15814 F W Csrp 

3182 WO15815 F PF Rock Bass 

3182 DDO15816 F W Carp 

3163 WO15817 F W Carp 

3183 WO15818 F PF Ssuger 

3184 00015819 F W Carp 

31B4 DD015620 F PF Uhitt Creppie 

3185 DDO15B21 F W Channel Catfish 

3185 DD015822 F PF lm Boss 

3185 SD015821 F W Channel Cetfish 

3186 DOD15823 F PF Spot 

3186 DOD15824 F UP Southtrn Flow&r 

3167 DDOlSW2 F UP Suancr Floutder 

31BB 00015903 F W Carp 

318B 00015904 F PF Ln Bass 

3189 WOlSW5 F W Carp 

DlOXlN / FURAN DETECTION LIMITS, W/9 

2378 12378 123478 123678 

TCDO PECDD HXCDD HXCDD 

1.00 

1.01 

MA 

MA 

MA 

WA 

WA 

MA 

MA 

0.99 

1.16 

1.07 

MA 

MA 

0.99 

MA 

0.99 

0.99 

1.10 

WA 

1.02 

1.23 

1.11 

1.06 

:-2 

1:oo 

0.: 

0.99 

1.12 

A 

2.29 

WA 

MA 

WA 

1.04 

MA 

WA 

WA 

1.22 

WA 

1.02 

2.70 

1.39 

2.36 

0.92 

1.00 

WA 

MA 

WA 

MA 

MA 

1.00 

WA 

1.10 

0.92 

0.92 

WA 

0.92 

0.93 

MA 

0.92 

0.92 

0.92 

0.2 

1.68 

1.14 

1.52 

0.92 

0.97 

0.92 

1.:: 

0.93 

0.92 

WA 

0.92 

1.64 

0.: 

0.:: 

NA 

WA 

04 

1.04 

1.21 

1.: 

MA 

2.47 

2.47 

3.40 

WA 

MA 

WA 

2.:; 

MA 

2.46 

2.:: 

2.2: 

2.46 

2.46 

2.46 

2.46 

2.46 

WA 

2.46 

2.47 

2.46 

MA 

2.47 

2.47 

2.47 

2.56 

2.46 

2.46 

2.47 

2.2: 

2.48 

2.46 

2.46 

MA 

2.47 

WA 

MA 

2.2: 

2.46 

2.47 

MA 

2.46 

MA 

1.85 

MA 

WA 

WA 

MA 

MA 

WA 

1.85 

WA 

1.84 

MA 

1.84 

MA 

1.85 

1.84 

1.: 

1.84 

1.86 

MA 

WA 

1.: 

1.; 

1.85 

1.85 

I.2 

::: 

MA 

MA 

3.04 

3.23 

1.84 

WA 

1.84 

MA 

MA 

WA 

1.84 

MA 

MA 

1.: 

WA 

123789 1234678 

HXCDD HPCDD 

1.38 

1.38 

2.53 

2.:: 

MA 

WA 

1.38 

2.44 

1.37 

WA 

1.38 

MA 

1.38 

1.37 

WA 

1.37 

1.37 

1.37 

MA 

1.37 

1.38 

1.37 

1.38 

1.38 

1.38 

1.38 

1.38 

1.37 

1.37 

1.38 

1.:: 

1.38 

1.37 

1.38 

MA 

1.38 

MA 

MA 

1.:: 

1.38 

WA 

MA 

1.37 

I.36 

MA 

WA 

WA 

MA 

WA 

MA 

MA 

WA 

MA 

4.43 

MA 

WA 

MA 

WA 

1.26 

1.:: 

1.26 

MA 

MA 

MA 

MA 

1.34 

WA 

WA 

1.:: 

MA 

1.26 

1.62 

1.32 

MA 

WA 

WA 

MA 

MA 

1.:: 

WA 

WA 

MA 

1.32 

WA 

MA 

1.:: 

WA 

2378 12378 23478 123478 123678 

TCDF PECDF PECDF HXCDF* HXCDF 

0.49 

WA 

0.49 

0.67 

0.49 

WA 

MA 

MA 

WA 

MA 

MA 

WA 

MA 

MA 

0.50 

0.:: 

0.49 

WA 

0.49 

0.53 

MA 

0.56 

WA 

0.49 

0.84 

0.49 

WA 

0.59 

0.60 

0.49 

MA 

MA 

MA 

WA 

0.93 

1.24 

0.52 

MA 

MA 

MA 

1.00 

MA 

0.71 

MA 

0.57 

MA 

0.78 

0.78 

0.77 

0.: 

WA 

MA 

0.78 

MA 

0.77 

0.77 

0.77 

MA 

0.78 

0.77 

MA 

0.77 

0.77 

0.77 

0.78 

0.77 

0.78 

0.77 

0.80 

0.78 

0.78 

0.78 

0.78 

0.77 

0.77 

0.78 

2.18 

0.77 

WA 

WA 

0.77 

0.80 

0.78 

1.18 

WA 

WA 

0.79 

0.77 

0.77 

MA 

0.77 

0.77 

0.85 

WA 

0.94 

1.33 

1.03 

MA 

MA 

0.85 

WA 

0.95 

0.86 

0.85 

WA 

0.85 

0.85 

0.2 

0.84 

0.93 

0% 

0.96 

0.85 

0.:: 

0.85 

0.85 

0.92 

0.85 

0.85 

0.85 

WA 

0.86 

WA 

0.:; 

1.04 

0.85 

1.57 

WA 

0.2 

0.85 

0.85 

WA 

0.84 

WA 

2.84 

2.84 

WA 

WA 

MA 

MA 

MA 

2.84 

2.:: 

2.83 

2.83 

MA 

f :E 

2.83 

2.83 

2.82 

2.82 

MA 

2.83 

2.84 

2.83 

3.79 

2.84 

2.84 

2.84 

WA 

2.83 

2.82 

2.83 

2.: 

2.88 

2.: 

2.: 

MA 

WA 

2.: 

2.83 

2.83 

MA 

2.82 

MA 

2.85 

2.85 

MA 

3.:; 

3.:: 

2.85 

1.28 

2.83 

2.84 

2.84 

2.:: 

2.84 

2.84 

2.84 

2.83 

2.83 

2.85 

2.84 

2.85 

2.84 

2.85 

2.85 

2.85 

2.85 

2.85 

2.84 

f :Z 

2.: 

2.86 

WA 

f :Z 

2.85 

MA 

WA 

MA 

2.84 

2.84 

2.84 

MA 

2.83 

2.81 

123789 234678 1234678 1234789 

HXCDF HXCDF HPCDF 

2.78 

2.78 

2.77 

2.77 

2.76 

i-F 

2:78 

1.40 

2.76 

2.77 

2.77 

2.76 

2.78 

2.77 

2.77 

2.77 

2.76 

2.76 

f-Z 

2:78 

2.77 

2.78 

2.78 

2.78 

2.78 

2.78 

2.77 

2.76 

2.7? 

2.77 

2.76 

2.77 

2.77 

2.77 

2.77 

2.77 

2.77 

2.75 

0.87 

2.77 

2.77 

z 

2:76 

2.74 

1.96 

1.96 

WA 

MA 

WA 

MA 

1.96 

1.96 

1.57 

::: 

1.96 

1.95 

1.96 

1.95 

1.96 

1.96 

1.95 

1.95 

r.E 

1.96 

1.95 

I.2 

1.97 

1.96 

WA 

1.96 

1.95 

1.96 

MA 

1.95 

1.96 

1.; 

MA 

1.96 

1.z 

1.x 

1.96 

1.96 

WA 

1.95 

MA 

1.45 

1.45 

MA 

WA 

MA 

1.:: 

1.45 

0.67 

2.25 

MA 

1.45 

1.2: 

1.44 

MA 

1.44 

1.44 

1.44 

1.:: 

1.45 

1.44 

1.:: 

1.:: 

1.:: 

1.44 

1.45 

MA 

1.44 

1.45 

MA 

1.44 

HA 

1.45 

MA 

MA 

MA 

1.44 

1.45 

1.45 

MA 

1.44 

MA 

2.62 

2.62 

2.61 

MA 

2.61 

2.:: 

2.62 

1.87 

3.82 

2.61 

2.61 

2.60 

2.62 

2.61 

2.61 

2.61 

2.61 

2.60 

2.62 

2.61 

2.62 

2.61 

2.62 

2.62 

2.62 

2.62 

2.62 

2.61 

2.61 

2.62 

2.61 

2.61 

2.61 

2.61 

2.61 

2.62 

2.62 

2.75 

2.59 

WA 

2.61 

2.61 

2.61 

2.62 

2.60 

2.59 

D436 
Episode SCC Type Description 

3189 DD0159D6 F PF Lm Bass 

3190 DDO15907 F NB Carp 

3190 00015908 F PF Lm Bass 

3191 05024003 F UP Starry Flounder 

3191 DJO24005 M Soft Shell Clams 

3192 05024007 F UP Starry Flowder 

3192 DJO240W N Soft She\\ Clams 

3192 QDO20789 L Soft SheLL Clams 

3193 DC039001 F PF Striwd Bass 

3193 POD39001 L PF Stri& Bass 

31% DH020104 F UB Carp 

31% OH020105 F UB chub 

31% DH0201D8 F UB Sucker 

3197 DHO20110 F UB Sucker 

3198 DH020111 F UB Sucker 

3199 DHO20101 F UB Carp 

3199 DH020103 F UB Carp 

3200 DHO20112 F UB Sucker 

3201 DJ024012 F IJB Carp 

3203 05024018 F UB Carp 

3205 05024024 n Crayfish (uhole) 

3206 05022301 M UB Crayfish 

3206 05024102 F PF Lm Bass 

3206 05024103 F UB Sucker 

3208 DJO24109 F UB Sucker 

3212 05024121 F blB Carp 

3212 PO050388 L b!B CarD 

3216 05023707 F PF S&fish 

3216 DJO23708 F UB Sucker 

3216 90091688 F UB Sucker 

3217 DJO23709 F PF Uhitefish 

3217 05023710 F UB Sucker 

3218 DJ023711 F PF Squaufish 

3218 05023712 F UB S&ker 

3219 05023713 F UB tiite Sturgeon 

3219 DJ023?14 F PF Uhite Sturgeon 

3220 05023902 F PF Squawfish 

3220 DJO23903 F UB Bridgelip Sucker 

3220 QD012288 F PF Souawfish 

3221 05022405 F UB C&p 

3221 05023904 F BF Channel Catfish 

3221 05023905 F UB Sucker 

3222 DJ023906 F PF Swawfish 

3222 05023907 F MB S&ker 

3223 DJO23717 F UP Starry Flow&r 

3224 DJ023715 R Soft Shell CLams 

3226 DJO23721 M Pacific Oysters 

2378 

TWD 

MA 

NA 

1.: 

1.07 

#A 

1.19 

1.23 

WA 

1.26 

1.68 

NA 

1.08 

1.12 

IA 

1.g 

NA 

NA 

0.: 

WA 

WA 

NA 

1.12 

WA 

NA 

WA 

MA 

MA 

MA 

WA 

NA 

WA 

IA 

IA 

NA 

NA 

#A 

MA 

WA 

MA 

MA 

MA 

1.:: 

1.23 

12378 

PEWD 

0.93 

NA 

0.95 

0.98 

0.91 

It:: 

0.92 

1.28 

1.31 

1.42 

WA 

NA 

1.04 

WA 

IA 

0.97 

1.17 

NA 

0.: 

1.2: 

0.:: 

0.93 

0.91 

WA 

WA 

WA 

NA 

NA 

1.:: 

0.92 

0.92 

WA 

1.:: 

WA 

WA 

1.:: 

MA 

0.97 

0.91 

0.92 

DIOXIN / FURAN DETECTlOW LIMITS. m/Q 

123478 

HXCDD 

2.45 

IA 

2.46 

2.47 

2.45 

2.45 

2.46 

2.46 

2.47 

2.46 

2.46 

2.46 

2.:: 

2.46 

2.47 

2.47 

2.46 

3.:; 

2.47 

2.64 

2.46 

2.:: 

2.47 

2.45 

2.47 

2.48 

2.46 

WA 

2.46 

2.46 

2.46 

2.46 

2.47 

2.46 

2.98 

2.45 

2.46 

2.47 

2.44 

2.47 

2.46 

2.46 

2.45 

2.47 

123678 

HXCDD 

1.83 

HA 

1.84 

1.85 

1.84 

1.83 

1.84 

1.84 

WA 

1.86 

2.06 

WA 

WA 

1.84 

WA 

WA 

1.85 

1.84 

NA 

WA 

1.85 

MA 

WA 

1.:: 

1.85 

1.83 

IA 

MA 

WA 

WA 

1.84 

NA 

WA 

1.84 

1.84 

WA 

1.84 

1.96 

WA 

IA 

1.83 

WA 

IA 

MA 

MA 

1.84 

123789 1234678 

HXCDD 

1.37 1.25 

1.:; 

WA 

1.26 

1.38 MA 

1.37 WA 

1.37 WA 

1.37 IA 

1.37 WA 

1.38 NA 

1.38 IA 

1.37 NA 

1.37 IA 

1.36 IA 

1.37 WA 

1.38 IA 

WA NA 

1.38 WA 

1.37 WA 

MA WA 

1.:: 

MA 

WA 

WA WA 

1.38 NA 

1.:: 

NA 

MA 

1.38 WA 

1.37 1.65 

1.38 WA 

WA NA 

1.:: 

MA 

NA 

1.37 NA 

1.37 WA 

1.38 2.27 

1.37 WA 

1.38 WA 

1.37 MA 

1.37 MA 

1.37 1.91 

1.37 3.20 

1.38 WA 

1.36 

1.38 1.:: 

1.37 WA 

1.37 NA 

1.82 MA 

1.38 1.47 

2378 

TCDF 

. .- - 

12378 

PEWF 

0.72 

MA 

WA 

0.49 

WA 

WA 

NA 

NA 

NA 

NA 

1.09 

WA 

WA 

NA 

WA 

NA 

1.05 

WA 

NA 

0.E 

NA 

NA 

WA 

WA 

0.61 

0.77 

WA 

NA 

NA 

MA 

NA 

WA 

NA 

NA 

NA 

WA 

NA 

WA 

NA 

WA 

WA 

NA 

NA 

IA 

MA 

WA 

0.77 

0.88 

0.77 

0.78 

0.77 

0.77 

0.77 

0.77 

0.77 

1.03 

0.79 

0.87 

0.77 

0.77 

0.: 

0.90 

0.77 

NA 

0.2 

WA 

0.84 

0.2 

0.78 

0.77 

WA 

0.:; 

0.82 

0.77 

NA 

0.83 

#A 

0.77 

WA 

WA 

0.77 

WA 

0.77 

0.77 

0.78 

0.77 

0.77 

0.77 

0.78 

23478 123478 123678 

PECDF HXWF* HXCDF 

0.84 

IA 

0.84 

0.85 

0.84 

OX 

0.84 

WA 

NA 

1.27 

NA 

0.84 

0.85 

MA 

0.91 

0.93 

WA 

NA 

NA 

0.85 

WA 

WA 

WA 

0.85 

0.85 

0.84 

MA 

MA 

NA 

WA 

0.85 

MA 

1.18 

NA 

0.85 

1.03 

NA 

NA 

NA 

WA 

WA 

WA 

1.:: 

0.87 

0.95 

2.82 

3.57 

2.82 

Zi 

2.81 

2.83 

2.82 

2.83 

2.83 

2.83 

2.82 

WA 

2.83 

2.83 

2.84 

2.84 

2.82 

NA 

NA 

2.84 

2.:: 

2.:: 

2.84 

2.81 

2.84 

2.84 

2.83 

MA 

2.:: 

2.: 

2.83 

2.82 

2.82 

2.82 

2.83 

2.83 

2.2 

2.83 

2.82 

2.: 

2.83 

2.76 

2.83 

2.85 

2.83 

2.83 

2.84 

2.83 

2.84 

f-2 

2:83 

2.82 

2.84 

2.84 

2.85 

2.85 

2.83 

NA 

MA 

2.85 

2.; 

2.79 

:-: 

2:82 

2.85 

2.86 

f % 

2184 

2.83 

2.84 

2.83 

2.84 

2.83 

2.83 

2.83 

2.84 

2.84 

2.82 

2.85 

:% 

2:83 

2.85 

123789 234678 1234678 1234789 

2.76 

2.69 

2.76 

2.78 

2.76 

2.76 

2.77 

2.76 

2.77 

::T: 

2.76 

2.75 

2.77 

2.77 

2.78 

2.78 

2.76 

2.77 

2.79 

2.78 

2.; 

2.72 

2.79 

2.78 

2.75 

2.78 

2.78 

2.77 

2.72 

2.77 

2.76 

2.77 

2.76 

2.77 

2.76 

2.76 

2.76 

2.77 

2.77 

2.75 

2.78 

2.77 

2.76 

2.76 

2.77 

HXWF HPWF HPCDF 

1.95 

MA 

1.95 

1.96 

1.95 

1.95 

1.96 

E 

1:w 

1.96 

1.95 

1.: 

1.96 

1.96 

1.96 

1.0s 

NA 

1.: 

1.:: 

1.: 

1.96 

1.94 

1.96 

1.97 

1.96 

MA 

IA 

1.95 

1.96 

1.45 

1.96 

1.95 

1.95 

1.95 

1.96 

1.w 

1.94 

1.96 

1.95 

1.95 

1.95 

1.w 

1.44 

WA 

1.44 

1.45 

#A 

WA 

WA 

1.:: 

1.44 

WA 

NA 

WA 

1.44 

1.47 

WA 

1.45 

1.44 

IA 

NA 

1.45 

WA 

WA 

1.:: 

1.45 

1.44 

1.45 

WA 

WA 

MA 

1.44 

1.44 

MA 

1.44 

1.45 

1.44 

1.46 

1.44 

1.44 

1.45 

1.43 

1.4s 

MA 

WA 

MA 

1.45 

2.60 

2.53 

2.68 

2.62 

2.60 

5:: 

2.61 

2.61 

2.61 

2.61 

2.61 

2.59 

2.61 

2.61 

2.62 

2.62 

2.60 

2.61 

2.63 

2.62 

2.:: 

2.56 

2.63 

2.62 

2.59 

2.62 

2.62 

2.61 

2.56 

2.61 

2.61 

2.61 

2.60 

2.61 

2.60 

2.60 

2.60 

2.61 

2.61 

2.59 

2.62 

2.61 

2.60 

2-M) 

2.62 

0437 
Episode SCC Type Description 

3227 DJO23723 n Pacific Dysters 

3231 05023911 F W Carp 

3234 OH020301 F W Squawfish 

3235 DH020303 F W Uhite Sucker 

32% DHOZOUK F UB Largescale Sucker 

3236 DH020306 F PF Brow Trout 

3237 DHO20307 F PF Rainbow Trout 

3237 OH020308 F W Largescale Sucker 

3238 05023918 F UP DOLLY Vnrden 

3238 pDO80888 F Up DolLV Vsrden 

3241 DJO23924 F UP Doll; Varden 

3244 DJO23-622 F UB Coast Sculpin 

3245 05023623 F UP Spotted Ratfish 

3245 DJO2 1624 F W Fiathead Sole 

3246 DJ02 !108 F PF Red Striped Rockfish 

3246 DJ02 !I09 F UP Flsthead Sole 

3248 DJO2 JO2 F W Cqmsite Bottom 

3249 DJO2 1504 F W Sucker 

3250 DJO2 506 F UB Sucker 

3b2 DJO2 510 F W Sucker 

32SZaOD8 I288 L W Sucker 

32% DJO2 !517 F PF Sm Bass 

3256 0502 !SlU F UB Sucker 

32S8 DC03 I901 F PF Spat 

32S8DCO3 902 F W Croaker 

3259DB00 1566 F W Goldfish 

3259 DBO6 ,101 F W Sucker 

3260 DBOO 1193 F W Carp 

3261 DYO2 002 F W Striped Mullet 

3262 VI02 004 F W Tilapie Tilapia 

3264 DYO2 1602 F W Hornyhead Turbot 

3266 DY02 I702 F W Charnel Catfish 

3267 DYO2 HO1 F PF Rainbow Trout 

3267 DY02 !102 F W Sacramento Sucker 

3267 pDO2 I288 L PF Rainbow Trout 

3269 131022106 F W Charnel Catfish 

3270 DYO22107 F PF Samwfish 

3270 DY022108 F W Sucker 

3270 81022108 F W Sucker 

3271 DYO22110 F W Sucker 

3272 DYO22111 F PF Leopard Shark 

3272 DYO22112 F W Uhite Surfperch 

3273 DY022113 F W Sculpin 

3273 DYO22114 F W Surf Smelt 

3274 01022116 F W Sculpin 

32'15 DYD22118 F W Sucker 

3276 DY022119 F W Uslleye 

DIOXIN / FURAN DETECTICRT LIMITS. w/a 

2378 12378 123478 123678 

TCDD PEWD HXCDD HXCDD 

1.01 

WA 

1.15 

WA 

WA 

:-zz! 

1:37 

1.11 

1.04 

1.:: 

1.02 

1.11 

1.14 

0.95 

1.01 

1.00 

1.10 

WA 

WA 

WA 

WA 

1.:: 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

1.74 

WA 

WA 

WA 

0.2 

WA 

WA 

1.23 

1.11 

0.99 

WA 

1.52 

WA 

0.94 

WA 

WA 

0.: 

1.15 

O.% 

0.92 

1.21 

0.94 

0.91 

0.: 

0.88 

0.95 

0.92 

1.30 

1.16 

1.05 

0.92 

0.93 

2.89 

0.92 

WA 

1.68 

1.25 

1.98 

0.96 

WA 

1.57 

1.14 

0.97 

1.28 

WA 

WA 

1.03 

0.33 

1.00 

0.92 

WA 

1.35 

1.07 

0.93 

1.00 

WA 

2.47 

2.67 

2.53 

2.51 

2.:; 

2.46 

2.47 

2.46 

2.46 

2.46 

2.46 

2.43 

2.46 

2.46 

I:: 

2.47 

2.45 

2.47 

2.47 

5:Z 

2.61 

2.47 

3.12 

2.2: 

WA 

2.46 

2.47 

2.46 

2.46 

2.47 

2.47 

2.47 

2.47 

2.46 

1.04 

2.44 

2.46 

2.70 

2.47 

2.47 

2.49 

2.46 

2.45 

2.81 

WA 

1.90 

WA 

2.:: 

1.84 

1.85 

1.84 

1.84 

1.: 

1.82 

2.01 

1.84 

1.76 

1.8s 

1.85 

1.: 

WA 

1.84 

1.79 

3.20 

WA 

WA 

2.: 

WA 

WA 

WA 

::: 

1.85 

1.84 

WA 

WA 

1.84 

0.65 

WA 

WA 

WA 

WA 

1.84 

1.86 

1.84 

WA 

123789 1234678 

HXCDD HPCDD TCDF PECDF 

1.::: 

1.42 

1.39 

1.39 

1.38 

1.37 

1.38 

1.38 

1.37 

1.38 

1.37 

1.36 

1.38 

1.38 

1.32 

1.38 

1.38 

1.37 

1.38 

1.38 

1.37 

1.34 

1.47 

1.39 

1.:: 

1.38 

WA 

1.37 

1.53 

1.38 

1.37 

1.38 

1.38 

1.38 

1.38 

1.38 

1.22 

1.36 

1.37 

1.: 

1.38 

1.39 

1.38 

WA 

WA 

WA 

WA 

WA 

WA 

2.09 

1.26 

1.59 

WA 

WA 

WA 

WA 

WA 

3.: 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

5.:: 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

2.: 

WA 

WA 

2.K 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

0.91 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

1.25 

0.52 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

0.81 

WA 

WA 

WA 

WA 

0.66 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

0.:: 

WA 

0.77 

WA 

0.80 

0.83 

0.82 

8:: 

0.81 

0.77 

0.77 

0.81 

0.88 

0.77 

0.77 

0.77 

0.74 

0.78 

0.78 

0.77 

0.78 

0.78 

0.77 

0.75 

WA 

0.: 

WA 

WA 

WA 

0.84 

0.92 

0.77 

0.;: 

0.90 

0.81 

0.78 

0.77 

0.43 

0.77 

0.77 

WA 

WA 

0.77 

0.78 

0.77 

0.77 

2378' 

- - 

12378 23478 123478 123678 

PECDF HXCDF+ HXCDF 

1.22 

2.34 

0.87 

WA 

WA 

1.08 

1.06 

1.40 

0.85 

0.85 

1.02 

0.92 

0.84 

1.08 

0.85 

0.81 

0.85 

0.85 

WA 

0.97 

0.2 

0.82 

WA 

0.85 

WA 

WA 

WA 

WA 

0.89 

WA 

WA 

WA 

0.99 

WA 

WA 

0.2 

WA 

0.84 

1.01 

WA 

WA 

0.85 

0.85 

0.85 

WA 

2.83 

WA 

2.91 

X:E 

2.84 

2.82 

5.: 

2183 

2.83 

2.83 

2.80 

2.83 

2.83 

2.71 

2.84 

5-E 

2183 

2.84 

I% 

2:87 

WA 

2.: 

2.84 

WA 

f-E 

2183 

2.83 

f-ii 

2:84 

2.84 

2.83 

0.93 

2.80 

2.82 

2.83 

WA 

2.83 

2.86 

2.83 

2.81 

2.84 

2.84 

2.92 

2.87 

2.87 

2.85 

2.83 

2.85 

2.84 

:-ii 

2:84 

2.81 

I-E 

2172 

2.85 

5-E 

2:ss 

2.85 

I:: 

I:E 

2.: 

2.85 

2.83 

::: 

f-2 

2:85 

2.85 

2.85 

2.85 

2.84 

1.23 

2.81 

2.84 

2.: 

2.84 

2.87 

2.84 

2.82 

123789 234678 1234678 1234789 

HXCDF HXCDF HPCDF HPCDF 

2.77 

2.76 

2.85 

f:ii 

f :E 

2.78 

2.77 

f :Z 

X:Z 

2.77 

2.77 

2.65 

2.n 

2: 

2.77 

2.78 

2.76 

2.70 

2.81 

2.78 

::z 

2.78 

2.76 

2.76 

2.78 

2.77 

2.77 

2.78 

2.T7 

f:i 

i:G 

2.74 

2.76 

2.77 

2.77 

2.TT 

2.80 

2.77 

2.Ts 

1-w 

2.:: 

1.97 

1.98 

1.96 

1.95 

1.96 

1.96 

1.95 

1.w 

1.96 

1.93 

1.96 

1.w 

1.87 

1.w 

1.96 

1.95 

1.96 

1.96 

1.95 

1.91 

1.99 

IA 

1-w 

1.w 

1.96 

1.2 

1.96 

1-w 

1.96 

::: 

1.96 

1.96 

I% 

1.94 

1.95 

1.w 

WA 

1.96 

1.97 

1.96 

1.94 

WA 

1.:: 

WA 

WA 

1.45 

1.44 

1.45 

1.45 

1.44 

1.44 

1.44 

1.43 

1.45 

1.44 

1.38 

WA 

1.4s 

WA 

1.45 

1.45 

1.44 

WA 

1.45 

WA 

WA 

1.: 

WA 

WA 

WA 

1.45 

1.44 

1.45 

1.45 

1.45 

1.45 

1.45 

0.70 

1.43 

1.44 

1.63 

WA 

1.45 

1.46 

1.45 

WA 

2.61 

2.61 

2.69 

5-Z 

2:62 

2.61 

2.62 

2.61 

2.61 

2.61 

2.61 

2.58 

2.61 

2.61 

2.50 

2.62 

2.62 

2.60 

2.62 

2.62 

2.61 

2.54 

2.62 

2.62 

2.61 

2.61 

2.62 

I2 

2:62 

2.61 

2.61 

2.62 

2.62 

2.62 

2.62 

2.61 

2.07 

2.58 

2.61 

2.61 

2.62 

2.61 

2.64 

2.61 

2.59 

0438 
Episode See Type Description 

3276 DYO22120 F PF Broun Rockfish 

3278 DY022124 F UB Sacrunento Sucker 

3281 DYO22205 F UB Sucker 

3282 DYO22207 F UB Carp 

3283 DY022209 F b/B Carp 

3285 DY022212 F UP Stingray 

3285 01022213 F UB Dimwnd Turbot 

3286 DY022215 F UB Carp 

3287 DY022216 P UB Tilapia Zilli 

3288 DY022218 F UB Sucker 

3288 PO060188 F UB Sucker 

3289 DYO22219 F UP Bocaccio 

3289 01022220 F UB Sculpin 

3290 DYO22221 F PF Red&r Svlfish 

3290 DYO22222 F UB Blackfish 

3294 DJD22111 F UP True Cod 

3294 DJD22113 W Mussel 

3295 DJO22114 F UP Atlantic Sahon 

3296 DBD40101 F UB mite Sucker 

3297 DBO41501 F UB Carp 

3297 De041504 F PF Sm Bass 

3297 SBO41501 F NB Carp 

3298 DBO41601 F UB Carp 

3298 DBO41604 F PF Lm Bass 

3298 00112988 L PF Ln Bass 

3299 DBO40601 F UB Uhite Sucker 

3299 DBWMD4 F PF Lm Bass 

3300 De040201 F UB Uhite Sucker 

3300 DBO40204 F PF Sm Bass 

3300 SBO40201 F IJB Mite Sucker 

3301 De041101 F UB Carp 

3301 DBD41104 F PF Northern Pike 

3301 DDO92088 L UB Carp 

3301 SBO41101 F UB Carp 

3302 De041901 F UB Uhite Sucker 

3302 De041904 F PF Lm Bass 

3303 08042301 F UB lihite Sucker 

3304 DBO41001 F PF Northern Pike 

3304 DBO41004 F UB Uhite Sucker 

3305 DBO42001 F UB Channel Catfish 

3305 DBO42004 F PF Sm Bass 

33% DBD41801 F UB Uhite Sucker 

3307 De042101 F W Uhite Sucker 

3307 PO100588 L UB Uhite Sucker 

3308 DB040001 F PF Northern Pike 

3308 PO030689 L PF Northern Pike 

3309 De041301 F UB Uhite Sucker 

2378 

TCDD 

1.13 

0.99 

0.99 

1.70 

WA 

NA 

1.76 

NA 

WA 

::: 

0.99 

1.20 

1.07 

WA 

1.02 

0.99 

1.11 

1.34 

NA 

1.14 

WA 

WA 

0.99 

0.99 

WA 

WA 

NA 

NA 

NA 

WA 

NA 

WA 

WA 

WA 

WA 

NA 

WA 

WA 

WA 

1.48 

WA 

IA 

WA 

1.11 

1.01 

NA 

12378 

PECDD 

0.98 

0.92 

1.15 

1.23 

WA 

WA 

NA 

WA 

0.99 

0.99 

1.14 

0.93 

0.97 

0.96 

0.2 

0.92 

0.W 

1.04 

OX 

WA 

WA 

0.92 

0.92 

WA 

HA 

1.: 

NA 

0.: 

IA 

NA 

0.: 

0.:: 

WA 

0.2 

1.11 

1.41 

1.12 

0.93 

0.94 

0.97 

DIOXIN / FURAN DETECTlOW LIUITS, w/B 

123478 123678 123789 1234678 2378 12378 

HXCDD HXCDD HXCDD HPCDD TCDF PECDF 

2.42 

2.46 

2.46 

2.56 

2.50 

2.:;: 

2.2: 

2.47 

2.45 

2.45 

2.46 

2.47 

WA 

2.47 

2.46 

2.47 

2.44 

2.78 

2.46 

NA 

WA 

2.46 

2.47 

2.3 

2.46 

2.46 

1.10 

2.:: 

5.04 

2.:: 

2.47 

2.46 

2.45 

2.45 

2.63 

2.45 

2.46 

2.43 

2.46 

2.47 

2.47 

2.47 

WA 

1.@4 

1.84 

1.91 

NA 

IA 

WA 

1.: 

1.85 

1.83 

1.83 

1.84 

1.85 

1.:: 

1.84 

WA 

1.83 

WA 

1.84 

WA 

NA 

1.84 

1.84 

1.; 

2.06 

1.84 

0.67 

WA 

1.84 

WA 

2.:; 

1.85 

NA 

1.84 

NA 

WA 

1.83 

1.84 

1.82 

Z 

1.84 

WA 

1.35 

1.38 

1.37 

1.44 

1.40 

WA 

WA 

WA 

1.37 

1.38 

1.37 

1.37 

1.37 

1.38 

WA 

1.38 

1.38 

1.38 

1.36 

WA 

1.37 

1.24 

IA 

1.38 

1.38 

1.37 

1.37 

1.37 

1.38 

1.31 

1.:: 

WA 

1.70 

1.38 

1.38 

1.37 

1.37 

1.37 

1.38 

1.37 

1.37 

1.36 

1.37 

1.38 

1.38 

1.38 

WA 

NA 

#A 

2.27 

NA 

NA 

WA 

WA 

WA 

WA 

WA 

WA 

#A 

WA 

NA 

1.41 

1.50 

IA 

NA 

NA 

IA 

NA 

WA 

1.34 

1.36 

NA 

WA 

1.:: 

WA 

IA 

1.35 

IA 

IA 

WA 

WA 

1.:: 

WA 

1.:: 

WA 

1.:: 

1.30 

1.26 

NA 

NA 

0.49 

0.71 

WA 

WA 

NA 

NA 

WA 

NA 

WA 

WA 

WA 

WA 

0.60 

WA 

WA 

0.55 

WA 

WA 

NA 

0.51 

WA 

WA 

0.51 

0.49 

WA 

NA 

NA 

WA 

NA 

IA 

NA 

WA 

NA 

WA 

0.65 

WA 

WA 

WA 

NA 

IA 

NA 

WA 

WA 

WA 

WA 

WA 

0.76 

0.77 

0.77 

0.98 

WA 

1.:: 

NA 

0.77 

0.78 

0.77 

0.85 

0.77 

0.78 

WA 

0.78 

0.77 

0.m 

0.77 

NA 

0.77 

NA 

IA 

0.77 

0.77 

NA 

WA 

0.2 

WA 

WA 

0.79 

WA 

NA 

0.: 

0.77 

0.77 

WA 

NA 

0.77 

WA 

1.04 

WA 

0.77 

0.77 

0.78 

23478 123478 123678 123789 

PECDF HXCDF' HXCDF HXCDF 

WA 

0.85 

0.84 

#A 

WA 

NA 

WA 

0% 

NA 

WA 

0.90 

0.84 

0.85 

WA 

0.85 

0.85 

0.85 

IA 

WA 

IA 

WA 

WA 

0.85 

0.85 

NA 

WA 

WA 

1.59 

IA 

IA 

1.08 

WA 

IA 

IA 

0.88 

0.:: 

WA 

1.: 

WA 

WA 

0.E 

0.85 

0.86 

t :Z 

2.B2 

2.83 

WA 

2.: 

2.93 

2.83 

f :Z 

2.82 

5:: 

WA 

f :Z 

f :Z 

IA 

WA 

WA 

2.:: 

2.83 

WA 

NA 

2.:: 

IA 

2.: 

HA 

IA 

2.: 

2.83 

2.82 

2.82 

NA 

2.81 

2.83 

2.79 

2.83 

2.83 

2.83 

2.84 

2.79 

2.84 

2.84 

2.84 

2.89 

3.36 

WA 

NA 

2.84 

2.85 

2.83 

2.83 

2.83 

2.85 

2.2 

2.84 

2.85 

2.82 

IA 

WA 

WA 

WA 

2.84 

2.84 

3.: 

2.84 

2.84 

1.17 

2.2 

NA 

2.: 

2.85 

f-2 

2:83 

2.:: 

2.84 

2.81 

2.84 

2.84 

2.114 

2.85 

2.72 

2.TT 

2.76 

f-Z 

2:7B 

2.73 

2.81 

2.n 

2-E 

2:76 

2.76 

2.18 

2.73 

2.78 

2.n 

2.78 

2.75 

2.TI 

2.76 

0.87 

2.77 

2.77 

2.77 

f-E 

2:n 

2.77 

1.06 

2.n 

2.77 

2.77 

1.07 

2.77 

2.78 

2.77 

2.76 

2.76 

2.77 

2.75 

2.77 

2.74 

2.77 

2.77 

2.77 

2.78 

234678 1234678 1234789 

HXCDF -HPCDF HPCDF 

1.92 

1.96 

1.95 

1.96 

1.99 

1.; 

1.99 

1.95 

1.96 

1.95 

1.95 

1.95 

1.96 

IA 

::2 

::it 

2.37 

1.95 

WA 

NA 

1.96 

1.w 

WA 

1.95 

1.w 

1.w 

1.03 

1.2 

WA 

1.: 

1.96 

1.96 

1.95 

1.95 

1.97 

1.94 

E 

1.96 

1.96 

1.w 

1.96 

WA 

1.44 

1.44 

1.45 

NA 

IA 

1.59 

IA 

1.2: 

1.44 

1.44 

1.44 

1.45 

WA 

1.45 

1.45 

1.45 

1.43 

1.:: 

WA 

IA 

1.44 

1.45 

IA 

NA 

1.:: 

0.65 

1.:: 

IA 

WA 

1.:: 

WA 

1.44 

1.44 

1.59 

1.43 

1.44 

1.43 

1.44 

1.45 

1.45 

WA 

2.57 

2.61 

2.61 

2.61 

2.66 

2.62 

2.57 

2.65 

2.61 

2.62 

2.60 

2.60 

5-z 

2:57 

2.62 

2.61 

2.62 

2.59 

2.: 

1.81 

2.78 

2.61 

2.61 

2.: 

2.61 

2.61 

2: 

2.61 

2.67 

2.07 

2.61 

2.62 

2.61 

2.60 

2.60 

2.62 

2.59 

2.61 

2.58 

2.61 

2.61 

2.61 

2.62 

0439 
Episode SCC Type Description 

3310 DC032701 F UB BulLhead 

3310 DC0327D2 F PF Walleye 

3311 DC032801 F UB Rcdhorse Sucker 

3311 DC032802 F PF Sm Bass 

3312 DC033101 F VB Redhorse Sucker 

3312 DC033102 F PF Sm Bass 

3313 DC033201 F UB Redhorse Sucker 

3313 DC033202 F PF Sm Bass 

3314 DC033301 F UB Channel Catfish 

3314 DC033302 F PF Uhite Bass 

3314 SC033301 F UB Channel Catfish 

3314 SC033302 F PF White Bass 

3315 DC033401 F UB Care 

3316 DC033501 F UB Uhiie Sucker 

3316 DC033502 F PF Brow Trout 

3317 DC033601 F UB Uhite Sucker 

3317 DC033602 F Yp Pur+inseed 

3317 SC033601 F UB Mite Sucker 

3317 SC033602 F Up punpkinseed 

3318 DC033701 F UB Uhite Sucker 

3318 DC033702 F PF Rock Bass 

3319 DBD41401 F Yp Winter FLouder 

3319 BDO63DB8 F UP Uinter Flounder 

3320 08041412 F UP Bluefish 

3321 DBO40401 F t@ Winter Flounder 

3322 De040412 F up Bluefish 

3323 DBD41206 F UP Yintcr Flow&r 

3324 06041252 F Up Bluefish 

3325 DBD41218 F Up Bluefish 

3325 BDOB29B8 L Up Bluefish 

3326 DBD412DB F UP Bluefish 

3327 DBO40301 F UP Bluefish 

3327 DBO40315 F UP Bluefish 

3328 DDO29111 F VB Carp 

3328 00029112 F PF Lm Bass 

3328 SD029111 F HI Carp 

3328 SD029112 F PF Lm Bass 

3329 Do016003 F UB Boufin 

3329 SD016003 F UB Bowfin 

3330 DDO291W F PF Sunamee Bass 

3330 DDO29110 F UB Spotted Sucker 

3330 DDO29423 F PF BLwk Craooie 

3331 00016001 F UB Brown Bulihead 

3331 DDO16002 F PF Lm Bass 

3331 DDO16007 F UB Carp 

3331 DDO16OOB F BF Mite Catfish 

3331 SD016008 F BF Uhite Catfish 

2378 

TCDD 

1.:: 

i-z 

2:12 

1.01 

WA 

IA 

NA 

NA 

WA 

IA 

1.33 

NA 

NA 

NA 

IA 

IA 

WA 

NA 

1.2 

WA 

NA 

WA 

WA 

WA 

WA 

WA 

NA 

NA 

NA 

WA 

WA 

NA 

WA 

IA 

NA 

WA 

1.20 

WA 

0.99 

IA 

WA 

NA 

WA 

NA 

12378 

PECDD 

WA 

0.94 

1.00 

0.94 

0.:: 

0.; 

IA 

0.96 

WA 

0.22 

NA 

NA 

1.05 

WA 

0.92 

0.38 

0.27 

1.00 

0.92 

1.24 

1.20 

1.61 

NA 

0.91 

0.92 

::: 

1.03 

1.03 

1.36 

WA 

0.: 

0.:: 

NA 

WA 

1.30 

NA 

0.92 

0.92 

0.99 

NA 

IA 

NA 

DIOXIN / FURAN DETECTlOW LIMITS, w/g 

123478 

HXCDD 

123678 123789 1234678 

IA 

1.84 

1.84 

1.85 

IA 

1.84 

WA 

1.85 

NA 

1.85 

WA 

0.64 

NA 

1.E 

1.: 

X:22 

WA 

1.83 

1.86 

WA 

1.84 

WA 

1.82 

1.84 

1.83 

1.84 

1.84 

1.84 

1.84 

NA 

WA 

1.84 

0.2 

WA 

12 

WA 

1.85 

NA 

1.84 

4.91 

WA 

WA 

HXCDD HPCDD 

2378 

TCDF 

12378 

PECDF 

NA 

2.47 

2.46 

2.47 

2.47 

2.47 

2.46 

2.47 

2.46 

2.47 

WA 

1.15 

2.:: 

2.46 

2.46 

2.46 

1.07 

1.15 

2.46 

2.45 

2.47 

2.47 

2.47 

2.44 

2.44 

2.47 

2.45 

2.46 

2.46 

2.46 

2.46 

NA 

2.: 

1.36 

1.11 

2.47 

1.04 

2.47 

2.45 

2.47 

2.46 

2.46 

2.47 

2.47 

1.12 

1.:: 

1.37 

1.38 

1.38 

1.38 

1.38 

1.38 

IA 

::3": 

1.34 

1.:: 

1.37 

1.37 

1.37 

1.22 

1.33 

1.37 

1.37 

1.38 

1.38 

1.38 

1.37 

1.36 

1.3B 

1.37 

1.37 

1.37 

1.37 

1.38 

NA 

1.37 

1.37 

1.21 

1.31 

1.38 

1.22 

1.38 

NA 

1.38 

1.37 

1.37 

NA 

IA 

1.32 

IA 

IA 

IA 

1.26 

WA 

WA 

NA 

NA 

WA 

WA 

1.: 

WA 

IA 

NA 

WA 

WA 

1.08 

IA 

WA 

NA 

WA 

WA 

4.10 

1.: 

2.23 

IA 

WA 

IA 

WA 

WA 

WA 

IA 

IA 

IA 

1.:: 

IA 

WA 

NA 

NA 

IA 

IA 

NA 

IA 

NA 

NA 

WA 

NA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

WA 

NA 

WA 

NA 

WA 

WA 

WA 

IA 

WA 

WA 

WA 

WA 

WA 

WA 

IA 

WA 

WA 

NA 

NA 

IA 

NA 

WA 

WA 

WA 

NA 

WA 

IA 

NA 

0.49 

0.:: 

WA 

NA 

WA 

NA 

NA 

NA 

0.78 

NA 

0.80 

NA 

0.77 

0.: 

WA 

WA 

WA 

NA 

WA 

WA 

0.77 

1.:: 

NA 

WA 

NA 

0.77 

NA 

NA 

WA 

NA 

0-Z 

WA 

WA 

WA 

NA 

NA 

WA 

IA 

0.77 

1.04 

0.43 

NA 

WA 

0.77 

0.77 

0.78 

0.77 

0.77 

WA 

0.78 

0.43 

23478 123478 123678 123789 

PECDF HXCDF* WXCDF HXCDF 

NA 

0.85 

NA 

0.86 

WA 

0.91 

IA 

0.85 

WA 

WA 

NA 

NA 

NA 

WA 

WA 

IA 

WA 

NA 

WA 

NA 

0.84 

WA 

WA 

WA 

WA 

0.:: 

NA 

NA 

HA 

NA 

NA 

WA 

WA 

NA 

IA 

NA 

WA 

WA 

0.85 

IA 

0.85 

0.84 

0.84 

1.41 

WA 

IA 

2.95 

2.83 

2.82 

2.84 

2.83 

2.83 

2.83 

2.84 

WA 

NA 

IA 

0.89 

2.82 

WA 

2.: 

2.82 

0.87 

0.88 

2.82 

2.81 

::: 

2.83 

2.81 

2.w 

2.83 

2.81 

2.83 

2.83 

5: 

2:83 

f :E 

0.: 

WA 

WA 

2.83 

2.82 

f :Z 

5:Z 

2.84 

0.94 

2.; 

2.83 

2.85 

2.85 

2.84 

2.84 

2.85 

2.:: 

1.10 

1.11 

2.83 

2.; 

f:it 

1.03 

1.10 

i:: 

2.85 

2.85 

2: 

2.81 

2: 

2:84 

2.84 

2.84 

2.84 

2.84 

2.83 

2.83 

1.22 

1.18 

WA 

WA 

f-Z 

2:85 

2.84 

2.83 

2.76 

2.77 

2.76 

2.78 

2.77 

2.77 

2.77 

2.78 

2.77 

2.78 

0.99 

0.99 

2.76 

2.TI 

2.77 

Z 

E 

2.76 

2.76 

2.78 

2.77 

235 

2174 

2.77 

f-E 

2177 

2.77 

2.77 

2.77 

2.76 

2.76 

0.96 

1.07 

f :G 

Z 

z! 

2:76 

2.77 

2.78 

1.07 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

2.02 

1.96 

1.95 

1.96 

1.96 

1.96 

1.96 

l.% 

NA 

1.96 

0.91 

0.91 

1.95 

1.96 

1.95 

::: 

0.86 

0.91 

1.95 

1.95 

E 

1.w 

1.94 

1.94 

1.96 

1.95 

1.96 

1.96 

1.95 

1.96 

1.w 

E 

0.95 

1.03 

IA 

0.95 

1.96 

1.95 

1.w 

1.95 

1.95 

IA 

2.31 

1.45 

1.44 

1.45 

1.45 

1.45 

1.50 

1.45 

1.:: 

0.71 

0.67 

1.44 

1.44 

1.44 

1.44 

1.44 

0.67 

0.67 

1.44 

1.44 

1.45 

1.45 

1.78 

1.43 

1.43 

1.45 

1.44 

1.44 

1.44 

1.44 

1.44 

IA 

1.44 

1.44 

0.66 

0.66 

WA 

NA 

1.45 

1.44 

1.45 

1.44 

1.44 

IA 

1.45 

0.71 

2.61 

2.62 

2.60 

2.62 

2.62 

2.61 

2.61 

2.62 

NA 

2.62 

1.87 

1.88 

2.60 

2.61 

2.61 

2.61 

2.61 

1.87 

1.87 

2.61 

2.60 

2.62 

2.62 

3.12 

2.59 

2.59 

2.61 

2.60 

2.61 

2.61 

2.61 

2.61 

2.61 

2.60 

2.60 

1.80 

1.65 

2.62 

1.81 

2.61 

2.60 

2.62 

2.61 

2.61 

2.61 

2.62 

2.07 

D-440 
Episode SCC Type Description 

3332 DDO16009 F Up Spotted Drun 

3332 DDO16010 F PF Crevalle Jack 

3333 DDO16011 F PF Bluefish 

3333 DDO16012 F UB Sea Catfish 

3333 DD029108 F PF Ueakfish 

3333 Qo121588 L PC Bluefish 

3334 DDO160!3 F UB Sea Catfish 

33% DDO16014 F BF Striped Mullet 

3335 DD016015 F UP Spot 

3335 DD016016 F PF Spotted Bass 

3335 DDO29101 F Up Red Drum 

3335 DDOzOlO2 F UB Southern Flow&r 

3335 DDO29103 F W Sheepshead 

3335 QoD8158B L UP Southern Flouder 

3335 SD016015 F UP Spot 

3336 DD016OD4 F UP BLack DrM 

3336 DDO16005 F PF Stricd Mullet 

z: 

33 

33 

33 

33 

33 

33 

33 

33 

ii 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

33 

~36 DDO16006 F UP She&head 

'36 DDO16017 F UP Red Drus 

836 DD016018 F PF Spotted Seatrout 

'36 a0092288 F PF Spotted Seatrout 

837 DDOl6019 F UB Spotted Sucker 

37 DDO16020 F PF Lm Bass 

37 a0051388 F UB Spotted Sucker 

138 DD016021 F PF Lm Bass 

138 DDO16022 F UB Spotted Sucker 

;38 DDO29107 F PF Chain Pickerel 

139 DDO16023 F UB Carp 

'39 DDO16024 F PF Uhite Bass 

'39 PO016023 L UB Carp 

'40 DDO29113 F PF Lm Bass 

40 DD029114 F UB Channel Catfish 

'40 SD029114 F UB Channel Catfish 

'41 DDO16103 F PF Lm Bass 

41 DDO16104 F UB Catfish 

41 90092788 F PF Lm Bass 

41 SD016103 F PF Lm Bass 

;41 SD016104 F UB Catfish 

;42 DD016105 F UB Spotted Sucker 

;42 DD016106 F PF Bluegill 

;43 DD016107 F UB Uhite Sucker 

)43 DDO16108 F PC Redweast Sunfish 

44 DD016109 F UB Carp 

i44 DDO16110 F PF Lm Bass 

i44 SD016109 F UB Carp 

i45 DD016111 F UB Redhorse Sucker 

I45 DDO16112 F PF Lm Bass 

DIOXIN / FURAN DETECTlOW LIMITS. w/g 

2378 12378 123478 1236?8 

TCDD PECDD HXCDD HXCDD 

WA 

1.16 

NA 

WA 

1.05 

WA 

NA 

1.00 

1.:: 

IA 

WA 

WA 

WA 

IA 

0.99 

NA 

NA 

1.17 

0.99 

0.99 

WA 

WA 

IA 

1.07 

NA 

NA 

WA 

IA 

WA 

WA 

WA 

NA 

NA 

WA 

WA 

WA 

WA 

1.:: 

NA 

NA 

NA 

NA 

WA 

WA 

WA 

NA 

0.99 

WA 

0.:: 

NA 

0.: 

WA 

0.92 

0.92 

WA 

WA 

WA 

NA 

0.94 

1.22 

0.: 

0.92 

0.92 

0.:; 

0.: 

WA 

0.97 

NA 

NA 

WA 

0.93 

WA 

0.: 

IA 

0.97 

0.22 

WA 

0.2 

WA 

1.84 

0.:; 

WA 

WA 

NA 

2.2: 

2.46 

2.23 

2.45 

2.:: 

2.47 

2.46 

2.46 

2.46 

2.45 

2.44 

1.09 

2.47 

2.47 

2.46 

2.46 

2.46 

2.46 

WA 

2.45 

2.:: 

2.47 

2.47 

2.2; 

2.:: 

WA 

1.87 

2.46 

NA 

2.47 

1.15 

WA 

2.2; 

2.47 

4.93 

NA 

2.46 

3.2 

2.46 

WA 

1.83 

2.13 

NA 

1.84 

WA 

NA 

1.84 

NA 

::: 

2.35 

WA 

NA 

NA 

NA 

::ti 

1.84 

1.84 

1.84 

NA 

1.83 

1.: 

1.: 

WA 

NA 

WA 

1.85 

NA 

NA 

1.84 

WA 

1.85 

0.64 

NA 

1.: 

5.95 

WA 

1.; 

WA 

NA 

WA 

123789 1234678 

HXCDD HPCDD TCDF PECDF 

NA 

1.37 

1.37 

NA 

1.38 

1.37 

WA 

1.37 

WA 

1.37 

IA 

1.37 

1.37 

NA 

NA 

NA 

1.38 

WA 

1.37 

1.38 

1.37 

WA 

1.37 

1.:: 

WA 

1.38 

WA 

1.38 

1.53 

1.38 

NA 

1.:: 

1.:: 

1.33 

WA 

NA 

1.38 

NA 

2.75 

1.:: 

NA 

WA 

1.37 

1.:: 

NA 

1.:: 

WA 

1.:: 

IA 

NA 

WA 

NA 

IA 

NA 

IA 

WA 

WA 

NA 

NA 

WA 

WA 

WA 

IA 

WA 

1.28 

1.:: 

WA 

WA 

1.:;: 

WA 

1.:; 

NA 

1.48 

1.30 

NA 

#A 

WA 

WA 

11 

1.3 

NA 

WA 

NA 

NA 

0.50 

WA 

0.:: 

NA 

NA 

0.52 

NA 

#A 

NA 

NA 

NA 

NA 

NA 

NA 

WA 

NA 

0.: 

0.58 

NA 

IA 

WA 

0.53 

0.; 

NA 

NA 

WA 

NA 

WA 

WA 

NA 

WA 

NA 

WA 

WA 

WA 

0.92 

WA 

NA 

NA 

0.53 

NA 

NA 

WA 

NA 

0.77 

0.77 

0.77 

0.78 

0.77 

0.77 

0.77 

NA 

NA 

WA 

0.77 

0.; 

WA 

0.77 

0.78 

0.87 

0.77 

0.77 

0.77 

0.80 

0.77 

0.77 

0.77 

1.33 

0.78 

1.47 

NA 

WA 

0.78 

IA 

0.44 

WA 

0.81 

0.78 

0.42 

0.41 

0.: 

WA 

1.55 

WA 

0.77 

WA 

1.17 

0.77 

. ,--- 

2378 12378 23478 

PECDF 

WA 

0.84 

WA 

WA 

0.85 

2.:: 

0.84 

WA 

0.84 

0.85 

0.90 

IA 

0.88 

0.:; 

0.95 

1.42 

0.84 

0.85 

0.85 

NA 

0.84 

0.: 

NA 

0.85 

IA 

WA 

0.: 

NA 

NA 

WA 

WA 

WA 

0.36 

NA 

0.: 

NA 

1.69 

2.79 

0.85 

WA 

WA 

0.85 

123478 

2.81 

2.81 

2.82 

2.82 

2.83 

2.82 

2.82 

2.82 

2.2 

2.: 

2.: 

2.:: 

2.83 

2.82 

2.82 

2.83 

2.83 

f :f 

2.82 

2.82 

2.91 

2.84 

2.: 

2.: 

2.84 

0.94 

2.83 

2.81 

2.84 

0.88 

0.84 

2.: 

5.2 

2.:: 

WA 

NA 

2.83 

123678 123789 

HXCDF HXCDF 

FE 

2183 

2.83 

2.85 

?: 

2183 

IA 

2.84 

2.84 

2.84 

WA 

2.81 

2.: 

2.85 

2.83 

2.83 

2.84 

2.84 

2.85 

2.82 

2.84 

2.83 

2.85 

2.85 

2.: 

2.: 

2.86 

1.19 

2.84 

2.83 

2.85 

1.10 

1.10 

2.84 

2.85 

IA 

5.69 

3.48 

2.84 

2.:: 

2.84 

2.76 

2.75 

2.76 

2.76 

2.77 

2.76 

2.76 

2.76 

2.78 

2.76 

2.77 

f-E 

2174 

0.97 

2.77 

2.77 

2.76 

2.76 

:%+ 

2:78 

2.75 

2.76 

2.76 

2-z 

2:76 

2.77 

2.76 

2.78 

2.78 

1.07 

2.77 

2.76 

2.78 

0.99 

0.87 

2.77 

2.78 

2.77 

5.55 

2.78 

2.77 

0.87 

2.78 

2.77 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

1.95 

1.94 

1.95 

1.95 

1.w 

1.95 

l.% 

1.95 

NA 

1.95 

WA 

1.95 

NA 

1.94 

1.65 

::z 

1.95 

1.95 

1.96 

1.96 

1.97 

1.95 

1.95 

1.95 

1.96 

1.96 

1.:: 

1.95 

1.96 

WA 

1.04 

1-w 

1.95 

1.96 

0.91 

0.86 

1.96 

1.96 

3.; 

NA 

1.96 

NA 

1.96 

1.96 

1.44 

1.43 

1.44 

1.44 

1.45 

1.44 

1.44 

1.44 

NA 

1.44 

1.44 

1.44 

1.59 

1.43 

WA 

1.:: 

1.44 

1.44 

1.44 

1.44 

NA 

1.44 

WA 

1.44 

NA 

1.45 

1.:: 

1.:: 

WA 

0.66 

1.44 

1.44 

1.45 

0.67 

0.65 

NA 

1.45 

WA 

2.89 

WA 

1.44 

NA 

WA 

1.44 

2.60 

2.59 

2.61 

2.60 

2.62 

2: 

f:Zi 

2.61 

2.61 

2.61 

2.60 

2.59 

1.88 

2.61 

2.62 

2.61 

2.61 

2.61 

2.61 

2.62 

2.M) 

2.61 

2.61 

2.62 

2.62 

z! 

2.60 

2.62 

2.62 

1.66 

2.61 

2.60 

2.62 

1.87 

1.80 

2.61 

2.62 

2.62 

5.23 

2.62 

2.61 

3.01 

2.62 

2.61 

D-&41 
Episode SCC Type Description 

145 SD016111 F W Rcdhorse Sucker 

46 DDO16113 F W Creek Chtbsucker 

;d6 DDO16114 F PF Lm Bass 

&6BDD42OBB L W Creek Chubsucker 

;L6 50016113 F W Creek Chtbsucker 

;46 SD016114 F PF Lm Bass 

Y7 DDO16115 F W Carp 

47 DDO16116 F PF Lm Bass 

~47 SD016115 F W Carp 

M DDO16117 F PF Hite Perch 

&8 DDOl6118 F W Blue Catfish 

3348 Q)ORBBB F W Blue Catfish 

3348 SD016117 F PF Uhite Perch 

3348 SD016118 F W Blue Catfish 

3349 DDO16119 F W Carp 

3349 DDO16120 F PF 11 Bass 

3350 DDO16121 F W Carp 

3350 00016122 F PF Lm eass 

3350 QDO5268B F W CarD 

3351 DO016123 F PF Rccic Bass 

3351 Do016124 F W Carp 

3351 WOZlB8B L W Carp 

3352 DF023723 F PF Crappie 

3352 DF023724 F UB Carp 

3352 POW1388 F W Carp 

3353 DFO24121 F BP Blue Catfish 

3353 DF024122 F W Sm Buffalo 

3353 a0024121 1 BF Blue Catfish 

3354 DYO22301 F W Carp 

3354 DY022302 F PF Lm Bass 

3355 DYO22303 F W Carp 

3355 DY0223D4 F PF Lm eass 

3355 SYO22303 F W Care 

3356 DE030201 F W Car; 

3356 SE030201 F W Carp 

3357 DY022223 F PF -fish 

3357 DY022224 F W Sacrmnento Sucker 

3360 DD029117 F W Carp 

3360 DDO29118 F PF Lm Bass 

3360 QDO22389 L W Carp 

3375 Do016305 F W Carp 

3375 DDO163W F PF Ln Bass 

3375 9olOllBB L W Carp 

3376 DDOl6307 F W Carp 

3376 DDO163OB F PF Lm Bass 

3376 a0050389 L PF Lm Bass 

3377 000163W F W Carp 

2378 

TCDD 

NA 

NA 

IA 

WA 

WA 

NA 

IA 

NA 

WA 

NA 

IA 

IA 

WA 

IA 

IA 

WA 

IA 

WA 

IA 

HA 

WA 

WA 

1.00 

WA 

IA 

WA 

NA 

WA 

1.:: 

1.:: 

IA 

NA 

IA 

NA 

NA 

1.:: 

2.36 

IA 

NA 

IA 

1.:: 

1.19 

WA 

12378 

PECDD 

IA 

WA 

0.98 

NA 

IA 

NA 

IA 

WA 

NA 

WA 

WA 

WA 

NA 

WA 

0.: 

WA 

0.91 

WA 

0.92 

NA 

0.:: 

NA 

IA 

NA 

WA 

WA 

WA 

WA 

1.; 

NA 

WA 

WA 

WA 

WA 

IA 

1.14 

WA 

NA 

1.19 

NA 

1.:: 

1.29 

IA 

010X11 / FURAN DETECTlOll LIMITS. w/R 

123478 

HXCDD 

2.:; 

2.46 

2.46 

NA 

0.90 

IA 

2.46 

2.:: 

IA 

1.:: 

NA 

WA 

2.47 

2.2: 

2.:: 

WA 

2.2: 

IA 

2.2: 

2.2; 

2.23 

NA 

2.46 

IA 

WA 

2.2 

2.45 

2.47 

2.46 

2.46 

IA 

2.46 

IA 

2.x 

2.83 

WA 

123678 

HXCDD 

IA 

1.85 

1.84 

1.84 

WA 

0.69 

8.97 

IA 

IA 

IA 

IA 

0.: 

WA 

IA 

1.04 

1.: 

1.: 

NA 

WA 

1.113 

NA 

IA 

NA 

NA 

WA 

NA 

WA 

NA 

IA 

IA 

IA 

WA 

WA 

WA 

1.: 

WA 

IA 

IA 

IA 

2.:; 

2.12 

IA 

1237B9 1234678 

HXCDD 

NA 

1.3B 

1.37 

1.37 

NA 

1.15 

WA 

1.37 

1.: 

NA 

1.:: 

1.51 

WA 

1.38 

IA 

1.37 

WA 

1.38 

WA 

1.36 

1.37 

IA 

WA 

IA 

NA 

WA 

WA 

1.38 

IA 

1.37 

IA 

WA 

1.:; 

1.37 

1.38 

1.3B 

1.38 

WA 

1.37 

WA 

1.:: 

1.62 

IA 

HPCDD 

NA 

IA 

IA 

IA 

IA 

WA 

IA 

NA 

WA 

NA 

IA 

IA 

IA 

IA 

IA 

WA 

1.; 

1.; 

NA 

WA 

IA 

WA 

IA 

NA 

IA 

WA 

NA 

IA 

NA 

NA 

WA 

WA 

1.:: 

IA 

1.:: 

WA 

IA 

IA 

NA 

NA 

1.:: 

IA 

. .- - 

2378 12378 

TCDF PECDF 

NA 

IA 

IA 

WA 

WA 

NA 

IA 

IA 

WA 

IA 

WA 

WA 

IA 

WA 

IA 

IA 

IA 

0.77 

IA 

0.63 

IA 

0.:: 

NA 

NA 

WA 

WA 

NA 

WA 

0.57 

IA 

0.62 

IA 

WA 

WA 

NA 

WA 

1.:: 

WA 

NA 

IA 

HA 

NA 

0.64 

0.64 

IA 

0.92 

IA 

0.77 

IA 

NA 

WA 

WA 

0.77 

NA 

IA 

WA 

WA 

WA 

IA 

NA 

0.77 

0.: 

WA 

0.77 

WA 

IA 

0.77 

0.78 

0.77 

0.77 

0.: 

NA 

0.77 

WA 

0.77 

WA 

WA 

NA 

0.77 

0.: 

0.81 

0.77 

IA 

0.81 

WA 

0.: 

0.78 

WA 

23478 

PECDF 

WA 

WA 

IA 

NA 

NA 

2.: 

0.85 

IA 

WA 

IA 

WA 

NA 

WA 

IA 

0.85 

WA 

0.84 

WA 

0.85 

IA 

WA 

0.84 

0.85 

0.91 

WA 

WA 

1.09 

WA 

0.85 

1.; 

IA 

IA 

IA 

IA 

WA 

WA 

0.87 

IA 

WA 

WA 

IA 

IA 

0.85 

0.85 

IA 

123478 

HXCDF* 

0.76 

2.B4 

2.B3 

f-F 

0:76 

NA 

2.B3 

IA 

2.B4 

2.B4 

IA 

0.94 

1.05 

2.B4 

2.B3 

2.: 

2.: 

WA 

2.: 

f:ii 

;-ii 

2:B4 

2.: 

2.: 

WA 

IA 

2.: 

2.112 

2.B3 

2.B3 

2.B3 

IA 

2.B2 

IA 

2.: 

2.w 

WA 

123678 

HXCQF 

1.25 

2.85 

2.B4 

2.B4 

1.28 

1.25 

3.08 

2.B4 

2.: 

2.B4 

2.85 

1.19 

1.11 

2.85 

2.B4 

IA 

2.B3 

IA 

2.04 

WA 

WA 

f-Z 

2:B3 

2.83 

2.84 

2.115 

IA 

2.84 

NA 

2.B4 

IA 

IA 

WA 

2.w 

2.83 

2.85 

2.B4 

2.84 

NA 

2.84 

IA 

2.; 

2.85 

NA 

123789 234678 1234678 1234789 

HXCDF HXCDF HPCDF HPCDF 

0.88 

2.78 

2.77 

2.77 

0.94 

0.87 

2.77 

2.77 

0.99 

2.M 

2.77 

2.m 

1.07 

0.99 

2.78 

2.77 

2.77 

2.76 

2.78 

2.77 

2.76 

2.74 

2.75 

2’:; 

2.76 

2.77 

2.n 

2.77 

2.77 

2.77 

2.77 

0.20 

2.77 

0.96 

2.77 

2.76 

2.77 

2.77 

2.77 

2.77 

2.76 

2.76 

2.76 

2.78 

0.83 

1.96 

1-w 

1.96 

0.118 

0.83 

WA 

A:: 

::it 

::: 

0.91 

1.96 

1.96 

IA 

1.95 

IA 

1.96 

IA 

1.; 

1.96 

1.95 

1.45 

1-w 

1.96 

2.17 

1-w 

1.: 

NA 

IA 

WA 

::2 

1.96 

1.96 

1.96 

1.: 

IA 

IA 

1-w 

1.w 

IA 

0.81 

1.45 

1.44 

i% 

0.81 

IA 

IA 

1.:: 

1.45 

1.45 

0.66 

0.68 

1.45 

1.45 

1.: 

1.:: 

IA 

1.2: 

1.45 

1.44 

1.44 

1.44 

1.45 

IA 

1.45 

WA 

1.44 

WA 

NA 

IA 

1.44 

1.44 

1.45 

1.44 

1.45 

NA 

1.44 

IA 

1.:: 

1.45 

IA 

3.01 

2.62 

2.61 

2.61 

3.01 

3.01 

2.61 

2.61 

1.81 

5:: 

2.62 

1.66 

1.81 

2.62 

2.61 

2.61 

f :Z 

2.61 

2.60 

2.59 

2.59 

2.62 

2.61 

2.60 

2.61 

2.62 

2.62 

2.61 

2.: 

NA 

2.61 

1.87 

2.61 

2.60 

2.62 

2.61 

2.61 

IA 

2.61 

WA 

WA 

2.62 

2.62 

IA 

D-4-42 
Episode SCC Type Description 

3377 DD016310 F PF Lm Bass 

3377 SD016309 F W Carp 

3378 DDD16311 F UB Spotted Sucker 

3378 DD016312 F PF Lm Bass 

3378 DD029115 F UB Creyfin Sucker 

3378 DDO29116 F BF Channel Catfish 

3385 DD016-401 F W Rcdhorse Sucker 

33% DO016421 F W Redhorse Sucker 

33% DD016422 F PF Lm Bass 

33% SD016421 F UB Redhorse Sucker 

3401 DD0165W F UB Carp 

3401 DD016510 F PF Lm Bass 

3403 DD016513 F UB River Carpsucker 

3403 DD016514 F PF Lm Bass 

3404 DD016515 F W Carp 

3404 DD016516 F PF Lm Bass 

3404 SD016515 F W Carp 

3409 De040701 F W Carp 

3400 DBO40706 F PF Lm Bass 

3411 DBD40501 F UB Redhorse Sucker 

3412 DBD40901 F PF Sm Bass 

3412 De040907 F W Carp 

3412 SBD40907 F UB Carp 

3414 DC036203 F PF Sm Bass 

3414 DC036204 F BF Channel Catfish 

3415 DC036205 F PF SRI Bass 

3415 DC036206 F PC Channel Catfish 

3416 DF025210 F BF Channel Catfish 

3416 DF025211 F BF Carp 

3416 DF025212 F PF Lm Bass 

3418 DF025007 F BF Blue Catfish 

3419 DC036207 F UB Uhite Sucker 

3419 DC036208 F PF Freshwater Drus 

3420 DC036209 F PF Greenfish 

3420 DC036210 F UB Carp 

3421 DC036211 F PF White Perch 

3421 DC036212 F W Carp 

3421 SC036212 F W Carp 

3422 DC036213 F PF Lm Bass 

3422 DC036214 F W Yellow Bullhead 

3423 DC036215 F PF Uhite Perch 

3423 DC036216 F W llhite Catfish 

3424 DC036217 F PF Shortnose Gar 

3424 DC036218 F W Uhite Catfish 

3425 DF025005 F HI Carp 

3425 OF025012 F BF Chamel Catfish 

3425 CtDO31389 L BF Chamel Catfish 

DIOXIN / FURAN DETECTION LIMITS. m/g 

2378 12378 123478 123678 

TCDD PECDD HXCDD HXCDO 

1.24 

IA 

1.:; 

1.: 

WA 

WA 

IA 

WA 

1.:: 

WA 

IA 

WA 

NA 

WA 

1.: 

WA 

IA 

WA 

WA 

1.11 

1.: 

WA 

WA 

1.:: 

NA 

1.16 

0.99 

WA 

IA 

NA 

NA 

NA 

WA 

WA 

WA 

WA 

NA 

WA 

IA 

IA 

IA 

O.% 

1.: 

3.06 

1.:: 

1.26 

NA 

1.25 

IA 

WA 

0.94 

1.:: 

1.:: 

NA 

0.:: 

IA 

1.00 

NA 

IA 

0.92 

1.22 

0.92 

IA 

1.17 

1.37 

1.09 

1.01 

1.19 

0.91 

IA 

0.: 

IA 

NA 

0.94 

0.91 

1.07 

0.: 

WA 

IA 

NA 

IA 

2.46 

2.:: 

2.47 

WA 

2.47 

2.46 

3.33 

2.46 

1.59 

2.:: 

2.:: 

NA 

2.46 

NA 

2.9: 

2.46 

2.45 

WA 

2.2: 

2.47 

2.46 

2.:: 

2.47 

2.46 

2.46 

2.47 

2.45 

2.46 

2.95 

2.46 

2.47 

2.2; 

2.45 

2.47 

2.45 

2.46 

2.56 

2.2: 

2.46 

1.88 

WA 

2.02 

1.85 

NA 

1.84 

WA 

WA 

1.84 

WA 

WA 

WA 

1.:: 

WA 

1.85 

NA 

1.: 

1.: 

#A 

1.: 

NA 

1.84 

1.; 

1.84 

1.84 

1.84 

1.84 

1.83 

WA 

WA 

1.84 

NA 

1.2 

1.83 

1.84 

IA 

1.: 

NA 

2.2: 

123789 1234618 

HXCDD HPCDD TCDF PECDF 

1.38 

IA 

1.37 

1.38 

1.38 

1.38 

1.37 

WA 

1.38 

1.39 

IA 

1.37 

1.:: 

1.:: 

WA 

WA 

1.38 

1.38 

1.37 

WA 

WA 

1.37 

1.38 

1.38 

1.37 

1.37 

1.38 

1.37 

1.38 

1.38 

1.37 

1.37 

1.:; 

WA 

1.: 

1.37 

1.38 

WA 

1.37 

WA 

IA 

WA 

NA 

2.27 

WA 

1.:: 

1.: 

WA 

NA 

IA 

WA 

WA 

1.35 

WA 

1.42 

NA 

IA 

NA 

IA 

IA 

1.:: 

NA 

WA 

1.26 

WA 

1.39 

WA 

WA 

WA 

1.32 

1.52 

1.55 

1.25 

IA 

WA 

1.56 

WA 

NA 

1.71 

IA 

WA 

IA 

WA 

IA 

IA 

NA 

IA 

NA 

WA 

WA 

0.53 

0.:: 

WA 

WA 

NA 

WA 

NA 

WA 

IA 

NA 

WA 

IA 

IA 

IA 

IA 

WA 

NA 

IA 

0.:: 

0.2: 

WA 

IA 

NA 

NA 

WA 

0.2 

WA 

WA 

IA 

WA 

WA 

NA 

WA 

WA 

IA 

IA 

IA 

WA 

NA 

WA 

0.77 

WA 

0.91 

0.78 

0.94 

0.80 

0.77 

0.: 

WA 

NA 

0.77 

NA 

0.77 

0.: 

IA 

NA 

0.77 

0.94 

0.77 

IA 

IA 

0.77 

0.78 

0.77 

IA 

0.82 

0.77 

0.77 

0.77 

0.91 

0.77 

NA 

NA 

0.77 

WA 

0.: 

0.77 

0.77 

IA 

0.77 

0.85 

0.: 

0.85 

* .--- 

2378 12378 23478 123478 123678 123789 

PECDF HXCDF” HXCDF HXCDF 

0.85 

WA 

WA 

0.85 

WA 

0.86 

IA 

NA 

1.16 

IA 

WA 

0.85 

NA 

1.04 

0.: 

NA 

WA 

0.85 

WA 

1.18 

IA 

WA 

IA 

WA 

0.85 

IA 

0.94 

1.24 

0.85 

1.12 

1.61 

0.84 

IA 

WA 

S:: 

IA 

0.85 

0.87 

0.87 

WA 

1.19 

WA 

WA 

WA 

IA 

2.83 

NA 

2.83 

2.84 

2.84 

2.83 

2.82 

2.84 

2.83 

0.94 

2.81 

2.83 

WA 

ES 

2.83 

0.94 

2.: 

2.: 

WA 

2.: 

2.83 

2.B3 

2.83 

2.B2 

2.83 

2.113 

2.83 

2.83 

2.02 

5.: 

2:m 

WA 

2.; 

2.82 

2.83 

2.B2 

2.82 

2.B2 

2.89 

f :E 

2.84 

2.2 

2.85 

2.85 

2.85 

2.83 

2.; 

1.19 

2.83 

2.84 

WA 

f :Z 

2.84 

1.18 

WA 

2.84 

f :Z 

WA 

IA 

5:E 

2.84 

2.B4 

I:: 

5:: 

2.85 

5:: 

2.85 

2: 

::: 

2.83 

2.84 

IS! 

2.B3 

2.: 

2.B4 

2.77 

1.40 

2.77 

5:E 

Z:R 

5:: 

1.07 

2.76 

2.77 

2.76 

2.76 

2.76 

2.77 

1.06 

f :ZS 

52 

2.77 

1.07 

2.76 

2.77 

2.77 

2.77 

2.76 

2.77 

f :Z 

f-E 

2177 

2.77 

f:Z 

0.89 

x 

2:77 

2.76 

2.76 

2.76 

2.77 

2.76 

2.77 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

1.w 

1.2 

::: 

::it 

1.96 

1-w 

::2 

1.45 

WA 

::: 

1.w 

1.03 

1.: 

1-w 

1.95 

1.: 

l.% 

1.w 

::2 

::: 

1-w 

1.96 

::: 

::: 

1.96 

1.96 

0.87 

1.w 

1.95 

1.96 

::: 

::9”7 

1.44 

IA 

1.44 

1.45 

1.45 

1.45 

1.44 

1.54 

1.45 

IA 

IA 

1.44 

WA 

1.44 

IA 

1.44 

NA 

1.:: 

WA 

1.44 

WA 

1.:: 

1.45 

1.44 

1.44 

:::: 

1.44 

1.45 

1.45 

1.44 

1.:; 

1.44 

1.45 

0.66 

1.45 

1.44 

1.45 

1.44 

1.44 

1.44 

IA 

2.61 

0.93 

2.61 

2.62 

2.62 

2.62 

2.60 

2.62 

2.61 

1.66 

2.60 

2.61 

2.: 

2.60 

2.61 

1.65 

2.61 

2.61 

2.61 

2.60 

2.61 

1.66 

2.61 

2.62 

2.61 

2.61 

2.61 

2.61 

2.61 

2.61 

2.62 

2.60 

2.61 

2.62 

2.61 

2.62 

1.66 

2.62 

2.60 

2.61 

2: 

2.60 

5:: 

2.61 

D-443 
Episode SCC Type Description 

3426 DBD69102 F PF Bluefish 

3427 08069103 F PF Bluefish 

3428 08069104 F PF Bluefish 

3429 DBD69105 F PF Ueakfish 

3430 DBo691D6 F W Mite Catfish 

3431 De069109 F W Red Snapper 

3432 DBO69111 F BF Red Snapper 

3433 08069112 F UP Flow&r 

3433 PO021689 L VP Flounder 

3434DBO408OlFUPFlouder 

3435 DDO166Dl F PF White Bass 

3435 DDO16602 F W Bigmouth Buffalo 

3437 DJ022302 M W Crayfish 

3438 DJO22303 II Du&ness Crab 

3439 DJ022304 F W Uhite Sturgeon 

3439 90062289 L W Uhite Stur&on 

3440 05022305 F W Uhite Sturgeon 

3441 05022306 F W Uhite Sturgeon 

3442 DF024301 F BF Charnel Catfish 

3442 a0081089 1 BP Channel Catfish 

3444 DDO16603 F W Carp 

3444 Do016604 F BF Charnel Catfish 

3444 DDO29512 F PF Lm Bass 

3444 QoWl289 F W Carp 

3445DD029S13FWFlowder 

3445 00029514 F W Mar&cad Catfish 

3446 DDO16605 F PF Striped Bass 

3446 DDO16606 F W Carpsucker 

3446 00029511 F W Carp 

3446 POW2089 F W Carp 

3450 DY022308 F PF Uhite Croaker 

3450 DYO223W F PF Uhite Croaker 

3451 DY022310 F PF mite Croaker 

3451 DY022314 F PF White Croaker 

3452 DF025218 F W Sm Buffalo 

3452 OF025219 F BF Blue Catfish 

3452 OF025220 F PF Flathead Catfish 

3452 40103189 F W Sm Buffalo 

2378 

TCDD 

NA 

1.; 

0.99 

NA 

1.22 

0.99 

WA 

NA 

WA 

1.72 

1.:: 

2.:; 

NA 

IA 

A:2 

0.99 

NA 

WA 

1.44 

1.: 

UA 

IA 

NA 

NA 

IA 

WA 

NA 

MA 

NA 

WA 

NA 

WA 

NA 

12378 

PECDD 

0.95 

0.94 

1.01 

1.00 

1.01 

WA 

1.01 

1.:: 

1.:; 

0.2 

1.22 

0.94 

1.06 

1.12 

0.92 

0.96 

0.92 

WA 

NA 

1.20 

1.:: 

1.:: 

0.92 

1.20 

1.28 

1.28 

1.64 

1.74 

1.48 

1.10 

WA 

1.16 

1.10 

DIOXIN / FURAN DETECTION LIMITS, pg/g 

123478 123678 

2.47 

2.47 

2.46 

2.46 

2.47 

2.57 

2.46 

2.46 

2.46 

t2:: 

3.04 

2.45 

2.45 

2.47 

2.47 

2.46 

2.48 

2.47 

2.45 

WA 

2.2 

2.2: 

3.18 

2.45 

2.46 

2.46 

2.46 

2.47 

2.46 

2.47 

2.47 

2.46 

2.71 

2.47 

2.47 

1.85 

1.84 

1.84 

1.84 

NA 

1.85 

1.84 

NA 

NA 

WA 

1.85 

1.: 

1.; 

1.85 

1.84 

1.85 

1.85 

1.84 

WA 

2.:: 

1.2 

1.:: 

1.84 

NA 

WA 

1.84 

:-z 

1:85 

1.84 

2.03 

1.84 

1.84 

123789 1234678 

HXCDD 

1.38 1.26 

1.38 1.26 

1.37 1.26 

1.37 1.26 

1.38 

1.38 1.:: 

1.37 1.26 

1.37 WA 

1.37 NA 

1.37 

1.38 1.:: 

1.:; 

MA 

1.37 3.: 

1.38 IA 

1.38 IA 

1.37 1.51 

1.38 

1.38 1.:: 

1.37 1.25 

NA IA 

WA 

1.56 1.: 

1.:: 

WA 

WA 

1.:: 

IA 

1.65 

1.37 1.59 

1.38 IA 

1.37 WA 

1.38 1.35 

1.37 1.26 

1.38 1.26 

1.38 1.26 

1.38 1.39 

1.54 1.99 

1.38 1.26 

1.38 1.29 

2378 12378 23478 123478 123678 123789 

TCDF PECDF PECDF HXCDF* HXCDF HXCDF 

WA 

WA 

WA 

0.49 

NA 

WA 

0.49 

IA 

IA 

IA 

IA 

IA 

NA 

WA 

NA 

WA 

NA 

WA 

0.49 

0.48 

WA 

0.59 

0.75 

NA 

0.58 

0.64 

IA 

WA 

RI 

0.:; 

0.49 

0.57 

0.55 

WA 

WA 

0.54 

WA 

0.78 

NA 

0.87 

0.77 

IA 

WA 

0.77 

0.97 

1.03 

1.14 

0.80 

0.: 

0.91 

1.03 

1.:; 

;:FZ 

0.77 

IA 

0.82 

0.87 

WA 

0.78 

0.78 

1.28 

1.05 

1.32 

1.39 

0.77 

X:p7 

1.02 

0.93 

0.80 

0.80 

0.80 

NA 

MA 

MA 

0.85 

NA 

IA 

0.85 

NA 

WA 

NA 

0.87 

0.: 

0.:: 

0.94 

0.93 

0.91 

0.85 

0.84 

WA 

WA 

0.91 

NA 

0.87 

1.19 

NA 

1.65 

NA 

NA 

0.93 

0.97 

0.96 

1.02 

0.96 

1.78 

0.86 

0.87 

z 

2:83 

2.83 

2.84 

f-E 

2183 

2.83 

2.83 

2.84 

WA 

2.82 

2.81 

2.83 

f-2 

2:83 

2.84 

2.82 

IA 

2':: 

2.:: 

2.84 

2.96 

2.82 

NA 

2.:: 

::: 

2.84 

2.83 

2.82 

2.83 

2.83 

2.85 

2.85 

2.84 

f 1: 

2.85 

2.84 

2.84 

2.84 

2.84 

2.85 

2.84 

2.83 

2.83 

2.85 

2.85 

2.84 

2.85 

2.85 

2.83 

2.E 

2.85 

IA 

2.84 

2.85 

2.83 

2.84 

2.94 

2.04 

2.84 

2.83 

2.85 

2.85 

2.84 

2.83 

2.84 

2.84 

2.78 

2.77 

2.77 

2.n 

2.78 

2; 

2.77 

2.77 

2.n 

2.77 

2.77 

2.76 

2.76 

2.77 

2.78 

2.77 

2.77 

2.78 

2.76 

2.77 

f :Z 

2.76 

2.77 

2.78 

2.76 

2.76 

2.77 

2.77 

2.n 

2.76 

2.78 

2.18 

2.77 

2.76 

2.n 

2.77 

234678 1234678 1234789 

HXCDF HPCDF HPCDF 

1.96 

1.96 

1.95 

1.96 

1.96 

1.96 

1.95 

:-2 

1:w 

1.96 

::2 

E 

:-z 

1:w 

i:E 

IA 

1.: 

1.2 

E 

::: 

::Ei 

:-iii 

1:96 

1.96 

1.95 

1.96 

1.96 

1.45 

1.45 

1.44 

1.44 

1.45 

1.45 

1.44 

1.44 

1.44 

1.44 

1.45 

1.:: 

1.54 

1.45 

1.45 

1.44 

1.45 

1.45 

1.44 

WA 

IA 

1.56 

WA 

1.44 

1.45 

1.44 

1.44 

1.70 

1.67 

1.45 

1.44 

1.45 

1.45 

1.44 

1.49 

1.45 

1.45 

2.62 

2.62 

2.61 

2.61 

2.62 

2.62 

2.61 

2.61 

2.61 

2.61 

2.62 

2.61 

2.60 

2.60 

2.62 

2.62 

2.61 

2.62 

2.62 

2.60 

3.02 

2.62 

2.78 

2.97 

2.61 

2.62 

2.68 

2.61 

2.61 

2.61 

2.61 

2.61 

2.62 

2.62 

2.61 

2.68 

2.61 

2.61 

D-4-44 
APPENDIX D-5 

Xenobiotic Data by Episode Number 
Key for Xenobiotic Data Table (Units = n&g) 

Mere 

123 TCB 

124 TCB 

135 TCB 

I234 TCB 

1235 TCB 

1245 TCB 

OCS 

PCB 

PCNB 

HCB 

aBHC 

gBHC 

cis CHLOR 

trans CHLOR 

= Mercury, pg 7439-97-6 

= 1,2,3 Trichlorobenzene 87-61-6 

= 1,2,4 Trichlorobenzene 120-82- 1 

= 1,3,5 Trichlorobenzene 108-70-3 

= 1,2,3,4 Tetrachlorobenzene 634-66-2 

= 1,2,3,5 Tetrachlorobenzene 634-90-2 

= 1,2,4,5 Tetrachlorobenzene 95-94-3 

= Qctac hlorostyrene 29082-74-4 

= Pentachlorobenzene 608-93-5 

= Pentachloronitrobenzene 82-68-8 

= Hexachlorobenzene 118-74-l 

= alpha BHC 3 19-84-6 

= gamma BHC (lindane) 58-89-9 

= cis Chlordane 5103-71-9 

= trans Chlordane 5 103-74-2 

GS 

D= Value below limit of quantitation for all xenobiotics except mercury and PCBs 

D = 2.5 ngfg 

For polychlorinated biphenyls 

ofl-3 1.25 

4-6 2.50 

7-8 3.75 

9-10 6.25 

Detection limit for mercury was 0.05 lg/g, except for 1990 samples which had a detection limit 

of 0.0013 pg/g. 

E = Value exceeds highest calibration standard 

See Dioxin/Wan Data Table Key for explanation of other codes. The tables include 

environmental samples (those starting with a sample number of D) and the duplicate samples 

(those starting with a Q) and confirmation samples (those starting with an S). The number of 

samples shown on the summary tables in Volume I does not include the duplicate and 

confirmation samples. 

D-5-l 
D-S-2 
XENOBlOTICS CONCENTRATIONS, rig/g 

Episode SCC Type Description 

1994 DE017703 f PF UeLLeye 

1994 DE017702 F IJB Carp 

1998 13421 F PF Northern Pike 

1998 i3285- F uB Carp 

2015 DFOOlOO2 F UP Crappie 

2015 0F001001 F UB Carp 

2016 DF001102 F BF Sucker 

2016 OF001101 F UB Sucker 

2017 DF001202 F EF Carp 

2017 DFOOl201 F UB tarp 

2018 DF001301 F UB Sucker 

2023 DF001402 F PF Spotted Bass 

2023 OF001403 F UB Carp 

2026 DF001706 F UB FLathead Catfish 

2026 DFOOT702 F IJB Carp 

2027 OF001802 F PF Lm Bass 

2027 OF001803 F UB Carp 

2037 DYOOO502 F VP not available 

2037 DYOOO501 F UB not available 

2056 DE000501 F UB Carp 

2057 DE000601 F UB Carp 

2059 DE000801 F UB Carp 

2060 DE000901 F UB Carp 

2070 DJ000901 F UP Rainbow Trout 

2070 05000902 F b/B Lononose Sucker 

2098 DHOOl504 F PF not-available 

2098 DH001501 F UB not available 

2100 WOO1702 F PF Sauger 

2100 DH001703 F UB Catfish 

2105 OH002201 F PF Sauger 

2105 OH002204 F UB Carp 

2109 DHO02602 F BF not available 

2109 DHOO2601 F YE not available 

2110 DHO02710 F UP Brown Trout 

2122 DHOO3901 F PF Rait-bou Trout 

2122 DH003904 F MB Uhite Sucker 

2126 DDO00303 F PF Uhite Crawie 

2126 DDOOO302 F VB Carp ” 

2133 DO001002 F BF BLue Catfish 

2138 DD001504 F PF Lm Bass 

2138 DDOOl501 F UB Redhorse Sucker 

2139 DD001604 F PF Rainbow Trout 

2139 DDOO1601 F UB Carp 

2142 DDOO1903 F PF Lm Bass 

2142 DO001902 F UB Catfish 

Mere 123 124 135 1234 1235 1245 

c9/9 TCB TCB TCB TCB TCB TCB 

0.12 

0.11 

0.28 

0.08 

0.17 

0.14 

0.31 

0.18 

0.15 

0.11 

0.07 

0.24 

0.16 

0.14 

0.16 

1.63 

0.21 

0.09 

0.10 

0.06 

0.12 

0.14 

0.09 

ND 

ND 

ND 

ND 

0.35 

0.32 

0.45 

ND 

0.12 

ND 

ND 

0.11 

0.12 

0.71 

0.14 

0.37 

0.88 

0.437 

!"08 

0.348 

0.10 

1.40 D 1.35 D ND 

ND ND ND 

ND ND ND 

0.19 D 0.29 D ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

69.0 191 E 2.77 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

0.45 D 0.64 D ND 

ND ND ND 

ND ND ND 

ND ND ND 

0.60 D 0.35 D ND 

1.02 D 0.60 D ND 

0.15 D 0.35 D ND 

0.28 D NO ND 

ND 

ND 

b9 

ND 

ND 

ND 

ND 

11.5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

D ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

15.3 15.3 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND ND ND ND 

ocs PCB PCNB HCB aBHC gBHC 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?72 

ND 

20.7 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 4.07 3.58 

ND ND ND ND 

ND ND 2.52 4.10 

ND ND ND ND 

ND ND ND ND 

ND ND 0.66 D ND 

ND ND ND 1.26 

ND ND ND ND 

4.72 ND 19.7 18.6 

ND ND ND 7.84 

ND ND 4.56 9.80 

ND ND 2.18 D 3.63 

ND ND NO ND 

ND ND ND 6.42 

ND ND 2.52 6.58 

ND ND ND 1.55 

ND ND ND ND 

ND ND ND ND 

ND ND ND 3.98 

ND ND ND ND 

ND ND ND 1.39 

ND 

ND 

NO 

ND 

ND 

ND 

D ND 

ND 

ND 

15.3 

::26 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

D 1.64 

ND 

NO 

ND 

ND 

CIS TRAMS 

CHLOR CHLOR 

46.4 43.6 

7.67 ND 

5.17 3.50 

3.30 ND 

ND 5.20 

13.2 8.23 

3.04 1.96 D 

ND ND 

148 E 111 

60.2 38.9 

68.2 38.0 

74.9 55.5 

ND ND 

ND ND 

26.0 22.7 

ND ND 

14.3 16.5 

ND ND 

2.43 D ND 

ND 2.73 

D 4.06 3.46 

ND ND 

45.5 22.2 
XENOBIOTICS CONCENTRATIONS, rig/g 

Episode SCC Type Description 

2148 DDW2504 F BF Saltuater Catfish 

2148 DDW2501 F HI Saltwater Catfish 

2151 DO002801 F PF Ln Bass 

2151 WOO2803 F UB Spotted Sucker 

2152 00002902 F PF lm Bass 

2152 WOO2903 F UB Lake Chubsucker 

2190 DGOO5101 F H) Carp 

2100 DGW5184 F PF Bluegill 

2191 DGW5206 F BF Carp 

2191 DGW5205 F UB Carp 

21% DC005504 F BF Chamel Catfish 

21% DC005501 F UB Carp 

2199 DC006001 F UB Carp 

2199 DGW6OD4 F PF Ln Bass 

2201 DC006204 F PF Bouffn 

2201 DGOG6201 F UB Carp 

2205 DC006602 F BF Carp 

2205 DGOO6601 F UB Carp 

2210 DC805401 F UB Catfish 

2211 DCW5503 F UB Rcdhorse Sucker 

2212 DCOOS602 F PF Sm Bass 

2212 DC005605 F W rrhite Sucker 

2215 DC005902 F VB Carp 

2216 DC006002 F PF Brown Trout 

2216 DCW6803 F UB White Sucker 

2220 DC006401 F PF Redbreast Sunfish 

2220 DC806405 F UB Catfish 

2225 DC006903 F UB Shorthead Rcdhorse 

2225 DC006902 F PF Sm Bass 

2227 DC007102 F PF Ln Bbss 

2227 DC007104 F bB Channel Catfish 

2228 DC007204 F PF Redhorse Sucker 

2228 DC007201 F PF Longear Sunfish 

2231 DC007503 F UB Gizzard Shad 

2246 DJ002301 F BF Bridgelip Sucker 

2246 05002302 F UB BridgeliD Sucker 

2247 05002403 F PF Bridgeti; Sucker 

2247 05002404 F UP Mountain Uhitefish 

2280 OF005204 F BF Channel Catfish 

2280 OF005201 F UB Carp 

2280 00121688 L UB Carp 

2283 DFOO5502 F UP Longear Sunfish 

2283 OF005501 F UB Gray Rcdhorse 

2290 DO003402 F PF Lm Bass 

2290 DD003403 F UB Spotted Sucker 

Mere 123 124 135 1234 1235 1245 

c9/9 TCE TCE TCB TCB TCB TCB 

0.28 

0.12 

0.81 

0.07 

0.98 

0.13 

?a5 

0.05 

:24 

0:10 

ND 

0.27 

0.58 

0.12 

0.16 

0.07 

0.08 

O.lSl 

0.24 

0.06 

EC 

0.08 

0.07 

:125 

0.23 

0.614 

0.138 

0.08 

0.16 

ND 

0.52 

0.20 

0.19 

0.10 

0.29 

0.17 

ND ND ND 

1.35 D 1.01 D ND 

ND ND ND ND 

ND ND ND ND 

2.60 1.97 D ND ND ND ND ND 

ND ND ND ND ND ND ND 

0.92 0 0.67 0 ND ND ND ND ND 

ND ND ND 

ND 0.76 0 ND 

ND ND ND 

0.35 0 0.26 D ND 

ND 0.35 0 ND 

0.28 0 0.45 0 ND 

ND 4.60 ND 

0.33 0 0.64 0 ND 

0.71 0 0.59 0 ND 

ND ND ND 

ND ND ND 

ND 0.15 0 ND 

ND ND ND ND 

ND 

ND 

ND 

0.10 

ND ND ND 

ND ND ND 

ND ND ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 0.46 0 ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND 0.82 0 ND 

ND ND 

ND ND 

ND 

ND 

ND ND 

0.38 0 ND 

ND 

ND 

ND ND ND 

ND ND ND 

0.13 

0.15 

1.13 

0.21 

ND ND 

17.7 104 

ND 

9.20 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND 12.0 12.0 ND ND ND 

OCS PCB PCNB HCB aBHC gBHC 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

2.43 0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.88 DND 

ND ND 

!!32 0 iii 

1.93 D ND 

ND 

ND 

ND ND 

ND ND 

ND 

0.51 

ND 

2.15 

11.6 

ND 

ND 

ND ND ND ND 

0 1.09 0 1.68 D 69.7 E 182 E 

ND ND ND ND 

0 10.2 

1.89 

ND 

ND 

ND 

0 11.9 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

Fo7 

ND 

ND 

2.72 

ND 

ND 

ND 

ND 

0.93 

6.55 

2.33 

ND 

ND 

ND 

ND 

D ND 

ND 

0 2.70 

1.36 

7.18 

13.6 

ND ND 

0.78 0 ND 

ND 

K2 

ND 

ND 

ND 

ND 

ND 

ND 

0.83 

ND 

15.7 

ND 

7.75 

ND 

ND 

ND 

ND 

D ND ND ND 

ND ND ND 

8.78 128 87.7 

ND 3.07 ND 

ND 

ND 

1.28 

ND 

ND 

CIS TRAMS 

CHLOR CHLOR 

4.90 3.97 

ND ND 

76.2 107 

77.5 72.9 

34.5 34.6 

19.9 11.0 

3.99 ND 

ND 166 E ::6 

7.14 3.94 

D 6.05 2.27 0 

112 E 64.3 

378 E 310 E 

ND ND 

4.57 2.40 0 

3.51 9.70 

2.46 D 1.17 D 

D 2.41 D 1.20 D 

ND ND 

41.8 39.8 

D-s-4 
XENOBIOTICS CONCENTRATIONS, rig/g 

Episode SCC Type Description 

2294 DD003801 F PF Lm Bass 

2294 DDOO3804 F UB Carp 

2297 DDoO4l03 F PF Lm Bass 

2297 DO004102 F NB Carp 

2298 000042Ol F UB Chat-net Catfish 

2298 DO004203 F UP Lm Bass 

2301 00004502 F UB Sm Bass 

2301 WOO4503 F UB Bluegill 

2301 DDO04501 F Up Btack Crappie 

2301 00004504 F UP Rock Bass 

2302 WOO4601 F YB guillback Carpsucker 

2304 00004804 F PF Ln Bass 

2304 DO004801 F UB Corn 

2309 WOOS304 F PF Lm bass 

2309 DDW530l F UB Carp 

2322 DBW1304 F PF Ln Bass 

2322 DBW13ol F UB Uhite Sucker 

2326 DB001704 F PF Rock Bass 

2326 DBW1701 F UB tiite Sucker 

2328 DBW1904 F PF Chinook Sabnon 

2329 DBW2004 F PF Broun Trout 

2341 Woo6002 F PF ln Bass 

2341 DDOO6003 F UB Carpsucker 

2355 DAW1603 F UB Hite Sucker 

2356 DA001703 F UB Ilhite Sucker 

2356 DAWl702 F PF Lm Bass 

2369 DA003202 F PF Lm Bass 

2375 DA003802 F PF Pickerel 

2375 DA003803 F UB Uhite Sucker 

2376 DA003903 F NB Uhite Sucker 

2379 DE005401 F UB Carp 

2379 DE005404 F PF Lm Bass 

2380 DEOOS501 F UB Carp 

2383 DEWS801 F UB Carp 

2385 DE006002 F UB Uhite Sucker 

2387 DE006201 F UB Carp 

2387 DE006204 F PF Walleye 

2394 DE006901 F UB Carp 

2394 ODOO6901 L UB Carp 

2394 WO22189 L UB Carp 

2397 DE007204 F PF Ualieye 

2397 DE007201 F UB Sucker 

2410 DE008501 F UB Carp 

2410 DE008SO4 F PF Sm Bass 

2416 DE009101 F YB Carp 

I4erc 123 124 135 1234 1235 1245 OCS 

P9/9 TCB TCB TCB TCB TCB TCB 

0.592 

0.068 

0.522 

0.076 

0.11 

0.23 

0.18 

0.2 

0.11 

0.14 

0.366 

0.356 

0.230 

0.32 

0.16 

0.74 

0.20 

0.21 

:32 

0.24 

0.296 

0.06 

0.100 

0.2 

1.07 

0.47 

0.64 

0.17 

ND 

0.14 

0.45 

0.11 

0.16 

0.167 

0.06 

0.15 

0.03 

3.53 2.25 0 0.44 0 ND ND ND ND ND 

0.77 0 0.47 0 ND ND ND ND ND ND 

0.51 0 0.37 0 ND ND ND ND ND ND 

ND ND w ND 

ND 0.29 D ND ND 

ND 0.65 0 ND ND 

0.35 0 0.29 0 ND ND 

ND 0.47 0 ND ND 

iD.46 0 0.7854 0 ND 0.15 D ND 0.35 

2.11 0 1.73 0 ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

D 0.33 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0 0.33 0 16.8 

ND 14.8 

24.8 49.0 11.3 

ND 0.59 D : 

12.9 

ND ND 

12.9 14.3 8.56 ND 30.3 ND 15.2 

ND ND ND ND 1.95 7.22 ND 

0.60 0 0.32 0 ND ND ND ND ND ND ND ND ND ND 

ND 0.84 0 MA ND ND ND ND ND ND 1.42 0 1.09 0 ND 

ND 0.78 0 ND ND ND ND ND 0.82 0 ND 85.5 ND 5.43 

1.10 0 0.71 0 ND ND ND ND ND ND ND ND ND ND 1.28 0 ND 

3.23 5.66 0.29 0 0.93 0 ND ND ND 2.77 ND ND 17.4 la.1 100 78.5 

ND 1.28 0 ND ND ND ND ND 3.40 ND 6.94 19.3 la.9 179 12s 

0.57 0 0.57 0 ND ND ND ND ND ND ND ND ND ND ND ND 

ND 0.69 0 ND ND ND ND ND 

ND 1.25 0 ND ND ND ND ND 

ND ND ND MD ND ND ND 

;:1: 

8:: 

ND 

ND ND ND ND 

ND ?33 ND it45 0 ND ND 

ND ND ND ND ND ND 

ND 10.2 ND 4.76 ND ND 

:i 7 

5.61 

ND 

PCB PCNB HCB aBHC gBHC CIS TRAMS 

CHLOR CHLOR 

ND NO 

ND ND 

2.67 

ND 

ND ND ND 

3.98 UD 3.07 

ND 4.35 2.49 0 

ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND 2.94 ND ND 

ND ND ND ND ND ND 

14.9 

4.74 

ND ND ND 1.12 DO.58 01.26 ON0 

l&2 

1.46 

ND 1.16 0 0.27 0 1.96 

0 ND 8.19 2.27 0 1.33 

0 ND 8.87 4.76 ND 

01.08 DND 

0 18.1 5.58 

17.0 1.91 0 

125 E 84.7 

3.69 ND 

ND ND 

3.08 

30.6 

:!24 

1.63 

ND 6.10 9.16 15.8 83.2 71.5 

0 ND ND ND 25.1 129 107 

0 ND ND ND 18.2 118 96.0 

L4 

E"21 

ND 0.85 0 2.22 0 ND 

ND 25.3 20.8 ND 

ND 2.38 0 1.45 0 0.86 

ND ND 15.9 44.5 

2.70 

95.3 :9.8 

01.86 DID 

164 112 

D-5-s 
XENOBIOTICS CONCENTRATIONS, rig/g 

Episode see Type Description 

2422 DE009702 F UB Carp 

2427 DE010203 F PF Ualleve 

2427 DE010202 F UB Carp ’ 

2429 DE010403 F PF Ualleye 

2429 DE010402 F UB Carp 

2430 DE010602 F PF Northern Pike 

2430 DE010603 F UB Redhorse Sucker 

2430 40121488 1 UB Redhorse Sucker 

2431 DE010702 F PF Brown Trout 

2431 DE010703 F UB Sucker 

2432 DE010713 F PF Ualleye 

2432 DE010710 F UB RwHorse Sucker 

2435 DE011004 F PF Brook Trout 

2435 DE011001 F IJB Longnose Sucker 

2437 DE011202 F PF Welleye 

2437 DE011203 F UB Carp 

2439 DE011401 F UB Carp 

2439 DE011402 F VP Sm Bass 

2478 DJ003901 F RF Sucker 

2478 05003903 F IJB Chiselmouth 

2478 DJOO3902 F UB Sucker 

2500 DC010201 F PF Bass 

2500 DC010203 F UB Black Buffalo 

2532 OF019302 F PF Lm Bass 

2532 OF019303 F UB Carp 

2544 OF019203 F PF Lm Bass 

2544 OF019202 F UB BLacktail Redhorse 

2608 DE014501 F PF Ualleye 

2608 DE014504 F LIB Carp 

2618 DE015401 F !dB Carp 

2618 DE015402 F RF Carp 

2618 DE015403 F UB QuiLLback 

2651 DB008401 F UB White Sucker 

2653 DBO08503 F UB Carp 

2654 08008601 F UB Carp 

2709 DB005101 F UB Catfish 

2721 DA006502 F UB Sucker 

2721 a0011089 1 UB Sucker 

2722 DA006601 F UB Sucker 

2725 DA006301 F UB Sucker 

2748 DYOO6SW F RF Sucker 

2748 01006505 F UB Sucker 

2776 DY007103 F PF Trout 

2776 DYOO7101 F UB Carp 

2776 a0010489 1 UB Carp 

Here 123 124 13s 1234 1235 1245 

P9/9 TCB TCB TCB TCB TCB TCB 

0.206 

0.23 

0.10 

0.33 

0.27 

0.2 

0.10 

ND ND ND ND ND ND ND 2.72 

ND ND ND ND ND ND ND 7.51 

ND ND ND ND ND ND ND ND 

ND 

ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND 0.51 

0.27 

0.09 

0.49 

0.25 

0.13 

0.08 

0.29 

0.12 

0.05 

0.05 

0.16 

ND 

0.14 

0.26 

0.12 

0.11 

ND 

0.73 

0.58 

0.69 

0.18 

0.02 

0.06 

0.04 

0.28 

0.14 

0.68 

0.10 

0.11 

ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 1.76 

ND 

0.32 

ND ND 

1.24 0 ND 

ND ND 

ND ND 

ND MD 

ND ND 

ND ND 

ND ND 

ND ND 

1.81 0 ND 

ND ND 

ND ND 

D 0.47 D ND 

ND ND ND ND ND ND 2.36 

ND 

ND 

ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND 6.49 

ND ND ND ND ND ND 3.08 

ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

0.65 ND ND ND 6.27 9.61 ND 93.7 

ND ND ND ND ND ND ND ND 

2.11 

ND 

0.33 

1.86 

ND 

0 ND ND 

ND ND 

0 ND ND 

ND ND 

0 0.34 D ND 

0 1.49 0 ND 

0.45 0 ND 

0.34 

0.06 

ND 

ND 

ND 

ND 

0.47 0 0.93 0 ND 

10.59 264.81E ND 

1.59 0 3.01 ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

0.51 0 ND ND 

ND ND ND ND ND ND 

ND ND ND 11.3 ND ND 

ND ND ND 1.92 0 ND ND 

ND ND ND ND 2.92 ND 

ND ND ND ND ND ND 

ND ND ND ND 0.59 0 ND 

0.57 0 0.93 0 0.93 0 ND 1.98 0 ND 

ND 0.52 D 0.52 0 ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND ND ND ND ND ND 

Of.3 PCB PCNB HCB 

4.03 

22.5 

5.41 

ND 

ND 

2.56 

0.84 0 2.37 0 ND 

3.48 3.58 

ND 

ND 

ND 

ND 

11.3 ND 

29.0 ND 

9.09 4.65 

ND ND 

D 1.56 0 NO 

2.32 0 ND 

0 3.37 ND 

D 9.08 2.97 

:"56 F.4 

2.61 9.95 

1.04 0 ND 

0.52 0 2.18 

ND 2.24 

ND ND 

15.9 ND 

6.00 17.2 

2.07 0 6.58 

ND 24.4 

0.80 0 ND 

1.45 0 5.25 

ND 

ND 

ND 

ND 

3.97 

ND 

ND 

ND 

19.0 

CIS TRAMS 

CHLOR CHLOR 

ND ND 

92.1 45.8 

31.0 14.5 

ND ND 

NO ND 

ND ND 

ND ND 

26.5 11.8 

12.2 ND 

96.0 69.4 

41.0 20.3 

1.97 

D 6.51 

0 41.0 

ND 

0 ND 

5.53 

48.0 

4.86 

ND 

147 

39.4 

131 

9.90 

6.73 

118 

31.4 

97.1 

3.92 

ND ND 

37.25 64.66 

41.1 20.9 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.11 0 ND 

1.31 0 ND 

D-S-6 
XENGBIOTICS CONCENTRATIONS, rig/g 

Mere 123 124 13s 1234 1235 1245 

P9/9 TCB TCB TCB TCB TCB TCB 

ocs 

0.82 

MA ND ND 

0.31 

0.05 0.28 0 0.47 

ND ND 

0 0.18 0 0.25 

D ND 

0 ND tt”28 

0 ND .09 

ND ND ND 

0.37 0 0.22 

0.34 0 0.67 

0 ND 

ND 

0 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND -28 0 ND ND ND 

ND 

ND 

ND 

0.39 

ND 

0.17 

ND 

0 0.57 

ND ND ND ND ND 

0 ND ND 

ND ND 

ND ND ND 

ND ND ND 

0 ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND NND ND ND ND ND 

ND ND 

0 ND 

ND ND 

0.15 0 ND 

ND ND ND 

0.29 ND ND ND 

ND 

El9 

ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

0 ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND 0.46 0 ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND ND ND ND ND ND 

ND 1.16 0 0.66 0 ND ND ND ND 

0.14 0 0.09 D ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

Episode SCC Type Description PCB PCNB HCB aBHC gBHC CIS TRAMS 

CHLOR CHLOR 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

.12 0 ND 0.59 0 2.40 0 0.67 0 5.05 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

3.88 ND 

ND ND 

0.77 D ND 

ND ND 

0.73 0 2.73 

1.41 0 1.83 

0.93 D 2.83 

0.86 0 2.27 

ND ND 

16.8 1.84 

1.73 0 0.21 

0.60 D 0.99 

ND 12.3 

ND ND 

ND 5.03 

1.37 0 2.59 

3.37 2.93 

3.06 ND 

ND ND 

0.59 0 1.16 

ND ND 

ND ND 

10.3 8.65 

0 ND 22.6 

2.53 ND 

0 ND 12.4 

ND 73.9 

0 8.25 102 

0 0.51 0 8.95 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.84 0 15.5 

0.82 0 ND 

ND ND 

ND ND 

ND ND 

0 0.76 0 1.50 

83.3 51.8 

ND 1.34 

70.9 89.9 

2.31 0 ND 

10.1 ND ND 

10.5 196 El88 E 

ND 19.9 21.2 

0 ND 23.6 21.8 

?w 

ND 

147 

0 0180 0 ND 

0 0.77 0 ND 

0 5.02 200 

ND 

ND 

ND 

ND 

3.50 

ND 

8.00 

26.3 

ND 

13.0 

77.4 

86.8 

E 7.03 E 

D 1.25 D 

57.1 

D 0.72 D 

90.8 

ND 

ND 

E 135 

ND 

ND 

E 169 

3001 DE019501 F PF Ualleye 

3001 DE019502 F UB Uhite Sucker 

3022 DA008402 F PF Chain Pickerel 

3022 DA008401 F UB Uhite Sucker 

3023 DA008501 F PF Sm Bass 

3024 DA008601 F PF Lm Bass 

3025 DA008702 F PF Chain Pickerel 

3025 DA008701 F UB Uhite Sucker 

3026 DA009001 F UB Catfish 

3026 DA009002 F PF Lm Bass 

3027 DA000301 F WE Sucker 

3028 DA008801 F PF Chain Pickerel 

3034 DC025702 F PF Lm Bass 

3034 DC025701 F UB Carp 

3035 DC025802 F PF Sm Bass 

3035 DC025801 F UB Carp 

3036 DGO25901 F PF Freshuater Drun 

3036 DC025902 F UB Carp 

3037 DC026002 F PF Black Crappie 

3037 DC026001 F UB Carp 

3038 DC026102 F BF Channel Catfish 

3038 DG026101 F UB Carp 

3039 DC026202 F BF Chaml Catfish 

3039 DGO26201 F UB Carp 

3040 DC026302 F PF Uhite Crappie 

3040 DC026301 F UB Carp 

3041 06026401 F RF Channel Catfish 

3041 06026402 F UB Carp 

3042 DG026501 F UB Carp 

3042 06026502 F PF Northern Pike 

3042 00026SOl L UB Carp 

3043 06026602 F PF Flathead Catfish 

3043 DC026601 F UB Carp 

3044 DC026702 F PF Flathead Catfish 

3044 DC026701 F UB Carp 

3045 06026801 F UB Carp 

3045 06026802 F BF Flathead Catfish 

3046 DC026901 F UB Bigmouth Buffalo 

3047 DC027002 F PF Sm Bass 

3047 DC027001 F UB Carp 

3048 DGO27101 F UB Carp 

3048 06027102 F PF Uhite Bass 

3048 90012689 1 PF Uhite Bass 

3048 GO027101 L H) Carp 

3049 DGO27202 F PF Crappie 

0.54 

0.37 

0.99 

0.28 

0.08 

0.8 

0.21 

0.73 

0.13 

0.08 

0.17 

0.08 

0.19 

ND 

0.09 

0.12 

0.077 

ND 

0.08 

0.05 

0.39 

0.11 

ND 

ND 

L 

0.16 

ND 

0.19 

!D13 

0.24 

0.14 

0.21 

0.09 

ND 

0.13 

2.32 0 2.01 0 3.50 4.74 

ND ND ND 0.76 

ND ND ND 0.66 

ND ND 2.23 0 1.68 

0.17 

D-s-7 
XENOBIOTICS CDNCENTRATIO1IS, rw/g 

Mere 123 124 13s 1234 1235 1245 

P9/9 TCB TCB TCB ICE TCB TCB 

OCS PCB PCNB HCB aBHC gBHC CIS TRAMS 

CHLOR CHLOR 

ND 0.40 0 ND ND ND ND ND ND ND 1.27 0 2.51 2.68 ND 30.2 

ND ND ND No ND ND m ND ND 1.37 0 4.51 3.19 21 .o 18.2 

ND ND ND ND ND ND ND ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND ND ND ND ND m 9.19 15.64 

ND ND ND ND ND ND ND ND ND ND ND ND ND ND 

ND 0.06 

1.73 0 1.05 

ND 1.36 

ND 0.45 

ND ND ND ND 0.13 0 0.42 D ND ND 

ND m ND ND ND 

:“69 :15 

11.5 

8.74 43.1 10.4 llD 75.0 6.16 

9.10 4.53 51.40 ND 43.69 3.23 ND 8.07 

ND 

9.30 

?13 

ND 

ND 

0.37 

ND 

0.51 

0.52 

0.62 

ND 

ND 

1.04 

FL4 

1.48 

ND 

ND 

ND 

0.15 

0 0.63 

0.15 

0 1.11 

0 0.71 

D 0.34 

0.66 

ND 

0 0.60 

?39 

0 0:87 

ND 

0.97 

0 ND ND ND 

OND ND 

D 0.54 0 3.47 :74 

0 0.18 0 5.21 ND 

ND No ND 

DlsD 0.60 D ND 

DND 0.19 0 ND 

0 ND ND ND 

DND ND ND 

DND ND ND 

DWD ND ND 

0 0.45 0 ND ND 

ND ND ND 

ON0 ND ND 

ND 

ES6 0 ND 

ND 

ND 

0.14 0 ND ND 

ND ND ND 

DND ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

m 

ND 

m 

ND 

r56 

ND 

ND 

m 

ND 

ND 

ND 

ND ND 

:24 0: 

:81 0: 

ND ND 

ND ND 

1.99 DllD 

DND ND 

ND ND 

No ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 0.80 D 1.98 DWD 3.12 

0.30 0 ND ND 2.70 3.08 

3.26 1.94 D 0.81 D a.46 6.86 

0.31 D ND ND 2.88 3.30 

6.19 6.63 ND 19.8 19.3 

2.41 0 ND 

ND ND Y.34 

1.75 0 2.64 

ND ND 

7.66 10.1 6.68 8.78 4.00 

ND 3.10 ND 3.51 ND 

ND ND 

?ll 

ND ND 

ND No 1.89 Dm, 

ND 4.71 MD 2.59 No 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

0.27 0 0.25 0 ND ND ND ND ND 

0.69 0 0.43 0 ND ND ND ND ND 

ND No 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND :53 

ND m ND 66.04 101.90 

0.73 D 0.96 0 0.66 0 2.00 0 1.35 0 

0.48 D 0.54 0 0.78 0 2.30 0 1.43 0 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND ND ND ND 0.99 0 ND ND 1.83 0 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND 0.38 0 ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND 4.81 ND ND 0.53 3 0.53 DND 

0.64 0 0.36 DND ND ND ND ND 

0.16 0 ND ND 0.06 DND ND ND 

ND ND 

ND ND 

ND ND 

0.34 0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND ND ND 

ND ND ND ND 

ND 4.04 1.07 DND 

ND 0.31 0 ND ND 

2.10 0 ND 1.59 0 5.19 

2.24 0 2.19 0 2.58 13.2 

ND 3.33 14.4 ND 

ND ND ND ND 

0.12 0 0.58 0 ND 1.70 

ND 

ii.2 

1.62 0 

19.67 

9.74 

31.0 

ND 

0 0.26 0 

Episode SCC Type Description 

0.09 

0.09 

0.12 

ND 

0.24 

0.20 

:23 

0.15 

0.07 

0.00 

0.06 

ND 

MA 

ND 

0.08 

ND 

!!ll 

0.20 

WA 

0.05 

0.06 

0.08 

0.66 

0.49 

0.11 

MA 

0.204 

0.06 

0.07 

0.38 

0.58 

0.09 

0.882 

0.42 

!A26 

0.07 

0.18 

0.06 

0.23 

0.83 

0.68 

3049 DGO27201 F YB Carp 

3050 DGO27301 F m Bigmouth Buffalo 

3060 OF009101 F UB Flatheod Catfish 

3060 OF009102 F UB Sm Buffalo 

3060 GO073189 1 UB Flathead Catfish 

3061 OF019105 F PF Bass 

3061 OF019106 F bl8 Sucker 

3062 OF024024 F UB Blue Catfish 

3063 DFO23301 F UB Sea Catfish 

3063 OF023302 F PF Spotted Seatrout 

3064 OF023306 F PF Spotted Seatrout 

3864 OF023305 II Shellfish 

3065 DFO23419 F BF Bigrwth Buffalo 

3065 DFO23420 F HI Flathead Catfish 

3065 aDOlO F BF Bigmouth Buffalo 

3066 OF023503 F UB Catfish 

3066 OF023504 F PF Freshwater Drun 

3068 DFO24Wl II Oysters 

3068 DFO24~2 F PF Atl. Croaker 

3869 OF024007 F UB Sea Catfish 

3069 OF024008 F PF Trout 

3869 GO051788 F 1111 Sea Catfish 

3078 OF024000 F UB Croaker 

3010 DFO24010 F PF Sheep&cad 

3071 OF024014 F UB Carp 

3071 DFO24015 F PF Longnose Gar 

3072 DFO24016 F PF Uhite Bass 

3072 OF024017 F UB Carp 

3072 PO070688 L UB Carp 

3073 DF019222 F PF Sn Bass 

3073 OF019221 F UB Uhite Sucker 

3074 OF026017 F PF Brown Trout 

3075 OF024102 F RF Hardread Catfish 

3076 OF028503 F PF Spotted Bass 

3076 OF028502 F UB Channel Catfish 

3077 OF019113 F PF Flathead Catfish 

3077 OF019114 F UB Redhorse Sucker 

3078 OF009118 F UB Carp 

3078 DF023815 F UB Sm &tffalo 

3078 OF023816 F PF Black Cramie 

3079 DF019205 F PF Uhite Bask 

3079 OF019206 F UB Carp 

3080 OF023317 F VB Carp 

3080 OF023318 F PF 11 Bass 

3081 OF024105 F PF Uhite Bass 
XENOBIOTICS CONCENTRATIONS, @w/g 

Uerc 123 124 135 1234 1235 1245 OCS 

NW3 TCB TCB TCB TCB TCB TCB 

Episode SCC Type Description PCB 

3081 DFO241Ob F UB Catfish 

3082 DF023402 F PF lm Bass 

3082 DFO23401 F b/B Carp 

3083 DFO23405 F UB Black Bullhead 

3083 DF0234Ob F PF Lm Bass 

3084 DF024109 F UB Channel Catfish 

3085 DFO24113 F UB Sea Catfish 

3085 DFO24114 F PF Black Drus 

3086 OF023411 F PF Black Drus 

30% DF0234W F UB Catfish 

3086 DF023410 F PF Red Drus 

3087 DFO234lb F hQ Lm Bass 

3087 DF023413 F UB Car-n 

3087 OF023414 F PF Uhite Crappie 

3087 DF023415 F UP Bluegill 

3088 DF023417 F UB Channel Catfish 

3088 DF023418 F PF B&gilt 

3089 OF019209 F PF Uhite Crappie 

3089 DFO19210 F UB Carp 

3090 DF019213 F PF (rhite Crappie 

3090 DF019214 F UB Channel Catfish 

3091 OF019218 F PF Uhite Crappie 

3091 OF019217 F UB River Carpsucker 

SW2 DF023501 F UB Carp 

3092 DF023502 F PF Vermouth 

3093 DF024011 F PF l.n Bass 

3093 DF024118 F UB Sm Buffato 

3094 DC017201 F BF Channel Catfish 

3095 DC038801 F BF Broun Bullhead 

3095 DC038802 F UB Charnel Catfish 

30% DC035001 F BF Brow Bullhead 

3096 DC035002 F UB Channel Catfish 

3097 DC038701 F BF Broun Bullhead 

3097 DC038702 F UB Carp 

3097 DDO71989 L PF Brown Bullhead 

3098 DC038601 F UB Uhite Sucker 

3098 DC038602 F PF American Eel 

3098 QoO51288 F UB Uhite Sucker 

3100 DC019701 F PF Uhite Perch 

3101 DC019901 F PF Brown Trout 

3103 DCOM201 F UB Charnel Catfish 

3103 DCO3b202 F UB Carp 

3104 DC020001 F PF Lm Bass 

3104 DC020002 F UB Carp 

3105 DF025001 F UB Carp 

0.10 

ND 

ND 

ND 

0.313 

0.10 

0.12 

0.05 

0.08 

0.31 

0.32 

0.09 

?.07 

0.03 

0.05 

0.18 

ND 

ND 

ND 

ND 

0.06 

i!2b 

0.28 

0.816 

0.207 

0.15 

0.06 

0.08 

0.06 

0.11 

0.16 

0.07 

0.08 

0.19 

WA 

ND 

ND 

0.05 

ND 

0.15 

ND 

0.08 

0.23 D 0.22 D ND 

ND ND ND 

0.32 D 0.30 D ND 

ND ND ND 

ND 

ND r91 D !: 

ND ND ND 

ND ND MD 

0.57 D 0.49 D ND 

ND ND ND 

0.55 D 0.46 D ND 

:2b D: 

ND 

ND 

ND 0.11 D ND 

0.43 D 0.30 D ND 

0.33 D 0.21 D ND 

0.35 D 0.21 D ND 

NO 0.31 D :78 D 1: 

0.53 D 0.29 D ND 

0.18 D 0.14 D ND 

!Lb 

0.08 D ND 

3.30 ND 

0.51 D 0.44 D ND 

ND 0.55 D ND 

1.35 D 1.11 D 0.08 

1.47 D 1.43 D ND 

ND ND ND 

ND ND 

54.89 103.82 :48 

!Dl3 

ND NO 

5.15 0.12 

ND ND ND 

0.99 D 0.78 D ND 

0.51 D 0.79 D ND 

ND ND ND 

ND ND ND 

0.89 D 0.98 D ND 

1.31 D 1.23 D ND 

ND ND ND 

0.07 D NO ND ND 

ND ND ND ND 

ND ND ND ND 

ND 

746 

ND ND 

ND 3.46 65.3 

ND 1:OS D 1.08 D ND 

2.18 D 3.17 3.17 138 

6.35 10.7 10.7 ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND 0.16 D 0.16 D ND 

ND ND ND ND 

ND 0.27 D 0.27 D 0.74 

0.05 D ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

0.6’ D ND ND ND 

10.4 4.25 4.25 ND 

1.82 D 1.44 D 1.44 D ND 

3.50 1.64 D 1.64 D ND 

D 1.16 D 1.29 D 1.29 D ND 

10.6 6.18 6.18 ND 

20.92 4.21 4.21 ND 

6.34 0.79 D 0.79 D ND 

D 76.65 28.30 28.30 ND 

ND ND ND ND 

D 2.22 D 1.23 D 1.23 D ND 

ND ND ND ND 

ND ND ND ND 

0.28 D ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

PCNB 

0.06 D ND ND 0.83 D ND ND ND 

ND ND 

ND ND 

ND ND 

42.6 MO 

11.02 ND 

1.54 D 7.56 NO ND 

ND 0.43 D ND 

ND 2.27 D 9.57 ii.6 

7.85 

913 E ND ND ND 

50.74 ND ND ND 

g.8 

ND 

ND 

El25 END 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D 0.57 D ND 

:32 0: 

ND ND 

ND ND 

ND ND 

7.76 NO 

1.71 D ND 

5.41 ND 

1.19 D ND 

9.47 ND 

30.49 ND 

46.3 ND 

M-17 ND 

ND ND 

1.30 0 ND 

ND ND 

0.53 D ND 

0.35 D ND 

ND ND 

ND ND 

ND ND 

1.26 D ND 

ND ND 

HCB aBHC gBHC CIS TRANS 

CHloR CHLcm 

202 E 4.23 lb4 D 6.62 ND 

18.1 0.74 D 0.29 D ND ND 

ND 2.83 

: 

ND 

ND 0.93 28D 1.54 D : 

ND 17.8 ND ND 

ND ND ND ND 

&4 D &O D :49 D :02 

4.38 

ND 

ND 

ND 

ND 

ND 

2.73 

ND 

1.35 D 

:17 

D 

?40 0.90 D 0.44 D 

D 19.3 11.2 

ND 0.63 D 0.42 D 0.62 D ND 

ND 1.65 D BD ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

0.25 D 0.65 D BD 1.b8 D 0.93 D 

5.38 2.78 1.68 D 92.8 E 58.1 

ND ND 2.09 D 23.1 17.2 

ND ND ND 

ND 0.64 D ND 

P57 

12.5 

15.3.10 D 4.86 ND 

1.97 D :41 D : 

ND ND ND 

0.77 D ND 38.8 

Y74 

0:31 

44.4.27 ND 2.85 

D ND ND 

2.11 D ND 

ND ND g-6 

ND 1.58 D ND 

ND ND 5.01 

ND ND ND 

78.4 53.1 

5.80 7.61 

97.7 62.2 

3.76 5.81 

7.80 ND 

2.44 D 3.81 

ND ND 

1.95 D 7.12 

ND ND 

4.52 13.08 

0.22 D 2.63 

26.25 51.05 

ND 15.9 

1.80 D 4.75 

56.9 45.4 

6.22 E 3.33 E 

D-s-9 
XENOBIOTICS COUCENTRAllONS, rig/g 

Episode SCC Type Description 

3105 OF025002 F PF Lm Bass 

3106 DE026801 F PF Walleve 

3107 DE026901 F UB Carp ’ 

3108 DE027001 F PF Walleye 

3108 DE027002 F UB Carp 

3109 DE025001 F bi8 Carp 

3110 DE022501 F BF Carp 

3111 DH015801 F PF balleye 

3111 DH015802 F UB Silver Redhorse 

3112 DE022401 F UB Carp 

3112 DE022402 F PF Ualieye 

3113 DE021101 F BF Channel Catfish 

3113 DE021102 F BF Carp 

3113 00030789 F BF Charnel Catfish 

3114 DE021201 F BF Carp 

3115 DE021301 F UB Carp 

3115 DE021302 F BF Catfish 

3115 00101689 1 UB Carp 

3117 DE021501 F PF Lake Trout 

3118 DE021601 F PF Ualleye 

3118 DE021602 F UB Carp 

3118 DE021603 F UB Carp 

3118 ODO10689 L W Carp 

3118 00020488 1 PF Walleye 

3119 DE021702 F PF lm Bais 

3119 DE021701 F UB Cam 

3120 DE021801 F UB Car; 

3120 DE021802 F PF Bass 

3122 OEO22004 F PF Sm Bass 

3122 DE022001 F UB Carp 

3122 DE022003 F UB Redhorse Sucker 

3125 DE022301 F UB Carp 

3125 DE022302 F PF White Bass 

3132 DE023201 F UB Carp 

3132 90010588 L UB Carp 

3134 06023403 F UB Carp 

3134 OE023405 F UB Carp 

3134 DE023406 F UB Sucker 

3135 OE023501 F UB Carp 

3136 OE0236Ol F PF Northern Pike 

3137 DE023701 F UB Redhorse Sucker 

3138 DE023801 F UB Carp 

3140 DE024001 F PF Ualieye 

3140 DE024002 F UB Csrrr 

3141 DE024101 F PF Nor’thern Pike 

Mere 123 124 135 1234 1235 1245 

CO/B TCB TCB TCB TCB TCB TCB 

0.134 

0.57 

0.16 

0.25 

0.30 

0.23 

0.11 

0.91 

0.14 

0.179 

0.47 

0.08 

0.08 

ND ND ND 

0.57 D 0.42 D ND 

ND 0.07 D ND 

0.18 D 0.13 D ND 

!!44 D ii 

ND 

ND 

NO NO ND 

ND w 

ND ND 

0.10 D ND 

ND ND 

0.11 D ND 

NO ND 

ND ND 

ND ND ND 

ND ND ND 

NO ND NO 

ND ND ND 

ND ND ND 

NO ND MD 

ND ND ND 

ND 

ND :“28 

0.07 

0.05 

0.09 

0.22 

0.56 

0.15 

0.24 

WA 

0.28 

0.33 

0.17 

0.30 

0.56 

1.40 

0.61 

0.11 

0.48 

0.22 

!“W 

0.03 

0.05 

0.09 

0.24 

0.13 

0.21 

0.09 

0.04 

0.17 

ND 

ND 

NO 

ND 

ND 

ND 

2.48 

ND 

6.94 

ND 

1.77 

ND 

ND 

ND 

0.50 D ND 

D 0.63 D ND 

ND ND 

ND ND 

ND ND 

0.50 D ND 

0.24 D NO 

2.43 D ND 

D 4.98 0.57 

1.06 D ND 

4.51 NO 

ND ND 

D ND ND 

ND ND 

ND ND 

ND ND 

0.03 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND ND 

D 0.28 D ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND 0.20 D ND ND ND ND ND ND 

0.22 D 0.13 D ND 0.06 0 ND ND ND ND 

ND ND ND 

0.16 D 0.19 D ND 

ND ND ND 

0.51 D 0.26 D ND 

1.47 D 8.41 ND 

2.05 D 11.94 ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND 

ND 1; ND 

ND ND ND 

ND ND ND 

ND 0.59 D ND 

ND NO 

ND ND 

ND ND 

ND 

0.74 D :: 

0.78 0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.04 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND MD 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

OCS PCB 

ND 

ND 

ND 

ND 

0.87 

0.91 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.54 D ND 

PCNB HCB aBHC gBHC CIS TRANS 

CHLOR CHLOR 

UD ND ND ND ND ND 

ND ND ND ND ND ND 

ND 0.77 D 1.81 D ND ND ND 

ND ND ND ND ND ND 

ND ND 1.77 D ND 2.03 D ND 

MD ND UD ND 5.81 3.87 

ND MD 1.08 D ND 4.42 2.09 D 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 10.6 7.59 7.53 5.24 

1.63 D 2.77 ND 3.35 1.17 D 

ND ND ND ND ND 

1.57 D 0.79 D 1.39 D 12.1 7.44 

1.88 D ND 2.17 D 23.7 14.4 

1.21 D 0.50 D 1.35 D 12.8 7.86 

0.75 D 1.45 D 1.71 D 31.3 33.5 

3.82 ND ND 31.0 36.4 

ND ND ND 39.4 

Y22 0.76 5.48 D ND 2: 154 51.8 341

0.10 D ND ND 6.74 1.71 D 

ND ND ND 18.8 5.80 

0.74 D 0.39 D ND 3.88 1.41 D 

r24 D !!I8 0: 7.73 19.6 6.29 187 D 

ND ND ND ND 10.40 6.06 

ND 0.15 D 0.42 D 0.48 D 2.99 0.86 D 

NO 

NO 

ND 

ND 

D ND 

D 13.85 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

MD 

ND 8.31 UO 35.2 18.4 

ND 1.55 D 0.69 D ND ND 

2.64 6.56 5.68 ND ND 

ND 0.34 D 0.61 D 2.21 D 0.50 D 

ND ND 12.40 53.84 41.20 

ND ND ND 67.69 46.00 

0.73 D 1.15 D 1.17 D 3.15 2.55 

ND 1.20 D ND 5.86 7.30 

ND ND ND ND ND 

0.92 D 1.46 D 1.58 D 4.73 2.74 

ND ND w ND ND 

ND 2.22 DND ND ND 

1.44 D ND ND 12.5 7.59 

ND ND ND 1.93 D 0.72 D 

0.49 D ND ND 3.63 2.32 D 

ND 3.31 ND 22.2 6.93 
XENOBIOTICS CONCENTRATIONS, n-g/g 

Mere 123 124 135 1234 1235 1245 ocs 

cm TCB TCB TCB TCB TC8 TCB 

PCB PCNB HCB 

0.78 D ND 

ND ND 

ND ND 

ND ND 

0.28 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.81 D NO 

ND ND 

ND ND 

NO NO 

NO ND 

ND nD 

NO ND 

ND ND 

0.52 D ND 

1.45 D ND 

ND ND 

MD ND 

2.77 ND 

4.69 

ND 

ND 

ND 

0.81 

ND 

0.57 

1.21 

L4 

3.19 

ND 

0.23 

ND 

ND 

ND 

ND 

0.64 

g.2 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.56 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

Pa4 

0189 

ND ND ND 4.83 

ND ND ND 4.40 

0.09 D ND 

0.09 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

gBHC CIS TRANS 

CHLOR CHlOR 

6.28 56.5 

D ND 10.3 

ND 67.8 

ND ND 

D ND 6.92 

ND 6.88 

D1.82 DND 

D ND ND 

:40 42.6 ND 

1.71 D ND 

ND 7.37 

D 6.40 10.0 

6.34 13.0 

D 6.50 14.3 

D 1.56 D 7.19 

3.98 

D ND ii.03 

1.40 D 155 

D ND 1.96 

D 0.66 D 0.58 

30.9 

2.79 

38.7 

!:52 

4.23 

ND 

ND 

ND 

28.9 

ND 

2.12 D 

3.64 

6.12 

6.62 

2.92 

ii.15 

82.7 

D 0.76 D 

D ND 

ND ND 

ND ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

D ND ND 

ND ND 

ND 

ND 

ND 

1.43 D 

ND 

ND ND 

MD 

1.15 D El8 

ND ND 

3.27 9.70 

ND 3.38 

ND 

2.01 D 

0.63 D 

0.49 D 

5.11 

ND 

4.53 

1.29 D 

Episode SCC Type Description 

0.02 

0.14 

0.04 

0.01 

0.05 

0.20 

0.22 

0.16 

0.28 

0.05 

0.08 

0.82 

0.14 

0.158 

!“22 

0.06 

0.12 

0.05 

0.05 

ND 

0.665 

0.18 

0.43 

0.25 

0.87 

0.29 

0.33 

0.08 

::19 

0.37 

0.4 

0.16 

0.82 

0.15 

0.72 

0.15 

ND 

0.11 

0.31 

0.06 

0.29 

0.05 

ND 

WD 

7.46 

3.78 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.20 

!!53 

ND 

ND 

ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

4.71 ND ND MD ND ND 

2.32 D ND ND ND ND ND 

ND ND ND ND ND ND 

ND 0.26 D NO 0.39 0 0.39 D ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND NO ND ND ND ND 

0.55 D ND ND 

ND ND 0.37 D :: 

ND ND 

ND ND 

ND ND NO ND ND ND 

ND ND ND ND ND ND 

ND MD ND ND ND ND 

ND ND ND ND ND ND 

D ND ND ND ND ND ND 

ND ND ND ND ND ND 

D 0.55 D ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND 33.4 

ND ND ND ND ND ND 

30.2 23.3 

4.90 8.52 

ND 

::: 

MD 

D 1.33 

ND 

D 1.95 

D 0.85 

:98 

3.29 

ND 

D 0.26 

ND 

::c”l 

ND 

D 0.59 

4.64 

0.45 

0.25 

3141 DE024102 F UB Carp 

3141 DE024103 F PF Nor’thern Pike 

3142 DE022502 F UB CarD 

3143 DE024401 F Rotien (catf) 

3143 DE024403 F UB Carp 

3144 DE024901 F UB Carp 

3145 DE026601 F UB N. Redhorse 

3146 DE026701 F UB Carp 

3146 DE026702 F PF Ualieye 

3147 DC035201 F UB Care 

3148 DE027101 F UB Carp 

3148 DE027103 F PF Walleye 

3149 DC038501 F UB Uhite Sucker 

3150 DA008901 F IJB Uhite Sucker 

3150 QD120187 1 UB Uhite Sucker 

3151 DA000101 F UB Nhite Sucker 

3252 DAOW201 F IJB Uhite Sucker 

3161 DC019801 F BF Black BulLhead 

3161 DC019802 F UB Uhite Sucker 

3162 DJO24001 F UP Starry Flounder 

3163 DJO24002 F UP Starry Flouder 

3166 DDO15701 F PF Lm Bass 

3166 DDO15702 F UB Carp 

3165 00015703 F PF La bass 

3165 DDO15704 F UB Redhorse Sucker 

3166 DD015705 F PF Ualleye 

31&b DDO157Db F UB White Sucker 

3167 DD015707 F PF Lm Bass 

3167 DO015708 F UP Bluegi II 

3167 CtOOb2388 1 UP Bluegill 

3168 DDO15711 F UB Carp 

3168 DDO15712 F PF Lm Bass 

3169 DDO15714 F PF Lm Bass 

3169 DDOl5713 F UB Black Rcdhorse 

3169 BDO22789 1 UB Black Redhorse 

3170 DO015716 F PF Lm Bass 

3170 DD015715 F UB Spotted Sucker 

3171 DDO15718 F PF Lm Bass 

3171 DDO15717 F UB Spotted Sucker 

3172 DDO15719 F MB Carp 

3172 00015720 F PF Lm bass 

3173 DD015721 F PF Lm Bass 

3173 00015722 F UB Channel Catfish 

3174 DD015723 F PF Lm Bass 

3174 00015724 F UB Channel Catfish 

ND 6.29 3.12 3.12 ND 

0.14 D 1.10 D ND ND ND ND 

0.24 D 0.25 D ND 0.23 D 0.13 D 0.13 D ND 

ND 

ND 

1.86 

DND 

ND ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

MD ND HD HD ND ND ND 

0.22 D ND ND ND ND ND ND 

ND ND ND ND ND ND ND 

ND ND NO ND ND ND ND 

ND 0.12 D ND ND ND ND ND 

ND 0.09 D ND 

ND 0.69 D ND 

ND ND NO 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND 1.26 D 1.26 D ND 

ND ND ND ND 

MD 0.42 D ND 

ND ND ND 

L?-s-11 
XENOBIOTICS COUCENTRATIONS, rig/g 

OCS PCB PCNB HCB aBHC 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

0.32 D ND 

ND ND 

3.25 3.69 

ND ND 

0.891 D ND 

9.30 7.83 

0.28 D ND 

ND ND 

6.57 ND 

ND ND 

ND ND 

ND 5.68 

ND ND 

ND 3.58 

ND 4.11 

CIS TRAYS 

CHLUt CHLOR 

1.48 DND ND 

ND 

ND 

ND 

:“32 

5.25 

1.06 D 

4.18 

4.12 

ND ND ND 

ND 8.13 6.73 

ND ND ND 

!D33 

14.6 

ND 

ND 

59.8 

D ND 

41.5 

52.3 

1.75 

ND ND 

38.5 

ND 

35.0 

40.3 

D 0.47 D 

ND 

8.02 38.8 30.6 

ND ND ND 

ND ND ND 

ND 60.1 58.4 

ND ND ND 

3.88 25.9 18.6 

4.67 31.8 23.7 

D ND 25.2 14.4 

DND ND ND 

ND ND ND 

1.46 D ND ND 

ND ND w 

ND 

DND 

ND 

1.56 

4.23 

11.1 

18.2 

DND 

D ND ND ND ND ND 1.21 D ND 16.3 12.0 ND 

D 0.06 D ND ND ND ND ND ND 0.52 D 0.93 D 0.45 

19.8 

14.0 

30.1 

D 1.25 

28.8 

D ND 

20.4 

ND 

Episode SCC Type Description Mere 123 124 135 1234 1235 1245 

l&v0 TCB TCB TCB TCB TCB TCB 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.58 D 0.65 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D 0.65 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

110 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3175 WO15802 F PF Lm Bass 

3175 DDO15801 F VB Charnel Catfish 

3176 WO15804 F PF ln Bass 

3176 Do015803 F UB Spotted Sucker 

3177 WO15805 F m Carp 

3177 00100488 1 UB Carp 

3178 Do015808 F PF Redeye Bass 

3178 DO015807 F UB North Hogsucker 

3179 WO15810 F PF ln Bass 

3179 DOD15809 F UB Golden Redhorse 

3180 WO15812 F PF Lm Bass 

3181 WO15813 F PF Lm Bass 

3181 00015814 F UB Carp 

3182 WOlMlS F PF Rock Bass 

3182 Do015816 F UB Carp 

3183 DOD15817 F UB Carp 

3183 00015818 F PF Sauger 

3184 WD15819 F UB Carp 

3184 WO15820 F PF Uhite Creie 

3185 DOD15822 F PF lm Bass 

3185 Do015821 F UB Chamel Catfish 

3186 00015824 F W Southern Flouder 

3187 Do015902 F UP Suncr Flomder 

3188 Do015903 F UB Carp 

3188 WO15904 F PF ln Bass 

3189 WO159Ob F PF LR Bass 

3189 00015905 F UB Carp 

3189 POW2188 1 UB Carp 

3190 WO15908 F PF la bass 

3190 Do015907 F UB Cam 

3191 DJ024003 F UP Striry Flounder 

3191 05024005 M Soft Shell Cluns 

3192 DJO24007 F UP Starry FLomder 

3192 DJO24009 M Soft Shell Clams 

3193 DC039002 F PF Sm Bass 

3193 DC039001 F PF Striped Bass 

31% DHD20104 F UB Carp 

31% DHO20105 F UB Chlrb 

31% DHO20107 F PF Brow Trout 

31% DH020108 F UB Sucker 

3197 DHD20110 F UB Sucker 

3197 DHOZOlW F PF Rainbow Trout 

31% OH020111 F UB Sucker 

3199 DHD20102 F PF Walleye 

3199 OH020101 F UB Carp 

0.4 

0.18 

0.13 

:03 

WA 

0.55 

0.23 

0.44 

0.24 

0.43 

0.28 

X:E 

0.04 

ND 

0.30 

0.14 

0.31 

0.67 

0.12 

0.05 

ND 

0.03 

0.14 

0.26 

0.06 

WA 

0.05 

0.05 

0.01 

0.01 

0.01 

0.01 

0.4 

0.35 

0.08 

0.14 

0.182 

0.182 

0.06 

ND 

0.12 

0.37 

0.09 

ND ND ND ND ND ND 

ND ND NO 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

D 1.90 D 1.02 D ND 

ND ND ND 

ND ND ND 

ND 0.73 D ND 

ND ND ND 

ND ND ND 

ND 5.73 ND 

ND ND ND 

ND ND ND 

ND 0.629 ND 

ND ND ND 

ND ND ND 

ND ND 

0.48 D ND ND 

ND NO ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND 0.54 D ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

0.39 D 0.27 D ND 

1.03 D 2.25 D ND 

ND ND ND 

ND ND ND 

ND ND NO 

ND ND ND 

ND ND ND 

ND ND 

ND ND 

ND ND 

1.67 1.43 

0.16 D ND 

ND ND 

ND ND 

ND 

D 0.07 

ND 

D 0.08 

ND 

ND 

ND 

ND 

0.486 ND ND 

0.09 D ND ND 

1.20 D ND ND 

0.20 D ND ND 

0.92 D ND ND 

D ND 0.06 D ND 

ND ND ND 

D ND 0.06 D ND 

ND ND ND 

0.33 D 0.51 

ND 0.25 

ND ND 

ND ND 

ND ND 

0.32 D ND 

ND 2.29 

ND ND 

ND ND 

ND 

0.09 

:05 

ND 

1.71 D 2.46 D ND ND ND 

ND 0.83 DNO ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND 2.00 

ND 0.17 
XENOBIOTICS CONCENTRATIONS, rig/g 

Episode SCC Type Description 

3199 DH020103 F UB Carp 

3200 DHO20112 F UB Sucker 

3203 DJ024018 F UB Carp 

3205 DJ024023 F PF Cutthroat Trout 

3205 05024024 M Crayfish (uhole) 

3206 DJ024103 F IJB Sucker 

3208 DJO241W F UB Sucker 

3212 05024120 F BF Catfish 

3212 DJO24121 F UB Carp 

3213 DJ024123 F UB Squawfish 

3215 DJ023705 F UB Sucker 

3216 DJ023707 F PF wufish 

3216 DJ023708 F b/B Sucker 

3216 a0022388 1 UB Sucker 

3217 05023709 F PF Whitefish 

3217 DJ023710 F UB Sucker 

3218 DJO23712 F UB Sucker 

3218 DJO23711 F PF Squawfish 

3219 DJD23713 F UB Uhite Sturgeon 

3219 DJ023714 F PF Llhite Sturgeon 

3220 DJO23W2 F PF Squawfish - 

3220 DJO23W3 F NB BridQeliD Sucker 

3221 DJO23904 F BF ChAl iatfish 

3221 DJ023905 F UB Sucker 

3222 DJ023906 F PF Squawfish 

3222 DJD23W7 F UB Sucker 

3223 05023717 F UP Starry Flounder 

3224 DJO23715 M Soft Shell Clms 

3226 DJ023721 H Pacific Ovsters 

3227 DJ023723 H Pacific O;Sters 

3231 05023910 F PF Sm Bass 

3231 DJD23911 F UB Carp 

3234 DH020302 F PF lake Uhitefish 

3234 OH020301 F UP Squawf ish 

3235 DHD20304 F PF Brown Trout 

3235 DH020303 F UB Uhite Sucker 

3236 OH020306 F PF Brown Trout 

3236 DH020305 F UB Largescale Sucker 

3237 DH020307 F PF Rainbow Trout 

3237 OH020308 F bJ8 largescale Sucker 

3237 MM80988 F UB Laraescatc Sucker 

3238 DJ023918 F UP Dolly Varden 

3241 DJ023923 F PF Rainbow Trout 

3241 05023924 F UP Dolly Varden 

3244 DJD23622 F UB Coast Sculpin 

Here 123 124 135 1234 1235 1245 OCS 

ash TCB TCB TCB TCB TCB TCB 

0.06 

0.11 

0.10. 

0.07 

ND 

ND 

0.13 

0.21 

0.22 

0.11 

0.18 

0.33 

0.05 

NA 

00:07 

0.09 

0.36 

0.10 

0.09 

0.23 

0.05 

0.34 

0.08 

0.74 

ND 

0.058 

0.06 

ND 

:24 

0.20 

0.08 

0.14 

oo:Jb 

0.1 

0.08 

0.08 

0.14 

WA 

0.05 

0.06 

0.05 

ND 

2.40 D 1.39 D ND ND 

0.34 D 0.32 D 0.24 D ND 

ND 0.72 D ND ND 

ND ND ND 

ND ND ND 

ND 0.38 D ND 

ND ND ND 

ND 

4.78 ::lb 

ND 

D 0.43 

7.05 6.26 ND 

ND ND ND 

0.24 D ND ND 

ND 0.48 D NO 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

0.12 D 0.17 D ND ND 

ND ND ND 

ND 0.12 D ND 

ND ND ND 

ND 

ND 

ND 

ND ND ND 

0.43 D ND ND 

ND No ND 

ND ND ND 

ND ND ND 

0.32 D 0.23 D ND 

ND NO ND 

0.20 D 0.14 0 ND 

0.31 D 0.55 D ND 

ND 

ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND NO ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

1.61 D 1.61 D ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND 1.02 D 1.02 D ND ND ND 

ND ND ND ND 

ND ND ND 

ND ND ND 

ND 

ND ND ND 

w ND ND 

ND ND ND 

ND ND ND 

ND 

ND 

ND 

No 

ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

PCB PCNB HCB aBHC gBHC 

ND ND 

0.60 DND 

0.54 D ND 

ND 9.33 8.64 

ND 13.7 ND 

DND 9.68 6.70 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO ND 

18.6 ND ND 

ND 7.03 2.45 D 

ND 3.59 2.48 D 

ND 13.7 7.36 

ND ND ND 

9.34 18.1 6.53 

ND 0.17 DND 

ND ND ND 

ND NO ND 

ND ND ND ND ND 

ND ND 

ND ND 

ND ND 

ND 0.73 DND 

ND 10.8 9.18 

ND 0.80 D 0.72 D 

ND ND ND ND ND 

ND ND 6.05 

ND ND ND 

ND ND ND 

ND ND ND 

DND ND ND 

ND ND ND 

ND ND ND 

D ND 12.3 7.27 

ND ND D ND 

ND ND 2.88 

ND ND 

ND ND 

6.88 ND 

2.12 D 1.11 

ND ND 

ND 7.17 

4.98 ND 

2.24 D ND 

15.6 ND 

ND ND 

ND ND 

ND 

ND !?74 

ND 5.48 

ND 4.03 

:32 ND 

ND ND 

ND ND 

10.6 4.119 

1.49 D ND 

ND m 

ND 

ND 735 

ND wo 

ND ND 

4.55 1.89 

0.40 D 0.91 

0.77 D 2.78 

0.67 D ND 

ND 

0.65 D MD 

1.07 D Wo 

1.47 D ND 

2.57 ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

3.35 ND 

3.88 ND 

ND ND 

ND ND 1.81 

CIS TRANS 

CHLOR CHLDR 

10.4 4.68 

0.67 

0.58 

D ND 

D ND 

ND 

ND 

No 

ND 

DND 
XENOBIOTICS CONCENTRATIOWS, rig/g 

ocs PCB PCNB HCB aBHC 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 7.48 ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND 0.74 D ND ND 

2.24 D ND ND 2.61 1.98 D 

ND 

?82 ND 

ND NO 

3.54 :42 ND 

NO 

::3b ND 

ND ND 

ND 7.24 E7 

3.28 0.70 D 0.75 D 2.43 D 0.87 D 

ND 17.48 2.67 10.76 20.85 

ND 7.88 5.66 5.19 2.45 D 

1.80 D ND ND 13.9 8.82 

ND ND ND ND NO 

ND ND ND ND ND 

1.03 D 2.54 1.88 D NO ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND 

:70 ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND ND ND ND ND 

ND ND ND 0.23 D ND 

ND 2.48 D 3.98 ND ND 

NO ND 4.06 ND ND 

ND ND ND ND ND 

4.82 8.43 7.78 21.9 4.62 

1.89 D ND 0.84 D ND ND 

ND ND ND ND ND 

ND ND ND 

ND ND ND 

0.60 D ND ND 

ND ND ND 

0.56 D ND ND 

0.93 D 0.75 D ND 

ND 5.01 ND 

ND ND ND 

ND ND ND ND ND 

0.15 D 1.33 D 0.39 D ND ND 

0.55 D ND ND 4.97 1.25 D 

0.23 D ND ND 6.06 3.73 

2.02 D ND ND 10.1 6.56 

6.83 23.82.91 :“82 2.01 ND D 7.99 10.33:: 

ND ND 97.2 E 67.6 

1234 

TCB 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.01 

D ND 

ND 

ND 

ND 

ND 

ND 

1235 

TCB 

ND 

ND 

!DW 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1245 

TCB 

ND 

ND 

ND 

D 0-W 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

Mere 123 124 135 

L9/9 TCB TCB TCB 

gBHC CIS TRANS 

CHLOR CHLOR 

Episode SCC Type Description 

ND 

0.04 

0.16 

NA 

0.08 

0.21 

0.11 

0.09 

0.29 

0.10 

WA 

0.21 

ND 

0.05 

0.21 

1.66 

0.29 

0.05 

0.05 

ND 

0.07 

0.33 

0.21 

ND 

ND 

0.81 

0.06 

0.18 

0.89 

0.13 

0.10 

0.03 

ND 

0.21 

ND 

0.06 

0.42 

0.24 

ND 

0.03 

ND 

0.09 

0.08 

3245 DJO23624 F UP Flathead Sole 

3246 DJ0221W F UP Flathead Sole 

3248 DJ022502 F UB Coqwsite Bottom 

3248 ODO50588 F UB not available 

3249 05022503 F PF Brook Trout 

3249 DJ022504 F UB Sucker 

3250 DJ022505 F PF Pink Salmon 

3250 DJO225Ob F UB Sucker 

3252 05022509 F PF lm Bass 

3252 DJ022SlO F UB Sucker 

3252 00020989 1 PF Lm Bass 

3252 GO052588 L UB Sucker 

3256 DJ022518 F UB Sucker 

3258 DC038901 F PF Spot 

3258 DC038902 F UB Croaker 

3259 DB000466 F UB Goldfish 

3259 06000473 F PF Lm Bass 

3259 DBO69101 F UB Sucker 

3260 De000493 F b/B Carp 

3261 DYO2bDOl F PF Giant Kingfish 

3261 DYO26002 F UB Striped Hullet 

3262 DYO26004 F tJB Tilepie Tilapia 

3266 01022701 F PF BLack Crappie 

3266 DY022702 F VB Channel Cbifish 

32&b CRY012389 1 PF Black Crappie 

3267 DYO22101 F PF Rainbow Trout 

3267 DYO22102 F t/B Sacramento Sucker 

3270 DY022107 F PF Squaufish 

3270 OYO22108 F LJB Sucker 

3271 DY022110 F UB Sucker 

3272 DYO22111 F PF Leopard Shark 

3272 0’1022112 F VB Uhite Surfperch 

3273 DY022113 F UB Sculpin 

3273 DYO22114 F UB Surf Smelt 

3274 OYO22115 F PF Rainbou Trout 

3274 DY022116 F UB Sculpin 

3275 01022118 F IJB Sucker 

3276 DYO22119 F UB Ualleve 

3278 DY022123 F PF Green’Sunfish 

3278 DY022124 F UB Sacramento Sucker 

3281 01022205 F UB Sucker 

3282 DY0222Ob F PF Flathead Catfish 

3282 DYO22207 F Ml Carp 

3283 DY0222W F tJB Carp 

3285 DY022212 F UP Stingray 

0.27 D ND ND 

ND ND ND 

ND 0.40 D ND 

ND 0.15 D ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND NO ND 

ND ND ND 

ND ND ND 

0.51 D 0.62 D ND 

ND ND ND 

ND 44.5 32.1 

ND 1.08 D ND 

ND ND ND 

ND 11.1 ND 

ND 

ND 

ND 

ND 

ND 

::19 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.67 D ND ND 

ND 0.09 D ND 

ND 

ND 

ND 

!“l& 

ND 

ND 

0 ND 

ND 

0.29 D ND ND 

1.02 D 0.72 D 0.08 

ND 

ND 

0.38 

ND 

ND 

ND 

NO 

D 0.26 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

4.77 2.99 0.46 D ND 

D-5-14 
XENOBIOTICS CONCENTRATIONS, rig/g 

Mere 123 124 135 1234 1235 1245 OCS 

P9/9 TCB TCB TCB TCB TCB TCB 

PCB PCNB HCE aBHC gBHC CIS TRANS 

CHLOR CHLOR 

Episode SCC Type Description 

3285 DY022213 F UB Diatmd Turbot 

3286 DY022215 F UB Carp 

3287 Or022216 F UB Tilapia Zilli 

3288 DY022217 F PF Squawfish 

3288 DY022218 F btB Sucker 

3289 01022219 F VP Bocaccio 

3289 DYO22220 F UB Sculpin 

3290 DYO22221 F PF Redear Smfish 

3290 DYO22222 F UB Blackfish 

3294 DJO22112 F PF Atlantic Salmon 

3294 DJ022111 F UP True Cod 

3294 05022113 M Mussel 

3295 05022114 F UP Atlantic Salmon 

3296 DBO40101 F UB Uhitc Sucker 

3297 DBO41501 F W Carp 

3298 DBO41bOl F IJB Carp 

3298 DBO4lbO4 F PF lm Bass 

3299 DBO4ObOl F UB Uhi te Sucker 

329V DBO40604 F PF Lm Bass 

3299 MI40601 1 W Sucker 

3300 DE040201 F UB Uhite Sucker 

33W De040204 F PF Sm Bass 

3300 PO021389 1 UB Channel Catfish 

3301 DBO41101 F U8 Carp 

3301 DBO41104 F PF Northern Pike 

3301 QDO30989 L PF Northern Pike 

3302 DBO4lWl F UB Uhite Sucker 

3302 DBO41904 F PF lm Bass 

3303 DBO42301 F UB White Sucker 

3303 DBO42304 F PF Sm Bass 

3303 00102588 L W Uhitc Sucker 

3304 DBO41001 F PF Northern Pike 

3304 DBO41004 F UB Uhitc Sucker 

3304 9DO41004 L UB Uhite Sucker 

3305 De042001 F W Channel Catfish 

3305 De042004 F PF SRI Bass 

3305 a0110388 L HI Channel Catfish 

3306 De041801 F UB Uhite Sucker 

3306 De041804 F PF Sm Bass 

3306 COO41801 1 UB White Sucker 

3307 De042101 F UB Uhite Sucker 

3308 DBO40001 F PF Northern Pike 

3309 08041301 F UB Uhite Sucker 

3310 DC032701 F M Bullhead 

3310 DC032702 F PF Ualleye 

0.11 

ND 

ND 

0.11 

ND 

0.02 

!“ll 

0.06 

0.05 

Il"o0 

0.05 

0.05 

0.03 

0.00 

0.32 

0.08 

0.11 

0.10 

0.14 

0.08 

0.17 

0.12 

0.25 

0.17 

1.19 

0.48 

0.20 

0.14 

0.32 

0.11 

0.72 

0.17 

0.48 

0.13 

r24 

ND ND ND ND ND ND 

110 0.354 ND ND w ND 

ND 0.26 D ND ND w ND 

0.17 D ND ND ND ND ND 

ND ND ND 

2.26 D 0.36 D !: 

ND NO 

3.89 ND ND 

ND 0.12 D ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

0.19 D 0.17 D ND 

0.25 D 0.24 D W 

ND ND ND 

ND ND ND 

ND 1.06 D ND 

ND 2.16 D W 

ND 

ND r37 D E 

ND 0.28 D ND 

ND ND ND 

ND NO ND 

ND ND ND 

ND 0.56 

ND ND 

ND w 

ND ND 

1.78 D 0.97 

0.76 D 0.75 

ND w 

ND ND 

ND ND 

ND 

0.17 D : 

0.13 D ND 

D 0.56 

ND 

ND 

ND 

D 0.97 

D 0.75 

ND 

ND 

ND 

ND 

ND 

w 

ND ND ND ND ND ND 

w 1.08 ND W ND 5.59 

ND ND ND ND ND 6.94 

ND ND ND 0.51 D ND ND 

ND ND ND 2.12 D ND ND 

ND ND ND ND 2.63 ND 

ND ND W 0.33 D 1.17 D ND 

w ND ND ND ND ND 

ND 0.80 D ND 2.14 D 2.54 4.85 

D ND ND 

ND ND 

ND ND 

ND 

D ND ?ll 

DW 5:82 

ND 

r94 D 0.45 

N 0.66 

ND 

26.6 To5 

1.35 D NO 

ND 

W 

ND 

W 

W 

ND 

ND 

D ND 

DW 

ND 

DW 

ND 

W 

ND 

ND 

UD 

ND 

ND 

W 

W 

ND 

W 

ND 

W 

ND 

ND 

NOD 

W 

W 

MD 

W 

W 

W 

ND 

0.79 0 2.64 ND 

ND 0.65 D 0.63 

ND ND 

i043 

4.57 2t)13 

8:SS 

4.05 ND 

16.0 ND 

:23 

ND ND 

0.84 D ND 

3.03 0.90 D ND 

1.65 D 0.39 D W 

9.80 3.42 4.16 

0.54 D ND ND 

0.78 D ND 

43.2 7.85 :28 

1.20 D ND ND 

1.13 D NO MD 

11.5 3.42 1.90 

0.30 D ND ND 

W 1.70 D ND 

ND ND 

ND ::b7 1.83 

ND ND ND 

0.58 D 0.42 D ND 

1.25 D 2.36 D 110 

11.1 3.94 1.39 

ND ND ND 

0.86 12.7 D 6.63 177 D 1: 

ND 0.72 D ND 

1.22 D 2.87 1.82 

(I.84 D 0.97 D WD 

ND ND W 

0.91 D W 

ND ND i:: 

0.80 D ND ND 

w ND 

ND 1.10 

ND ND 

ND ND 

2.40 D 3.09 

0.25 D 0.22 

ND ND 

ND ND 

t27 D ;: 

ND ND 

ND ND 

ND 1.58 

ND ND 

ND 

W !“19 

ND 

ND !!42 

W 0.14 

1.35 D 0.79 

ND 

1.95 D ::.O 

1.58 D 2.46 

ND ND ND ND 1.53 D ND 

DW 0.68 D 0.66 D 0.66 D 49.6 5.99 

W ND ND ND 1.01 D ND 

ND ND W 1.42 D ND 

0.32 D 4.63 1.56 D :56 D 28.2 8.37 

D ND ND NO ND ND ND 

W W W ND W ND 

ND ND 110 ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ::23 ND 

W ND ND ND 5.38 ND 

D ND ND ND ND 32.8 ND 

ND ND ND ND ND 

ND ND ND ND iF.1 ND 

D ND NO W ND ND ND 

ND ND ND ND 

D ND ND ND ND b4 D :: 

D ND ND ND ND 1.20 D ND 

DW ND W ND ND ND 

W W ND W W ND 

W W ND ND W W 

DW W W ND W ND 

37.4 17.5 

43.4 31.6 

3183 ND 

ND 2.48 D 

14.9 8.90 

ND ND 

1.48 D 0.80 D 

ND ND 

33.2 17.3 

ND ND 

D ND ND 

::13 ND 

8.64 4.55 

28.5 18.1 

ND 

!?w w 

1.64 D 0.32 D 

3.57 ND 

14.6 2.62 

1.08 D ND 

0.93 D ND 

32.9 14.6 

1.53 D NO 

1.86 D ND 

D 10.3 1.54 D 

0.60 D ND 

W 110 

ND W 

DW W 

ND ND 

4.43 ND 

6.19 ND 

0 34.8 7.40 

ND 

38.5 ::23 

1.94 D ND 

ND w 

D 3.01 ND 

2.06 D W 

ND ND 

DW ND 

12.2 8.07 

3.20 5.16 
XE~IOIICS CO)CENIRAIIOIIS. rig/g 

Episode SCC Type Description 

3311 DC032801 F U Rcdhorse Sucker 

3311 DcD32im f Pf mm Bus 

3312 OCMSlOf f W Rcdmrre Sucker 

3312 DCD33102 f pf sm mmr 

3313 DC033201 f m Rtiorse Sucker 

3313 oco33202 f ?f sm Bars 

3314 OCOff~I f H Chamd Cmttish 

3314 DcO333D2 f Pf lhitc Bars 

331s DC033401 f U Carp 

331s 0co33402 f If lm sass 

3316 OCO33SOf f U mite Sucker 

3317 DC033601 f 111 Uhlte kcker 

3318 DC033701 f YI Nhlte Sucker 

3319 MM1401 f IP Ufntw F(owder 

3320 0.041412 f w olueffsh 

3321 DOD40101 f IIP Ylnter floudrr 

3321 pOlDD688 I Up YMcr Ilouder 

3323 DBD4lEod f 11p Minter flader 

3324 01011252 f v lluefish 

3325 MO4121fl f w Blueflrh 

3326 OBoit206 f IP 8lueflsh 

3327 DID40301 f W Bluefish 

3327 DID40315 f LR bluefish 

3328 DDD29111 f w Carp 

3329 DDD16003 f U Oarfin 

3330 WOzOllO f W Spotted Sucker 

3331 WOMOD? f w Cwp 

3332 WOlddop f UP %aotted Drun 

3333 WDMDl2 f m S;a Catflsh 

3334 00016013 f W Sta Cdffsh 

333s 0001601f f up spot 

3335 WO29101 f Uf Red Drun 

3335 WO29102 f Mm Southern FLouder 

3335 DO029103 f Up Sheepshcad 

3335 aDO 1 w Id onr 

333600016OD4 f UPBlackonn 

3336 WOWM6 f IR Sheepshed 

3336DDD16D17 f Yp RedOru 

3336 000160~8 f Pf Spotted Seotrout 

3337 ODOl6D19 f UR Spotted Suker 

3338 DO016022 f U Spotted Suker 

3339 DDO16D23 f W two 

3340 00029114 f M Chkl Catfish 

3341 DD0161M f M CBffish 

3341 a0081788 1 UI Cstflsh 

krt 123 124 135 1234 1235 1245 CC.5 

LOlO 1# tea fca ICB 1CI 1Cl 

0.10 

D.ob 

m 

0.09 

0.23 

0.63 

0.07 

0.15 

ZS 

O.U? 

IID 

:or 

0.11 

0.02 

Fo3 

Ki 

0103 

0.08 

0.10 

0.0s 

0.02 

0.18 

0.05 

0.02 

0.18 

0.53 

0.53 

0.63 

0":: 

0.22 D 0.&8 D ND 

0.47 0 0.80 0 W 

10.10 D 110.05 D : 

0.13 D D.22 0 XD 

0.48 0 0.43 0 ND 

0.96 0 W 

ff26 0 0.17 D M) 

0.14 D 0.14 D 0.14 0 W 

0.16 0 I) w w 

No m m 10 

0.37 D 10 w W 

w w 

(0 ND 

0.15 0 0.12 

w w 

w m 

10 No 

:48 D :85 

0.0) D 0.85 

0.10 D 0.07 

4.56 2.93 

0.26 D 0.17 

D.8D 0 0.50 

2.27 0 10.6 

w 

w 

0111 

w 

w 

w 

10 

Dm 

DUD 

DRD 

0.39 

DUD 

DRD 

w 

2.69 W ND 

w 0.52 D 0.10 

x-z 

D:D6 

0.00 

0.11 

0.08 

0.10 

0.0s 

0.12 

MA 

0.17 D 0.35 D W 

0.16 DO.29 DWO 

m w 

10 z ND 

w 

w 

w 

w 0.12 0 # 

0.30 D 0.28 0 MD 

ND ND w 

MD m w 

w ND x0 

MB MI w 

10 MD w 

0.10 14402.09 D ND 0: 

0.70 D MD la 

3.16 6.57 W 

0.42 0 X0 w 

w 

w El0 0 ii 

m 

10 

MD 

w 

10 

w 

w 

w 

: 

10 

m 

m 

m 

0 ND 

ND 

m 

m 

w 

0110 

m 

m 

m 

m 

ii 

m 

m 

m 

10 

m 

m 

m 

m 

10 

m 

it99 

w 

110 

m 

w 

m 

m 

m 

110 

m 

m 

w 

: 

m 

m 

0.92 

m 

w 

m 

m 

w 

w 

10 

w 

110 

10 

w 

10 

: 

m 

ND 

10 

m 

w 

MD 

m 

m 

10 

m 

w w 

m w 

W w 

w 0.73 

w ND 

110 

w r&7 

m W 

m m 

m m 

m m 

m m 

0 0.92 D 3.19 

ND ND 

m m 

W ND 

110 W 

W m 

W W 

ND w 

W m 

w 110 

w w 

w m 

m w 

w m 

m 110 

m m 

No NP 

m m 

: 

w 

m 

m w 

10 m 

m m 

m 10 

m w 

0 1.04 D 1.04 D 1.60 D 0.57 D MD 

It0 NO NO w m 

110 ND W ND w 

w w m m m 

PCB PCNB 

0.34 D W 

m 10 

m m 

0.33 0 m 

W m 

w m 

w w 

DM) w 

ND m 

w w 

DUD w 

m m 

w w 

m m 

m m 

m 

1.56 0: 

WD m 

0.21 D m 

NO w 

0.09 D m 

m m 

w m 

W w 

m m 

0.11 0 m 

m w 

10 w 

m 110 

110 110 

m m 

110 w 

10 m 

m m 

w m 

m m 

w m 

m m 

m m 

m 10 

m m 

NCB l BHC ggHC CIS TRANS 

CNLOR CNLOR 

1.99 D 0.50 

1;18 0 10 

10 m 

w 2.57 

m W 

m w 

6.39 MD 

1.94 DXD 

II0 w 

m 

:‘6 D W 

w 8.11 

Drn 15.3 

10 1.40 

w lb.9 

w 4.68 

m 8.42 

WD 0.73 

:97 0 17.1 112 

ND 16.1 

m 

0.91 D :!bl 

m WD 

m 110 

m 1.69 D :64 D F.5 

0148 0 0.76 D ND 4.12 

La I.01 2.50 W 1.70 0 24.01 

0.23 0 DAD D 1.41 

W 2.33 0 1.53 

10 m 0.81 

m 1.51 D m 

m 1.98 0 0.39 

w 3.01 1.66 

m 10 ND 

m 10 m 

m 0.65 0 0.64 

z :!W D”D 

m W w 

m 110 w 

m 5.84 2.59 

m 0.61 D ND 

m 

?72D: m 

MD m m 

m 10 m 

aD RD w 

m m 10 

s 

m m 

m m 

E&l 0.85 10.6D : 

m 20.8 

ND L 

w 1.25 0 ii 

0 19.4 

D 12.3 

D 7.01 

11.4 

0 6.40 

IiD 

8.16 

w 

OW 

m 

w 

a.77 

D 3.M 

30.5 

10.65 

b-33 

0 2.03 D 

:;a’ 

9.s9 

(IO 

1.16 0 

ND 

7.16 

l.b2 0 

11.3 

10.8 

5.49 

8.15 

4.20 

6.10 

4.64 

IO 

5.36 

:“lO D 

w 

m 

1.35 D m 

lo.s w 

W 

ZYL& D m 

ND m 

DM m 

ND m 

w m 

w MI 

ND m 

0.69 D IID 

m m 

m 4.63 

27.7 17.2 

z3 

ID 

l-JO D 

6.Ot ND 

D-S-16 
XENOBIOTICS CDNCENTRATIONS, t-q/g 

Episode SCC Type Description 

3342 DDOl6105 F UB Spotted Sucker 

3343 DDOlllO? F UB vhitc Sucker 

3344 DDO16110 F PF Lm Bass 

3344 DD0161W F UB Carp 

3345 DDOl6111 F UB Rdorse Sucker 

3346 DDOl6113 F UB Creek Chubsucker 

3346 DDOl6114 F PF Lm Bass 

3347 DDOl6115 F UB Carp 

3348 DD016117 F PF Uhiie Perch 

3348 DD016118 F UB Blua Catfish 

3349 DO016119 F UB Carp 

3350 DDOl6121 F UB Carp 

3350 DD016122 F PF Lm Bass 

3351 DD016124 F UB Carp 

3352 DF023723 F PF Crappie 

3352 OF023724 F W Carp 

3352 00022089 L PF Crappie 

3353 DF024121 F BF Blue Catfish 

3353 DF024122 F UB SRI Buffalo 

3354 DYO22301 F W Carp 

3354 DYO22302 F PC Lm Bass 

3355 DY022303 F UB Carp 

3355 01022304 F PF Lm Bass 

3356 DE030201 F UB Carp 

3357 DY022223 F PF Squawfish 

3357 DY022224 F UB Sacramento Sucker 

3360 DDO29117 F MB Carp 

3375 DD016305 F UB Carp 

3375 00016306 F PF lm Bass 

3375 QDO7llB9 L PF Lm Bass 

3376 Do016307 F UB Carp 

3376 DD016308 F PF Cm Bass 

3377 DDOl63W F UB Carp 

3377 DDOl6310 F PF Lm Bass 

3378 DD016311 F IJB Spotted Sucker 

3378 DD029115 F IJB Greyfin Sucker 

3385 DDOl6401 F UB Redhorse Sucker 

3385 WlOl8BB C UB Redhorse Sucker 

33% DDOl6421 F UB Redhorse Sucker 

3401 DDOl65W F UB Carp 

3401 DD016510 F PF Lm Bass 

3403 Do016513 F UB River Carpsucker 

3403 DO016514 F PF Lm Bass 

3404 DDOl6515 F UB Carp 

3404 90016515 F UB Carp 

Nerc 123 124 135 1234 1235 1245 

Leg/g TCB TCB TCB TCB TCB TCB 

0.18 

ND 

0.26 

0.23 

0.87 

0.03 

0.32 

0.07 

0.25 

0.12 

0.12 

0.08 

0.65 

0.07 

0.17 

0.W 

3.92 7.58 ND 0.88 DND ND ND ND ND 

0.52 D ND ND ND ND ND ND ND ND 

0.32 

0.14 

0.07 

0.11 

0.03 

0.28 

0.04 

0.95 

0.10 

0.07 

0.08 

0.31 

0.37 D 0.50 D ND 

ND ND ND 

0.26 D 0.16 D ND 

::20 9.01 ND ND 0.06 

0.08 D ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

0.17 D ND ND 

ND ND ND 

0.41 D 0.28 D ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND 0.34 D ND 

ND ND ND 

ND 1.30 D ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

Zla 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D 0.18 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 2.30 

0.09 

0.34 

0.07 

0.20 

0.07 

0.07 

0.17 

NA 

0.24 

0.13 

0.42 

0.10 

0.21 

0.07 

ND ND ND 

1.83 D 1.20 D ND 

19.4 17.0 ND 

0.38 D 0.38 D ND 

0.55 D 0.61 D ND 

26.8 16.1 2.35 

0.24 D 0.24 D ND 

4.03 2.58 ND 

0.54 D 0.40 D 0.04 

8.16 4.77 0.79 

4.38 2.80 ND 

ND ND ND 

ND ND ND 

ND ND 

ND 0.51 D “dl25 

0.07 D 0.08 D ND 

1.14 D 1.05 D 14.9 

0.29 D 0.17 D 0.78 

ND ND ND 

0.97 D 0.62 D ND 

ND ND ND 4.64 ND ND 

ND ND ND ND ND ND 

NO ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

D ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

D ND ND ND ND ND ND 

D ND ND ND ND ND ND 

NO ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND NO ND 

D ND ND ND ND 0.36 D ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

D ND ND ND ND ND ND 

ND ND ND ND ND ND 

ND ND ND ND ND ND 

ocs PCB PCNB HCB aBHC 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.12 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.25 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

1.02 D : 

ND ND 

D 0.83 D ND 

ND 

ND !!ra 

2.00 D 4.01 

MD ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 2.79 

ND ND 

ND ND 

1.59 D ND 

No ND 

0.30 D 1.13 

ND ND 

ND 1.10 

ND 2.33 

1.38 D ND 

ND ND 

2.92 1.66 

ND ND 

ND 6.34 

11.5 ND 

ND ND 

ND ND 

0.90 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 1.02 

ND 3.05 

ND ND 

ND ND 

ND ND 

ND ND 

2.70 ND 

0.14 D ND 

2.31 D ND 

ND ND 

ND ND 

ND ND 

gBHC CIS TRANS 

CHLOR CHLOR 

25.7 ND 32.8 

4.66 ND 2.55 

6.75 ND 11.9 

0.90 D 2.18 D 1.42 D 

3.35 ND ND 

0.16 D ND ND 

ND 25.3 20.1 

ND ND ND 

4.62 ND ND 

ND ND 7.98 

ND ND ND 

ND 1.29 D ND 

ND ND 9.72 

ND ND 

D 1.14 D ND :I0 D 

ND ND 

D 0.58 D 6.14 ::37 

D 2.04 D ND 3.25 

8.42 ND 6.46 

ND 

g.9 

ND 

DND 32.0 

ND ND ND 

ND 43.8 25.8 

21.3 27.0 16.8 

2.37 D 16.2 10.9 

21.9 145 155 

:71 D 4153 2 01 D 6.40 13.26 

la.5 185 E 191 E 

ND 1.57 D 2.92 

21.9 177 159 

D 1.56 D 2.58 5.03 

ND ND ND 

4.98 ND ND 

1.35 D 13.2 8.06 

1.11 D 10.5 6.17 

ND 46.5 32.0 

ND 13.4 8.38 

0.39 D 0.43 D ND 

3.24 64.4 30.0 

ND 3.86 1.55 D 

ND 13.1 a.75 

0.50 D 12.9 8.77 

D-5-2 7 
XENOBIOTICS CONCENTRATI~S. nB/B 

123 124 135 1234 

TCB TCB TCB TCB 

1235 1245 

TCB TCB 

Episode SCC Type Description OCS PCB PCNB HCB aBHC gEHC 

3409 DBOO5101 F IJB Catfish 

3409 DBO40701 F UB Carp 

3409 08040706 F PF Lm Bass 

3411 DBO40501 F UB Redhorse Sucker 

3412 DBO40901 F PF Sm Bass 

3412 DBO40907 F UB Carp 

3414 DC036203 F PF Sm Bass 

3414 DC036204 F BF Channel Catfish 

3415 DC036205 F PF Sm Bass 

3415 DC036206 F BF Charnel Catfish 

3419 DC036207 F UB Uhite Sucker 

3419 DC036201 F PF Freshwater Drun 

3420 DC036209 F PF Greenfish 

3420 DCD36210 F UB Carv 

3421 DC036211 F PF Uhiie Perch 

3421 DC036212 F u8 Carp 

3422 DC036213 F PF Lm Bass 

3422 DC036214 F UB Yellow Bullheed 

3423 DC036216 F UB Uhite Catfish 

3424 DC0362111 F UB mite Catfish 

3425 DF025005 F UB Carp 

3426 06069102 F PF Bluefish 

3427 08069103 F PF Bluefish 

34211 DBO69104 F PF Bluefish 

3429 08069105 F PF Ueekfish 

3430 DBO69106 F b/B Uhite Catfish 

3431 DBO691W F UB Red Snapper 

3433 08069112 F UP Flounder 

3434 DBO40801 F UP Flour&x 

3434 ODOllBB9 L UP Flouder 

3435 00016602 F UB Bigmouth Buffalo 

3443 DFOO9118 F UB Carp 

3444 DDOl6603 F MB Carp 

3444 DDOl6604 F BF Channel Catfish 

3444 00029512 F PF Lm Bass 

3465 DDO29513 F UB Flounder 

3446 DD016605 F PF Striped Bass 

3446 00016606 F UB Carpsucker 

3446 ODWlBB9 F UB Carpsucker 

Mere 

ra/g 

0.1 

0.06 

0.26 

0.04 

0.22 

0.21 

0.31 

0.09 

0.22 

0.29 

0.02 

0.20 

0.07 

0.03 

0.05 

0.01 

0.73 

0.46 

0.07 

0.03 

0.03 

0.20 

0.28 

0.19 

0.11 

0.08 

0.15 

0.05 

0.04 

0.05 

0.422 

0.05 

0.08 

0.28 

0.04 

0.39 

0.02 

0.35 D 0.62 D ND ND 

ND 

1.93 D E.4 

ND 

0.95 0: 

ND ND ND 

ND :“ll ND ND 

5.34 3.12 0.55 D ND 

2.19 D 1.06 D ND ND 

0.14 D NO 

1.14 D 0.83 D : 

NO 

ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND 0.22 D ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND NO ND 

0.41 D 1.35 D ND ND 

17.7 11.9 1.70 D ND 

0.64 D 0.72 D NO ND 

0.18 D 0.15 D ND ND 

ND ND ND ND 

ND ND 

0.47 D 1.42 D : 

ND 

ND 

0.27 D 1.00 D ND ND 

0.68 D 2.31 D ND ND 

ND NO ND ND 

ND ND ND NO 

ND ND om[35 D : ND ND 

ND ND ND ND ND ND 

ND 0.30 D ND ND ND ND 

ND 0.13 D ND ND ND ND 

ND 0.22 D ND ND ND ND 

0.11 D 0.19 D ND ND ND ND 

0.22 D 0.22 D ND 0.47 D ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND 1.51 D ND ND 

ND ND 29.5 ND No 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND NO ND ND ND 

ND ND ND ND ND 

ND ND ND ND No 

ND ND ND ND ND 

ND NO ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND NO ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND NO ND ND ND 

ND ND ND ND ND 

ND ND ND ND 0.86 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND ND ND 

ND ND ND NO ND 

ND ND ND 4.90 ND 

L 

NO 

ND 

1.09 

2.93 

3.30 

1.87 D ND 

1.90 D ND 

NO ND 

ND ND 

D ND ND 

ND ND 

ND ND 

2.53 2.47 D 11.00 

ND 

:91 MD 

wo 

ND 

0.50 D 0.73 D ND 

11.5 ND ND 

ND ND ND 

ND 3.63 ND 

ND NO ND 

1.43 D ND 

:I4 D 4.65 ND 

ND ND ND 

ND 0.39 D ND 

ND ND ND 

ND 

ND 

ND ND ND 

ND ND ND 

ND 0.85 D ND 

ND NO ND 

CIS TRANS 

CHLOR CHLOR 

37.3 22.8 

ND ND 

ND ND 

1.72 D ND 

42.6 17.8 

:54 

1.63 

ND 

ND 

ND 

ND 

ND 

ND 

?.17 

ND 

ND 3.37 ND ND 

DND 1.13 D 0.37 D 2.81 

ND ND ND 5.11) 

ND ND ND 11.36 

ND ND ND 

ND ND ND ;:97 

ND ND ND 

ND 1.15 D 1.11 D E.5 

ND 1.25 D 13.0 

::.l RN No 2.67 10.6 

ND 1fJ 

7.24 NO ND B6.a 

10.7 ND ND 113 

0.85 D 0.73 D ND 7.66 

ND ND 0.31 D NO 

1.09 D ND NO 5.77 

0.94 4.97 1.41 D 10.3 

6.44 ND 1.35 D 11.3 

ND 

4.56 

ND 

6.39 

D 5.75 

1.92 D 

ND 

ND 

ND 

ND 

ND 

NO 

1.89 D 

ND 

ND 

1.35 D 

1.91 D 

3.61 

ND 

2.13 D 

ND 

4.86 

6.72 

5.77 

206 

85.0 

El26 E 

12.9 

ND 

23.9 

20.5 

22.1 

D-S-28 
Key for Xenobiotic Data Table (Units = ng/g)(continued) 

OXYCHLOR 

cis NON 

tram NON 

HEPT 

HEPT EP 

DDE 

DIELDRIN 

ENDRIN 

DICOFOL 

ME CHL 

PERTHANE 

MIREX 

NITROFEN 

CHLORPYRIFOS 

ISOPROP 

= Oxychlordane 

= cis-Nonachlor 

= trans-Nonachlor 

= Heptachlor 

= Heptachlor epoxide 

= p,p’- DDE 

= Dicofol (Kelthane) 

= Methoxychlor 

= Isopropalin 

PATA FLAGS 

D= Value below limit of quantitation for all xenobiotics except mercury and PCBs 

D = 2.5 ngig 

For polychlorinated biphenyls 

ber of Chlorines 

1-3 1.25 

4-6 2.50 

7-8 3.75 

9-10 6.25 

E = Value exceeds highest calibration standard 

26880-48-g 

3732-49-4 

39765-80-5 

76-44-8 

1024-57-3 

72-55-9 

60-57- 1 

72-20-g 

115-32-2 

72-43-5 

72-56-O 

2385-85-5 

1836-75-5 

2921-88-2 

33820-53-o 

See Dioxin/Fur-an Data Table Key for explanation of other codes. The tables include 

environmental samples (those starting with a sample number of D) and the duplicate samples 

(those starting with a Q) and confirmation samples (those starting with an S). The number of 

samples shown on the summary tables in Volume I does not include the duplicate and 

confirmation samples. 

D-5-19 
D-S-20 
Episode SCC Type Description 

2015 DFOOlOOl F UB Carp 

2016 DFOOllOl F IJB Sucker 

2017 DFOOl201 F UB Carp 

2018 DF001301 F UB Sucker 

2023 DF001403 F UB Carp 

2026 DF001702 F IJB Carp 

2027 OF001803 F UB Carp 

2037 DYOOO501 F. UB not available 

2056 DE000501 F UB Carp 

2057 DE000601 F UB Carp 

2059 DE000801 F UB Carp 

2060 DEOOWOl F UB Carp 

2070 DJ000902 F UB longnose Sucker 

2098 DHOOl501 F UB N/A 

2100 DH001703 F UB Catfish 

2105 DHOO2204 F UB Carp 

2109 DH002601 F UB N/A 

2110 DH002710 F UP Brown Trcut 

2122 DH003904 F UB Uhite Sucker 

2126 DO000302 F bitI Carp 

2133 DO001002 F BF Blue Catfish 

2139 DD0016Dl F UB Carp 

2142 DDOOl902 F UB Catfish 

2148 DDOO2501 F UB Saltwater Catfish 

2151 DD002803 F UB SDatted Sucker 

2152 00002903 F UB Like Chubsucker 

2190 DC005101 F UB Carp 

2190 DC005104 F PF Bluegill 

2191 DC005205 F UB Carp 

2194 DG005501 F UB Carp 

2199 DC006001 F UB Carp 

2199 DC006004 F PF Lm Bass 

2201 DC006201 F UB Carp 

2205 DG006601 F b/B Carp 

2210 DC005401 F UB Catfish 

2211 DC005503 F UB Redhorse Sucker 

2212 DC005602 F PF Sm Bass 

2212 DC005605 F UB Uhite Sucker 

2215 DC005902 F VB Carp 

2216 DC006003 F UB Uhite Sucker 

2220 DC006405 F UB Catfish 

OXY 

CHLOR 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

:x*5 

ND 

19.1 

ND 

ND 

ND 

ND 

12.9 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E.0 

ND 

ND 

28.8 

ND 

9.94 

NO 

:D62 

4:26 

4.09 

25.3 

91.4 

ND 

NO 

CIS 

NON 

22.6 

ND 

ND 

ND 

!?14 

ND 

:“o 4 

31:2 

25.5 

27.7 

ND 

r56 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

20.5 

ND 

ND 

ND 

14.6 

ND 

17.8 

23.3 

9.67 

12.6 

ND 

NO 

52.0 

5.57 

6.57 

42.5 

124 

NO 

ND 

TRANS HEPT 

NON 

61.7 

18.1 

2.49 

a.66 

4.96 

16.1 

3.85 

3.18 

82.9 

89.1 

74.6 

77.4 

ND 

ND 

25.2 

ND 

17.6 

::31 

9.23 

6.17 

ND 

36.8 

11.1 

ND 

:;.7 

ND 

56.2 

73.6 

26.3 

36.4 

2.38 

ND 

158 

15.6 

22.9 

142 

477 

ND 

7.07 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

:r)79 

ND 

ND 

D NO 

ND 

NO 

NO 

NO 

E NO 

E 19.6 

ND 

ND 

XENOEIOTICS CONCENTRATIONS. ns/s 

HEPT 

EP 

6.34 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

15.0 

16.0 

23.2 

ND 

ND 

ND 

ND 

24.4 

ND 

k7 

ND 

NLI 

NO 

ND 

ND 

KS 

ND 

::.7 

19.1 

7.91 

ND 

ND 

15.7 

ND 

1.07 

::.9 

ND 

ND 

DDE DIELDRIN ENORIN DICOFOL HE 

471 E 73.7 

1223 E ND 

66.7 ND 

NO NG 

30.5 1.70 

252 E ND 

64.4 ND 

0.51 0 ND 

38.7 58.5 

64.6 110 

769 E al.2 

46.5 153 

2.89 ND 

5.04 ND 

la7 E la.1 

2.57 ND 

62.8 108 

5.61 ND 

la.9 7.64 

474 E la.2 

659 E 15.4 

4.95 

Z:Z 

:9 

7.i6 

8.97 ND 

10.4 

56.2 E 1:4 

4.61 14.7 

52.3 258 

41.8 60.8 

70.0 312 

48.8 70.4 

19.2 8.79 

22.3 7.94 

381 E 73.1 

88.8 E a.45 

52.1 E 4.92 

186 E 112 

122 128 

2.04 D ND 

19.6 NO 

NO 

ND 

ND 

ND 

0 3.73 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

E ND 

ND 

7.50 

ND 

E ND 

E ND 

ND 

ND 

9.02 

NO 

ND 

E 2.25 

NO 

ND 

ND 

CHL PYRI FOS 

ND ND 

ND ND 

:I!26 D 1: 

ND ND 

ND 

ND r22 

NO NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

ND Fai 

0.79 D ND 

ND ND 

ND ND 

5.37 ND 

ND 

!‘lW ND 

NO ND 

ND ND 

4.56 ND 

2.32 D 1.04 

1.23 D NO 

0.66 D ND 

ND ND 

ND ND 

ND 4.82 

ND ND 

NO ND 

0 0.64 0 ND 

6.02 ND 

ND ND 

ND ND 

PERTHANE MIREX NITROFEN CHLOR I SDPROP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

4.24 

21.6 

ND 

ND 

ND 

ND 

ND 

2.07 

ND 

6.22 

0.76 

ND 

ND 

1.30 

NO 

NO 

ND 

z.1 

3.62 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

NO 

2.24 

2.31 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

D ND 

ND 

NO 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

D NO 

D NO 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

11.4 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::21 

1.82 

ND 

ND 

::61 

ND 

10.4 

ND 

ND 

19.4 

ND 

ND 

ND 

ND 

23.9 

NO 

ND 

7.66 

26.3 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

8.65 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D-s-21 
Episode SCC Tn>e Description 

2227 DC007104 F UB 

2228 DC007201 F PF 

2231 DC007503 F bIB 

2246 05002302 F UB 

2247 DJ002404 F UP 

2280 DF005201 F UB 

2280 po1216aa L UB 

2283 OF005501 F UB 

2290 DDOO3403 F UB 

2294 DDOO3aO4 F b/B 

2297 DDOO4102 F VB 

2298 DD004203 F Up 

2301 DD004504 F UP 

2302 DD004601 F UB 

2304 DD004aol F MB 

2309 DD005301 F IJB 

2322 DBOol301 F UB 

2326 DBOol701 F UB 

2328 DBOOl904 F PF 

2329 DBOo2004 F PF 

2341 DD006003 F UB 

2355 DA001603 F UB 

2356 DA001702 F PF 

2375 DA003803 F UB 

2376 DA003903 F UB 

2379 DE005404 F PF 

2380 DE005501 F UB 

2383 DE005aol F UB 

2385 DE006002 F b/B 

2394 DE006901 F UB 

2394 a0006901 L UB 

2394 a0022189 L UB 

2397 DE007201 F UB 

2410 DE008501 F UB 

2410 DE008504 F PF 

2416 DE009101 F UB 

2422 DE009702 F UB 

2427 DE010202 F UB 

2429 DE010402 F VB 

2430 DE010603 F UB 

2430 ml21488 L F 

2431 DE010703 F UB 

Channel Catfish 

Longear Sunfish 

Gizzard Shed 

Bridgelip Sucker 

Mountain Vhitefish 

Carp 

Carp 

Gray Redhorse 

Spotted Sucker 

Carp 

Carp 

Lm Bass 

Rock Bass 

PuiIlback Carpsucker 

Carp 

Carp 

Uhi te Sucker 

White Sucker 

Chinook Salmon 

Broun Trout 

Carpsucker 

Uhite Sucker 

Lm Bass 

Uhite Sucker 

Uhite Sucker 

Lm Bass 

Carp 

Carp 

Uhite Sucker 

Carp 

Carp 

Carp 

Sucker 

Carp 

Sm Bass 

Carp 

Carp 

Carp 

Carp 

Redhorse Sucker 

not available 

Sucker 

2432 DE010710 F UB Redhorse Sucker 

2435 DE011001 F IJB Longnose Sucker 

2437 DE011203 F UB Carp 

D-5-22 

OXY 

CHLDR 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

NO 

11.3 

10.6 

18.5 

NO 

ND 

ND 

la.3 

K.4 

68.0 

ND 

36.9 

63.2 

57.6 

ND 

ND 

ND 

ND 

:b 

ND 

ND 

NO 

ND 

17.9 

4.64 

ND 

CIS 

NON 

ND 

:;.7 

ND 

ND 

ND 

NO 

NO 

16.5 

ND 

ND 

ND 

ND 

ND 

12.7 

ND 

ND 

ND 

42.3 

24.6 

47.2 

ND 

ND 

ND 

12.2 

ND 

35.1 

65.7 

ND 

61.9 

59.9 

50.0 

ND 

ND 

NO 

ND 

ND 

ND 

14.9 

ND 

ND 

ND 

19.6 

10.0 

ND 

TRANS HEPT 

NON 

3.61 ND 

ND ND 

96.7 ND 

10.5 ND 

8.20 ND 

4.12 ND 

4.34 ND 

ND ND 

53.3 ND 

ND ND 

11.0 ND 

::06 0 ND 

3.40 ND 

37.2 ND 

14.9 

2.12 D :: 

ND NO 

129 E ND 

60.3 ND 

151 E ND 

2.81 NO 

NO ND 

8.27 ND 

38.5 ND 

2.18 D ND 

96.9 ND 

172 ND 

ND ND 

279 E ND 

197 E ND 

167 E ND 

2.46 D ND 

63.4 ND 

3.63 ND 

83.9 ND 

8.21 ND 

58.3 ND 

37.8 ND 

ND ND 

1.38 D ND 

ND ND 

58.6 ND 

20.4 ND 

10.9 ND 

XENCJBIOTICS CONCENTRATIDNS. t-d? 

‘4EPT 

EP 

DOE DIELDRIN ENDRIN- ;ICOFOl HE 

CHL 

ND 

ND 

a.a4 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

NO 

ND 

2.92 

5.06 

NO 

ND 

NO 

ND 

NO 

ND 

ND 

NO 

ND 

15.3 

26.1 

ND 

ND 

ND 

ND 

NO 

Ka 

ND 

ND 

ND 

ND 

ND 

11.4 

ND 

29.8 4.34 

1.09 0 NO 

151 49.6 

41.9 ND 

21.6 NO 

45.9 ND 

46.9 ND 

5.79 

94.0 Kl 

371 E 14.5 

la.8 ND 

la6 END 

14.2 ND 

53.9 E ND 

337 E 38.0 

217 E ND 

15.9 1.29 

9.63 3.76 

682 E 53.5 

415 E 47.3 

56.1 83.7 

14.9 9.73 

3.02 ND 

63.0 16.3 

39.0 25.6 

6.62 ND 

497 E 105 

997 114 

10.9 NO 

114 90.0 

86.6 73.0 

73.4 68.3 

19.6 6.17 

579 E 99.0 

15.3 4.30 

11508 2:: 

1521 E 1M) 

640 E 4.60 

12.6 NO 

11.7 ND 

7.73 2.48 

516 E ND 

114 E 55.8 

128 58.6 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

D NO 

ND 

4.19 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

::91 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0 NO 

ND 

13.4 

ND 

ND ND 

ND NO 

ND ND 

ND ND 

0.47 D NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ha 

2.82 

ND 

ND 

ND 

ND 

1.78 

ND 

?lO 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

N 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

D ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

PERTHANE HIREX NITROFEN CHLOR I SOPROP 

PYRIFOS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.03 D ND 

0.85 D ND 

ND ND 

ND ND 

7.89 ND 

ND ND 

ND ND 

ND ND 

0.89 D ND 

7.13 ND 

6.39 ND 

ND ND 

ND ND 

225 E 3.39 

131 ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND 

?a1 ND 

8.63 ND 

ND ND 

ND ND 

ND ND 

NO ND 

0.45 D ND 

3.911 ND 

ND NO 

ND ND 

ND ND 

2.46 D ND 

3.21 ND 

ND ND 

NO ND 

ND ND 

1.03 D ND 

0.44 D ND 

ND ND 

6.49 ND 

ND ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

0.95 0 ND 

NO ND 

NO ND 

ND ND 

ND ND 

ND ND 

4.66 ND 

ND ND 

26.4 ND 

33.0 ND 

ND ND 

la.2 ND 

21.5 NO 

11.2 ND 

ND ND 

9.44 ND 

ND ND 

46.7 ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 
Episode SCC Type Description 

2439 DE011401 F UB Carp 

2439 DE011402 F Up Sm Bass 

2478 DJOO3902 F UB Sucker 

2500 DC010203 F VB Black Buffalo 

2532 DF019303 F UB CarD 

2544 DFOl9202 F UB Bla;ktail Redhorse 

2608 DE014504 F UB Carp 

2618 DE015401 F UB Carp 

2618 DE015402 F BF Carp 

2618 DE015403 F UB Quillback 

2651 DB008401 F UB White Sucker 

2653 DB008503 F UB Carp 

2654 DBOO8601 F UB Carp 

2709 DBOO5101 F UB Catfish 

2721 DA006502 F UB Sucker 

2721 QDOl1089 1 UB Sucker 

2722 DA006601 F UB Sucker 

2725 DA006301 F UB Sucker 

2748 DY006505 F UB Sucker 

2776 DYOO7101 F UB Carp 

2776 POD10489 L UB Carp 

3001 DE019502 F UB White Sucker 

3022 DA008401 F UB !dhi te Sucker 

3023 DA008501 F PF Sm Bass 

3024 DA008601 F PF Lm Bass 

3025 DA008701 F UB Uhite Sucker 

3028 DA008801 F PF Chain Pickerel 

3034 DGO25701 F blB Carp 

3035 DC025801 F UB Carp 

3036 DG0259D2 F UB Carp 

3037 DGO26001 F UB Carp 

3038 DC026101 F UB Carp 

3039 DC026201 F UB Carp 

3040 06026301 F UB Carp 

3041 DC026402 F UB Carp 

3042 DC026501 F UB Carp 

3042 DC026502 F PF Northern Pike 

3042 PO026501 L bIB Carp 

3043 DGO26601 F UB Carp 

3044 06026701 F UB Car’p 

3045 DGO26801 F UB Carp 

3045 DG026802 F PF Flathead Catfish 

3046 DC026901 F UB Bigmouth Buffalo 

3047 DC027001 F UB Carp 

3068 DC027101 F UB Carp 

OXY CIS 

CHLDR NON 

57:; 48.3 548

NO ND 

ND ND 

ND 12.5 

ND NO 

E.2 

ND 

57.7 

24.3 19.3 

68.9 51.2 

1.45 D 7.04 

16.4 38.4 

9.34 

ND KB 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND NO 

ND NO 

ND ND 

NO ND 

ND ND 

ND ND 

NO 

ND :“29 

13.5 li.3 

:I!91 9.88 669

ND ND 

28.0 44.1 

1.17 D a.37 

ND ND 

4.08 ND 

NO NO 

NO 18.8 

:44 20.4 11.3 

42.3 59.6 

2.53 7.31 

6.95 a.02 

ND ND 

TRANS HEPT 

NON 

4.53 ND 

7.15 ND 

30.7 ND 

15.3 ND 

ND ND 

197 NO 

66.1 ND 

164 ND 

17.2 ND 

1% E ND 

65.61 ND 

57.2 ND 

NO ND 

ND ND 

ND ND 

ND ND 

NO NO 

3.14 NO 

5.42 ND 

NO NO 

ND ND 

ND ND 

ND ND 

11.1 E ND 

NO ND 

ND 

2D7.9 ND 

NO 

ii.1 ND 

ND NO 

133 E ND 

E 23.4 E ND 

2.07 D ND 

84.6 a.84 

2.33 D ND 

50.7 ND 

ND ND 

ND 4.43 

186 E 9.74 

22.3 2.09 

20.7 ND 

ND ND 

HEPT 

EP 

20.8 

16.8 

ND 

NO 

12.4 

ND 

ND 

28.6 

8.16 

ND 

ND 

6.57 

a.07 

ND 

ND 

ND 

NO 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 

ND 

19.9 

ND 

14.5 

ND 

1.03 

ND 

ND 

ND 

NO 

10.9 

24.1 

D 2.26 

10.6 

ND 

19.6 64.6 225 E 3.63 17.6 

DDE DIELDRIN ENDRIN--ZilCOFOL NE PERTHANE MIREX NITROFEN CHLOR I SDPRDP 

109 99.8 

80.9 103 

197 E ND 

6.98 3.99 

73.8 99.5 

25.3 38.2 

64.4 35.0 

77.6 128 

23.2 47.3 

65.2 88.5 

89.0 E 6.M) 

177 E 23.8 

59.92 19.25 

223 E 14.9 

20.6 ND 

13.8 ND 

3.01 ND 

10.6 ND 

31.1 NO 

58.7 E ND 

101 E NO 

27.6 NO 

14.0 NO 

2.18 D ND 

118 E 46.0 

la.6 E 3.68 

258 E 160 

72.0 323 

103 E 136 

70.3 NO 

la5 E 36.0 

555 E 24.6 

374 E 74.3 

165 E 61.3 

12.0 1.58 

108 55.8 

85.8 79.3 

133 E 116 

166 E 107 

23.4 18.5 

36.4 216 

iY.1 

ND 

190 

ND 

E ND 

ND 

NO 

7.45 

NO 

ND 

35.1 

12.9 

6.30 

NO 

ND 

ND 

:I!55 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

E 4.52 

NO 

NO 

E ND 

E ND 

E NO 

NO 

ND 

E ND 

E 4.97 

ND 

0 ND 

ND 

ND 

E NO 

E 7.37 

ND 

END 

ND 

E la.5 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:I!17 

ND 

ND 

NO 

NO 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

E ND 

ND 

NO 

ND 

ND 

ND 

:I!57 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

N 

NO 

ND 

CHL 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

D ND ND 

ND ND 

1.51 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

NO NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

2.50 D ND 

ND ND 

ND ND 

ND NO 

NO ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

NO ND 

ND ND 

1.73 D ND 

1.16 D NO 

2.63 ND 

NO ND 

ND ND 

NO NO 

ND ND 

0.97 D ND 

5.90 ND 

ND 10.40 

2.21 0 NO 

4.77 ND 

ND NO 

ND ND 

ND NO 

NO ND 

0.36 0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

ND ND 

1.03 D ND 

ND NO 

ND ND 

NO ND 

ND ND 

0.39 D ND 

ND ND 

ND ND 

NO NO 

ND NO 

ND ND 

ND ND 

0.70 D ND 

NO ND 

ND ND 

ND ND 

ND ND 

PYRI FOS 

ND NO 

17.3 ND 

ND ND 

1.50 0 ND 

ND ND 

NO ND 

ND ND 

17.8 ND 

5.55 ND 

ND 

:“91 ND 

4.59 NO 

ND 2.11 

3.62 NO 

NO ND 

NO ND 

NO NO 

NO ND 

ND NO 

NO ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

1.46 D NO 

4.53 15.0 

5.13 NO 

ND ND 

12.4 ND 

0.81 D 2.82 E 

ND NO 

30.1 13.4 

1.62 D ND 

40.8 25.9 

5.44 37.5 

9.04 10.5 

17.8 6.53 

6.12 NO 

ND ND 

ND 16.5 

12.1 5.92 

D-5-23 
Episode SCC Type Description 

3048 06027102 F PF White Bass 

3048 a0012689 L PF Uhi te Bass 

3048 abO27101 1 UB Cerp 

3049 DC027201 F UB Carp 

3050 DC027301 F UB Bigmuth Buffalo 

3060 DFDO9101 F UB Flathead Catfish 

3060 DFO09102 F UB Sm Buffalo 

3060 a0073189 1 UB Flatheed Catfish 

3061 DF019106 F UB Sucker 

3062 DFO24024 F UB Blue Catfish 

3063 OF023301 F UB Sea Catfish 

3063 OF023302 F PF Spotted Seatrout 

3064 DFD23305 Id Shellfish 

3065 DF023419 F BF Bigsouth Buffalo 

3065 OF023420 F UB FLatheed Catfish 

3D65 PO010788 F BF BiBmouth Buffalo 

3066 DFO23503 F UB Catfish 

3066 DFO23504 F PF Freshwater Drun 

3068 DFO24001 M Oysters 

306B DFO24002 F PF Atl. Croaker 

3069 DF024007 F UB Sea Catfish 

3069 DFO24008 F PF Trout 

3069 ODOS1788 F W Sea Catfish 

3070 DFO24DO9 F UB Croaker 

3070 DFO24010 F PF Sheepshead 

3071 DFO24014 F UB Caip 

3071 DFO24015 F PF Lorgnose Car 

3072 DF024017 F UB Carp 

3072 000706E8 L UB Carp 

3073 DF019221 F UB Uhite Sucker 

3074 DF026017 F PF Brown Trout 

3076 DF028502 F UB Chemel Catfish 

3077 DF019114 F UB Redhorse Sucker 

3078 DFOO9118 F UB Carp 

3078 DFO23815 F UB Sm Buffato 

3070 DF023816 F PF Bleck Crappie 

3079 DFOl9205 F PF Nhite Bass 

3079 DF019206 F UB Carp 

3080 DF023317 F UB Carp 

3080 DF023318 F PF Lm bass 

3081 DF024105 F PF Uhite Bass 

3081 OF024106 F UB Catfish 

3082 DFO234Ol F llB Carp 

3083 DFO23406 F PF Lm Bass 

3084 OF024109 F HI Channel Catfish 

OXY CJS 

CHLOR 1011 

2.27 D 5.42 

1.94 D 4.98 

18.6 38.1 

10.1 37.6 

6.75 8.92 

ND ND 

ND ND 

ND ND 

2.23 D ND 

ND 

F79 a.66 

ND 3.60 

ND ND 

ND ND 

ND 4.97 

ND ND 

ND 7.74 

ND ND 

ND ND 

ND 5.18 

ND 5.56 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

:.5 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

1.85 D yy.3 

ND ND 

ND ND 

ND 7.44 

2.27 D 13.2 

ND ND 

ND ND 

ND ND 

ND ND 

:59 E.6 

TRAMS 

NON 

12.9 

11.8 

97.5 

ND 

23.9 

ND 

21.47 

ND 

ND 

20.3 

20.1 

7.55 

3.77 

4.24 

10.6 

7.28 

16.3 

ND 

ND 

10.4 

9.98 

ND 

15.8 

4.44 

No 

HEPT 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

104.14 ND 

172.05E ND 

6.55 ND 

4.47 ND 

ND No 

ND ND 

7.10 ND 

ND 

!!72 ND 

45.9 ND 

2.89 ND 

24.86 ND 

18.3 ND 

31.9 ND 

ND 

:54 ND 

ND ND 

7.87 ND 

ND 

t.4 ND 

XENOBJOTJCS CONCENTRATJDNS, w/B 

HEPT DJCOFOL ME PERTHANE MJREX NJTROFEN CHLOR 1 SOPRDP 

EP 

DDE DJELDRJN ENDRJN 

CHL PYRJFOS 

4.15 

3.88 

17.0 

16.6 

9.34 

ND 

ND 

ND 

2.26 

ND 

ND 

ND 

ND 

ND 

ND 

LO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::21 

?a7 

3.40 

4.29 

ND 

llD 

ND 

ND 

ND 

ND 

13.1 26.2 

11.6 25.3 

32.0 92.8 

206 E 201 

30.6 125 

21.99 ND 

447.57E ND 

14.87 ND 

5.93 4.18 

271 E 8.33 

41.5 12.4 

8.54 5.91 

3.17 

18.8 :D61 

29.1 6144 

31.3 4.95 

39.6 61.5 

9.49 8.28 

16.8 ND 

12.2 13.4 

51.2 5.38 

3.33 

69.7 ::71 

6.80 ND 

0.56 D ND 

154.7!iE 53.11 

302.29E 89.36 

545 E ND 

ND ND 

ND ND 

ND ND 

E ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

2.52 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.64 D ND 

ND 

ND 

ND 

ND 

ND 

416 E ND ND 

7.79 2.20 D ND 

43.0 ND ND 

55.1 ND ND 

6.39 ND ND 

2425 E ND ND 

152 E 30.6 ND 

51.1 E 4.78 ND 

23.21 9.96 ND 

32.4 8.44 2.51 

298 E ND ND 

10.66 ND ND 

10.3 0.62 D ND 

4.40 

2199 

E: ND 

ND 

93.2 E-4 ND 

3221 E 18.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.30 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

2.10 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.81 D ND 

0.70 D ND ND 

ND ND ND 

ND ND ND 

ND ND NJI 

0.76 D ND ND 

4.05 ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.17 D ND 

:03 D t: 

0.88 D ND 

ND ND 

0.33 D ND 

0.51 D ND 

0.42 D ND 

ND ND 

ND ND 

ND ND 

!!35 DE 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

:19 ND 

ND ND 

ND ND 

ND ND 

0.94 D ND 

ND ND 

ND ND 

ND No 

ND ND 

ND ND 

ND ND 

ND ND 

42.4 ND 

ND ND 

0.34 D ND 

0-H D NO 

10.4 ND 

ND ND 

ND ND 

ND ND 

ND ND 

12.3 ND 

4.37 13.9 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.81 D ND 

ND ND 

3.11 9.09 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

63.68 NO 

11.78 ND 

1.83 D ND 

2.10 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

:%I ND 

0.82 D ND 

3.57 ND 

1.61 D ND 

17.5 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

g.6 ND 

D-5-24 
Episode SCC Type Description 

3085 DFO24113 F UB Sea Catfish 

3085 OF024114 F PF Black Dru 

3086 DF0234W F UB Catfish 

3OB6 DFO23410 F PF Red Dnr 

3087 OF023413 F Ufl Carp 

3087 OF023414 F PF tiite Crappie 

3087 DFO23415 F UP Btusgill 

3DJ%B qFD23417 F w Charnel Catfish 

3068 DFO23418 F PF Bluegill 

3089 DFOl92D9 F PF Uhite Crappie 

3089 DFOl9210 F UB Carp 

3090 OF019213 F PF White Crappie 

3090 DF019214 F UB Charnel Catfish 

3091 DFO19217 F UB River Carpsucker 

3092 DF023501 F UB Carp 

3092 OF023502 F PF Uaramth 

3093 DFO24Dll F PF Lm Bass 

3093 DFD24118 F YB Sm Buffalo 

3094 DC017201 F BF Chmci Catfish 

3095 DC038801 F BF Brown Bullhead 

3095 DC038602 F UB Chmnel Catfish 

3096 DC035001 F BF Brom Bullhead 

3096 DC035002 F YB Chamel Catfish 

3097 DCO387Ol F BF Brown BulUmad 

3097 DCOUlTOZ F m Carp 

3097 PO071969 L BF Brown Bullhead 

3098 DCO3B601 F Ys rrhite Sucker 

3098 DCO3B6D2 F PF Amrican Eel 

3098 QoOSl288 F UB site Sucker 

3100 DC019701 F PF Uhite Perch 

3101 DCOl99Dl F PF Bran Trout 

3103 DC036201 F UB Chamel Catfish 

3103 DC036202 F UB Carp 

3104 DC020001 F PF La Bass 

3104 DC020002 F UB Carp 

3105 DF025001 F UB Carp 

3105 DFO25002 F PF Lm Bass 

3106 DE026801 F PF UaLleye 

3107 DE026901 F UB Carp 

31011 DE027001 F PF Ualleye 

3108 DED27002 F UB Carp 

3109 DE025001 F UB Carp 

3110 DE022501 F BF Carp 

3111 DHOl5802 F UB Silver Redhorse 

3112 DED224Dl F UB Carp 

DXY 

CHLDR 

ND 

:53 

Jm 

ND 

ND 

ND 

ND 

ND 

Y) 

ND 

L 

ND 

ND 

m 

w 

ND 

w 

m 

11.7 

ND 

21.5 

w 

ND 

In 

ND 

7.29 

w 

?53 

YD 

w 

ND 

7.921 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CJS TRAYS HEPT 

NDN NON 

w ND ND 

ND ND ND 

18.8 53.8 ND 

ND w w 

ND ND w 

m ND 

m 2.29 D: 

ND Y) m 

m ND Y) 

Y) ND ND 

1.58 0 3.17 yo 

m 

13.8 

ND 

ND 

m 

m 

it.5 

a.64 

40.6 

z.6 

ND 

ND 

w 

w 

0.19 

ND 

w 

w 

ND 

m 

ND 

16.0 

ND 

w 

w 

ND 

m 

ND 

ND 

ND 

ND 

m 

1.12 D t0 

28.9 ND 

0.98 DU 

YD ND 

m ND 

UJ 

1.29 0; 

No 

i&4 m 

126 ND 

3.70 

162 E: 

5.42 ND 

7.65 Mi 

5.45 ND 

ND m 

19.0 ND 

ND ND 

11.811 m 

12.9 ND 

40.69 ND 

ND w 

7.66 w 

50.7 ND 

8.32 E ND 

w w 

ND 

&B ND 

ND ND 

2.40 D ND 

10.2 ND 

4.36 ND 

10.8 ND 

3.47 ND 

HEPT 

EP 

ND 

w 

w 

ND 

ND 

ND 

ND 

ND 

w 

ND 

0.80 

ND 

2.17 

ND 

m 

w 

w 

ND 

w 

ND 

ND 

w 

w 

m 

ND 

m 

w 

2.10 

ND 

Ml 

1.18 

ND 

w 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DDE DlELDRJN EllOilN--6ICOFOL ME 

86.11 ND 

14.97 ND 

48.6 25.1 

ND 

E.4 ND 

8.92 ND 

35.8 W 

6.89 ND 

2.09 D Y) 

2.46 OND 

20.8 3.97 

1.48 DND 

52.7 9.89 

33.1 0.51 

40.93 a.34 

0.81 D Y) 

0.76 0 W 

5.51 

984 E:.5 

322 20.3 

2329 E 64.9 

34.38 6.89 

1189 EY) 

77-R Y) 

114 ND 

70.09 w 

224 E YD 

D 551 E 11.7 

284 EY) 

18.61 7.47 

D 18.8 13.1 

164.92 7.69 

152.61 ?37 

81.6 E 29.4 

1448 E ND 

75.9 END 

5.57 ND 

22.99 1.73 

2.06 DND 

22.81 ND 

136 END 

91.5 E 7.73 

60.6 a.60 

53.5 5.15 

ND ND 

ND ND 

1.65 D ND 

w 

4.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DW 

12.25 

ND 

ND 

w 

w 

ND 

w 

ND 

yo 

ND 

5.63 

ND 

ND 

ND 

ND 

ND 

ND 

m 

ND 

w 

4.45 

ND 

No 

ND 

D ND 

ND 

JtD 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

w ND 

No ND 

ND NJI 

No ND 

ND NJJ 

ND tm 

NJJ ND 

ND ND 

ND ND 

w In 

ND w 

ND ND 

ND ND 

ND ND 

10.4 ND 

:69 

ND 

ND 

ND w 

ND ND 

Y) ND 

ND ND 

ND ND 

ND ND 

w 3.40 

ND ND 

ND 

In ::21 

1.13 I DND 

NJI ND 

ND ND 

4.66 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

2.44 D ND 

CHL 

PERTHANE MJREX NJTROFEN CHLDR I SOPROP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

?12 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.93 

ND ND 

ND NO 

2.45 D W 

ND ND 

0.99 DND 

ND ND 

0.68 DND 

3.68 ND 

ND ND 

ND ND 

0.52 D ND 

ND ND 

0.57 D Ml 

No ND 

0.71 D Yo 

NO ND 

ND ND 

0.29 DND 

No w 

No ND 

:01 

ND 

1.1111 D: 

0.21 D NO 

ND ND 

ND ND 

ND w 

ND ND 

NJJ ND 

ND w 

ND ND 

ND ND 

ND ND 

0.63 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

:D% w 

Nil MD 

0.47 D ND 

D 2.98 ND 

PYRIFDS 

ND ND 

w ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

No ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.82 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

19.8 ND 

a.95 ND 

19.4 ND 

2.50 ND 

23.0 w 

ND ND 

yo ND 

ND ND 

ND ND 

2.09 DND 

yo ND 

ND ND 

ND ND 

I.% D ND 

ND ND 

ND ND 

14.0 ND 

ND ND 

ND ND 

w ND 

ND ND 

ND ND 

w ND 

w ND 

ND ND 

2.19 D ND 

ND ND 
episode SCC Type Description 

3112 DE022402 F PF UatLeye 

3113 DE021101 F BF Chamcl Catfish 

3113 DE021102 F BF Carp 

3113 PDO30789 F BF Channel Catfish 

3114 DE021201 F BF Carp 

3115 DE021302 F BF Catfish 

3115 a0101689 L UB Carp 

3115 DE021301 F UB Carp 

3117 DEOZISOl F PF Lake Trout 

3118 DE021601 F PF Ualleye 

3118 DEOZl602 F UB Carp 

3118 DE021603 F UE Carp 

3118 PDOlO689 L UB Cam 

3118 PDO2048B L PF Ualieye 

3120 DE021801 F UB Carp 

3120 DE021802 F PF Bass 

3122 DE022001 F UB Carp 

3122 DE022003 F UB Redhorse Sucker 

3125 DE022301 F UB Carp 

3125 DE022302 F PF Uhite Bass 

3132 DE023201 F UB Carp 

3132 a0010588 L UB Carp 

3134 DE023403 F UB Carp 

3134 DE023405 F UB Carp 

3134 DE023406 F UB Sucker 

3135 DE023501 F UB Carp 

3136 DE023601 F PF Northern Pike 

3137 DE023701 F UB Rcdrorse Sucker 

3138 DE023801 F UB Cam 

3140 DE024001 F PF Uatieye 

3140 DE024002 F UB Carp 

3141 DE024101 F PF Northern Pike 

3141 DE024102 F UB Carp 

3141 DE024103 F PF Northern Pike 

3142 DE022502 F UE Cam 

3143 DE024401 F Rotien (cetf I 

3143 DE024403 F UB Carp 

3144 DE024901 F UB Carp 

3145 DEOZ&O? F UB N. Redhorse 

3146 DE026701 F UB Carp 

3146 DE026702 F PF Ualleyc 

3147 DC035201 F UR Carp . 

3148 DE027101 F UB Carp 

3148 DE027103 F PF UalLeye 

3149 DC038501 F UB Uhite Sucker 

OXY 

CHLDR 

L3 

9.75 

5.24 

11.9 

9.74 

:“6 

87.2 

3.90 

ND 

ND 

ND 

5.00 

::65 

ND 

ND 

ND 

ii.82 

25.93 

ND 

14.5 

NO 

ND 

ND 

ND 

ND 

ND 

it.0 

ND 

13.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CJS 

NDN 

L3 

25.3 

5.95 

23.7 

ND 

ND 

ND 

127 

9.25 

14.6 

3.51 

16.2 

10.4 

ND 

ND 

10.5 

ND 

ND 

K37 

48.02 

LB 

ND 

ND 

ND 

ND 

4.02 

ND 

ND 

18.6 

21.8 

9.40 

25.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

17.1 

7.70 

ND 

TRAMS HEPT 

NDN 

ND ND 

13.9 ND 

78.0 ND 

15.0 ND 

60.1 ND 

47.7 ND 

47.4 ND 

48.1 

350 E :: 

22.3 ND 

36.6 ND 

9.62 ND 

40.1 ND 

28.7 ND 

7.22 ND 

5.30 ND 

28.7 ND 

1.73 D ND 

ND ND 

2.66 

106.17 :i 

133.24 ND 

3.14 ND 

12.1 ND 

:41 

NO 

ND 

ND ND 

ND ND 

11.6 ND 

::: 

D ND 

ND 

57.3 END 

63.2 ND 

27.9 ND 

81.5 ND 

ND ND 

7.64 ND 

9.34 ND 

3.80 ND 

15.1 ND 

:i 3 

ND 

*a:0 

ND 

NO 

15.7 ND 

26.5 ND 

XENOBJOTICS COWCENTRATJDNS, rig/g 

HEPT DDE DJELDRIN ENDRJN DJCOFOL ME 

EP 

ND 

ND 

ND 

ND 

25.8 

10.2 

9.95 

ii.7 

0.84 

ND 

ND 

:97 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

29.5 

ND 

ND 

1.86 

ND 

ND 

ND 

ND 

NO 

0.67 

ND 

4.69 ND ND 

130 E 11.1 ND 

1003 E ND ND 

133 E 10.3 ND 

46.6 187 E ND 

104 E 55.3 ND 

73.3 52.1 ND 

76.6 1891 E 405 5.8 E :: 

145 12.2 

814 E 17.7 

181 ND 

895 E 19.5 

la0 16.0 

48.71 11.09 

35.60 4.36 

450 E ND 

10.70 NO 

136 54.0 

30.6 5.17 

50.71 83.39 

63.70 69.62 

22.2 2.80 

74.4 E ND 

33.8 ND 

59.1 8.62 

0.94 D ND 

6.86 0 ND 

85.6 4.15 

14.8 ND 

42.5 ND 

291 E 50.0 

564 E 63.8 

137 E 29.9 

658 E 228 

29.5 ND 

34.49 4.04 

137 23.9 

17.5 4.22 

100 16.5 

1.78 D ND 

79.2 15.8 

282 E 4.51 

85.7 9.37 

289 15.6 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

Lo 

3.07 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND No 

ND NO 

ND ND 

14.9 NO 

ND ND 

ND ND 

ND 0.64 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

1.51 D ND 

ND ND 

PERTHANE MJREX NJTRDFEN CHLDR I SDPRDP 

PYRJ FOS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 1.R D ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND 7.71 ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND NO 

ND 

1.71 D :: 

ND ND 

ND 

ii.3 ND 

ND ND 

ND ND 

7.06 ND 

0.32 D NO 

1.88 D ND 

0.64 D NO 

2.24 D ND 

0.27 D ND 

ND ND 

ND 

?32 NO 

ND ND 

ND ND 

0.70 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

1.16 D ND 

2.90 

0.34 D :: 

ND ND 

WD ND 

ND ND 

ND 

0.48 D !5 

1.52 D ND 

ND ND 

ND ND 

ND ND 

0.29 D ND 

ND ND 

ND 

6.92 

7.23 

7.40 

ND 

12.8 

7.22 

7.44 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

:!61 

ND 

ND 

w 

ND 

r.8o 

ND 

ND 

ND 

NO 

ND 

62.7 

ND 

5.23 

ND 

ND 

ND 

ND 

ND 

No 

ko 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

D ND 

ND 

ND 

NO 

ND 

NO 

D ND 

ND 

NO 

ND 

ND 

ND 

END 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

NO 

ND 

ND 

D-S-26 
Episode SCC Type Description 

3150 DA0089Dl F UB Uhite Sucker 

3150 POtMIST L UB Nhite Sucker 

3151 DA000101 F UB Uhite Sucker 

3152 DAOD9201 F UB Uhite Sucker 

3161 DC819801 F BF BLack Bullhead 

3161 DC019802 F UB Uhite Sucker 

3162 DJ024Wl F UP Starry Flouder 

3163 DJOZCOCJZ F UP Starry Flow&r 

3164 DD0157D2 F UB Carp 

3165 WOl5704 F W Rcdhorse Sucker 

3166 WO15706 F UB Uhite Sucker 

3167 DD015708 F LIP Bluegill 

3167 WO62388 L UP BLuegill 

3168 WOl5711 F UB Carp3168 DD015712 F PF Lm Bass 

3169 DDOl5713 F UB Black Rcdhorse 

3169 a0022789 L UB Black Redhorse 

3170 WOl5715 F UB Spotted Sucker 

3171 DDOl5717 F UB Spotted Sucker 

3172 DD015719 F UB Carp 

3lR DDOlSRO F PF Lm eass 

3173 DDOISRZ F UB charnel Catfish 

3174 DDOlSR4 F UB Channel Catfish 

3175 DDOl5801 F UB Chamel Catfish 

3176 WOl5803 F UB Spotted Sucker 

3177 WOl5805 F UB Carp 

3177 00100488 L UB Carp 

3178 DDOl5807 F UB North Hogsucker 

3179 WOl5809 F UB Golden Redhorse 

3lJM WO15812 F PF Lm Bass 

3181 WOl5814 F UB Carp 

3182 WOl5815 F PF Rock Bass 

3182 W015816 F UB Carp 

3183 WOl5817 F UB Carp 

3183 DDOl5818 F PF Sauger 

3184 DDOl5820 F PF Uhite Crappie 

3185 DDOl5821 F UB Channel Catfish 

3186 DDO15824 F UP Southern Flow& 

3187 DDO15902 F UP Sumwr Flwnder 

318B 00015903 F UB Carp 

3188 Do015904 F PF Lm Bass 

3189 DDO15905 F UB Carp 

3189 a0092188 L UB Cerp 

3190 Do015907 F IJB Carp 

3191 DJO24W3 F Yp Starry FLouder 

OUY 

CHLOR 

a.64 

9.45 

ND 

r33 

29.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

Jm 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::37 

::ss 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?51 

Lo 

ND 

ClS 

NOW 

ND 

ND 

ND 

ND 

ND 

47.2 

ND 

ii.1 

16.4 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NJI 

ND 

ND 

ND 

9.12 

ND 

ND 

ND 

ND 

ND 

NO 

D 3.82 

Z.0 

ii.9 

27.7 

ND 

ND 

19.2 

ND 

::.5 

ND 

14.0 

18.3 

11.1 

ND 

TRAMS HEPT 

NON 

7.32 ND 

7.63 ND 

7.93 ND 

ii.72 : 

161 ND 

4.39 1.57 D : 

104 ND 

52.3 ND 

ND ND 

1.75 DND 

2.64 ND 

2.80 ND 

ND 

?93 NO 

5:71 ND 

3.51 ND 

3.53 ND 

9.08 ND 

ND ND 

13.4 ND 

3.15 ND 

8.60 ND 

3.54 ND 

7.82 ND 

7.10 ND 

1.95 D ND 

15.4 ND 

ND 242 E : 

1.38 D NO 

94.2 E NO 

94.9 76.2 

2.39 D NO 

ND 

z.7 ND 

1.01 D ND 

ND ND 

130 E ND 

1.83 D ND 

42.6 ND 

55.5 ND 

a.1 ND 

ND ND 

XENDBIOTJCS CDNCENTRATJDNS. r&g 

HEPT 

EP 

ND 

ND 

ND 

Lo 

36.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?55 

ND 

ND 

END 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.83 

ND 

DDE DJELDRJN ENDitJN DJCOFOL ME 

CHL 

19.1 3.36 ND 

18.4 3.43 ND 

26.2 5.83 2.36 175 D :D63 

26.38 63.26 Ni 

114 450 

21.0 ND 

4.84 0.28 

Ill 32.2 

35.5 4.76 

79.9 ND 

15.2 ND 

21.9 ND 

SW E ND 

65.4 E ND 

384 END 

335 E ND 

104 EN0 

48.6 ND 

638 E ND 

32.1 ND 

55.0 785To7 

55.9 E 3.74 

82.2 E ND 

33.0 1.95 

30.8 1.89 

9.37 38.6 rw 

13.1 ND 

121 E 57.3 

3.16 

87.7 E ::.I 

38.8 13.5 

2.00 D ND 

27.3 ND 

41.9 17.6 

4.70 ND 

3.75 162 E ::O 

2.85 ND 

148 E 29.6 

203 E 47.6 

31.6 8.39 

0.89 D ND 

ND 

ND 

D ND 

ND 

4.73 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

D ND 

D ND 

ND 

ND 

ND 

ND 

Es3 

ND 

Jm 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

:92 

D ND 

ND 

8.16 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

L 

0.89 

ND 

ND 

ND 

ND 

ND 

0.50 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

56 

ND 

ND 

ND 

ND 

ND 

NJI 

ND 

ND 

No 

ND 

D ND 

DND 

ND 

a”15 

Nii 

ND 

DND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

!I!27 

PERTHANE MJREX NJTROFEN CHLDR J SDPRDP 

PYRJFOS 

NO 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DND 

ND 

:69 D ND 

6.09 

4.22 

ND ND ND 

ND ND 

ND ND ?35 

ND 

:!SO 0 NO 

13.6 

ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

4.96 2.04 D ND 

ND ND ND 

11.3 ND ND 

10.8 ND ND 

0.21 D ND ND 

0.28 D ND ND 

3.26 ND ND 

0.36 D ND ND 

ND ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

10.2 

ND ND 1.90 D ND 

73.2 END ND ND 

1.47 D ND ND ND 

0.30 D ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

1.39 D ND ND ND 

5.89 ND ND ND 

ND 0.65 D ND ND 

ND ND ND ND 

1.89 D ND 1.39 D ND 

ND 

ND 

6.88 

ND 

ND 

3.68 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

19.2 ND 

ND ND 

No ND 

ND ND 

ND ND 

ND 

ND :32 D 

ND ND 

ND ND 

D-S-27 
Episode SCC Type Description 

3191 DJO24W5 M Soft Shell CLams 

3192 DJO24W7 F UP Starry Flcmder 

3192 DJO24009 M Soft Shell Clams 

3193 DC039001 F PF Striped Bass 

3195 DHOZOlD4 F W Carp 

3195 DHO20105 F W Chub 

31% DH020108 F W Sucker 

3198 DHO20111 F W Sucker 

3199 ON020101 F W Carp 

3199 DH020103 F W Cam 

3200 DHO !0112 F W Sucker 

3203 DJO !4018 F W Carp 

3205 DJO !4024 H Crayfish (whole) 

3206 DJO !4103 F W Sucker 

3208 DJO !41W F W Sucker 

3212 DJO 14120 F BF Catfish 

3212 DJO !4121 F W Carp 

3213 DJO !4123 F W Squawfish 

3215 DJO !3705 F W Sucker 

3216 DJO !3707 F PF Sqwwfish 

3216 DJO !3708 F W Sucker 

3216 QDO !2388 L W Sucker 

3217 DJO 13710 F W Sucker 

3218 DJO 13711 F PF Squewfish 

3219 DJO 13713 F W Uhite Sturgeon 

3219 DJO23714 F PF White Sturgeon 

3220 05023903 F W BrideliD Sucker 

3221 05023905 F W Suck& ’ 

3222 05023907 F W Sucker 

3223 05023717 F UP Starry Flomder 

3224 DJO23715 M Soft Shell Clam 

3226 DJ023Rl M Pacific Oysters 

3227 05023123 M Pacific Dysters 

3231 DJ023910 F PF Sm Bass 

3231 DJD23911 F W Carp 

3234 DHO20301 F UP Squawfish 

3235 DHO20303 F W White Sucker 

3236 DHO20305 F W Largescale Sucker 

3237 OH020308 F W Largescale Sucker 

3237 DDO80988 F W Largescale Sucker 

3238 DJ023918 F Up Dolly Varden 

3241 DJ023924 F UP Dolly Varden 

3245 DJO23624 F W Flatheed Sole 

3246 05022109 F W Flathead Sole 

3248 DJO22502 F W C-site Bottom 

OXY 

CHLDR 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.93 

ND 

3.75 

ND 

ND 

ND 

ND 

5.56 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CJS 

NON 

ND 

ND 

ND 

15.4 

5.16 

10.6 

ND 

4.36 

6.26 

6.77 

!?4* 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

TRAMS HEPT 

NON 

ND ND 

ND ND 

ND 

::.8 ND 

16.4 ND 

33.4 ND 

1.38 D ND 

14.7 ND 

21.3 ND 

20.2 ND 

10.9 ND 

14.4 ND 

ND ND 

ND ND 

13.4 ND 

4.54 ND 

24.7 ND 

ND 

ii.3 ND 

1.58 D ND 

ND ND 

ND ND 

NQ 

?67 ND 

20.1 ND 

1.88 D ND 

NO ND 

15.8 ND 

4.45 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

23.9 ND 

7.32 ND 

1.81 V ND 

ND ND 

ND ND 

ND 

1.17 D :i 

4.57 ND 

ND ND 

ND ND 

ND ND 

XENOBJOTJCS CDNCENTRATJDNS, rig/g 

HEPT DDE DJELDRJN ENDRJN DJCOFOL ME PERTHANE MJREX NITROFEN CHLDJJ I SDPRDJ’ 

EP CHL PYRJFOS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?62 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

35.4 24.7 

78.8 33.5 

39.9 11.5 

200 79.2 

333 E 12.4 

0.58 D ND 

37.1 ND 

1142 E 88.0 

517 E 74.3 

3214 E 182 

43.5 ND 

463 E 37.3 

34.3 ND 

80.9 ND 

89.8 ND 

35.8 ND 

52.0 ND 

797 E ND 

136 END 

107 ND 

SW E ND 

89.2 E ND 

1.46 D ND 

1.00 ND 

1.50 D ND 

7.21 ND 

63.6 E 5.32 

2493 E 103 

44.3 ND 

16.9 ND 

15.7 ND 

13.0 ND 

1.04 DND ND 

1.44 D ND ND 

::I 

ND ND 

E 9.76 ND 

84.4 E 18.5 ND 

225 E 27.6 ND 

11.8 1.97 D ND 

ND 

ND 

ND 

26.5 

ND 

ND 

ND 

ND 

E ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

12.7 1.40 D ND 

7.94 ND ND 

50.5 ND ND 

5.29 ND NO 

I.80 D ND ND 

32.9 ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

21.1 

ND 

:“29 

ND 

ND 

ND 

18.4 

11.6 

ND 

ND 

9.91 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3.44 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

No ND 

ND ND 

ND 

2.5 ND 

393 E ND 

ND ND 

2.55 ND 

ND ND 

ND ND 

DND ND 

ND ND 

ND ND 

ND 

?42 ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.39 D ND 

ND ND 

ND ND 

0.56 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND No 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.39 D ND 

ND ND 

ND ND 

0.94 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.26 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.51 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

ND 

ND 

ND 

7.08 

15.4 

2.51 

26.5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.36 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3.44 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

D-s-2.8 
Episode SCC Type Description 

3248 90050588 F W not available 

3249 05022503 F PF Brook Trout 

3249 DJ022504 F W Sucker 

3250 DJO22506 F W Sucker 

3252 DJO225W F PF Lm Bass 

3252 05022510 F W Sucker 

3252 ODO2W89 L PF Lm Bass 

3252 00052588 L W Sucker 

3256 DJ022518 F W Sucker 

3258 DC038901 F PF Spot 

3258 DC038902 F W Croaker 

3259 DB000466 F W Goldfish 

3259 DB000473 F PF Lm Bass 

3259 DBO69101 F W Sucker 

3260 DB000493 F W Carp 

3261 DYO26DO2 F W Striped Mullet 

3262 01026004 F W Tilepia Tilapia 

3266 DYO22701 F PF Black Crappie 

3266 DY022702 F W Channel Catfish 

3266 DDO12389 L PF Black Crappie 

3267 DYO22lOl F PF Rainbow Trout 

3267 DYO22102 F W Sacramento Sucker 

3270 DY022108 F W Sucker 

3271 DYO22110 F W Sucker 

3272 DYO22112 F W Uhite Surfperch 

3273 DYO22113 F W Sculpin 

3273 DY022114 F W Surf Smelt 

3274 DYO22116 F W Sculpin 

3276 (31022119 F W Ualleye 

3278 DY022124 F W Sacramento Sucker 

3281 DY022205 F W Sucker 

3282 DY022206 F PF Flathead Catfish 

3282 DYO22207 F W Carp 

3283 DYO222W F W Carp 

3285 DY022212 F UP Stingray 

3285 DY022213 F W Diamond Turbot 

3286 DY022215 F W Carp 

3287 01022216 F W Tilapia Zilli 

3288 DY022217 F PF Squawfish 

3288 DY022218 F W Sucker 

3289 DY022219 F UP Bocaccio 

3289 DY022220 F W Sculpin 

3290 DYO2222l F PF Redear Sunfish 

3290 DY022222 F W Blackfish 

3294 DJO22Ill F UP True Cod 

OXY 

CHLDR 

ND 

ND 

ND 

ND 

ND 

4.39 

ND 

ND 

ND 

::33 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

14.3 

ND 

ND 

ND 

ND 

iDI4 

ND 

ND 

ND 

19.2 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CJS 

NON 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:!26 

ND 

ND 

ND 

ND 

44.7 

5.66 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

83.2 

22.2 

25.7 

a.94 

ND 

ND 

ND 

ND 

ND 

15.6 

ND 

TRAMS HEPT 

NON 

ND ND 

ND ND 

ND ND 

6.36 ND 

ND ND 

23.7 ND 

ND ND 

20.3 ND 

3.69 ND 

19.66 ND 

13.9 ND 

11.6 ND 

ND ND 

14.1 ND 

ND ND 

88.2 ND 

10.9 ND 

ND ND 

10.9 ND 

ND ND 

1.71 D ND 

2.78 ND 

4.57 ND 

ND ND 

16.0 NO 

1.11 D ND 

ND ND 

ND ND 

ND ND 

11.6 ND 

7.21 ND 

10.9 ND 

36.8 ND 

9.27 ND 

140 E ND 

43.5 606E :: 

25.5 ND 

3.63 ND 

16.6 ND 

ND ND 

5.16 ND 

ND 

tk3 ND 

ND ND 

XENDBJOTJCS CONCENTRATJDNS. no/a 

HEPT 

EP 

DDE DJELDRJN ENDRIM-.iJCOFOL ME 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

31.7 ND 

I.99 D ND 

7.37 ND 

60.6 E 4.00 

84.0 E 5.50 

848 E 56.8 

62.1 E 3.77 

1061 E 56.1 

117 10.8 

58.31 14.99 

45.8 16.8 

94.2 ND 

5.37 ND 

202 54.0 !?*I 

144 E 41.2 

48.8 ND 

54.8 E ND 

2090 E ND 

77.1 E ND 

3.90 ND 

10.4 ND 

53.8 ND 

3.10 ND 

805 E 260 

11.7 ND 

4.34 ND 

1.65 D ND 

7.23 ND 

73.2 E ND 

80.4 E 1.21 

2820 E 44.0 

8708 E 188 

772 END 

10.9 21.9 

10149 E :: 

45.7 4.12 

1433 E 174 

1484 E 161 

95.3 5.07 

172 E 6.78 

13.3 ND 

997 E ND 

9.46 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

16.2 

ND 

ND 

ND 

ND 

ND 

D ND 

13.8 

E 45.4 

ND 

ND 

ND 

ND 

ND 

E 7.39 

16.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.58 

24.3 

1.49 

36.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.93 

5.13 

ND 

ND 

ND 

ND 

ND 

ND 

11.8 

ND 

ND 

ND 

ND 

1.37 

ND 

CHL 

ND 

ND 

ND 

ND 

D ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

&6 

ND 

ND 

ND 

ND 

D ND 

ND 

PERTHANE HJREX NJTROFEN CHLDR I SOPRDP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D 0.29 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.87 D ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.48 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

D ND !i"os 

ND 3.17 

ND ND 

ND ND 

ND ND 

0.88 D ND 

ND ND 

PYRJFOS 

ND 

ND 

ND 

ND 

ND 

7.18 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

78.7 

344 

61.7 

ND 

ND 

5.12 

3.40 

ND 

ND 

ND 

ND 

F.22 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E ND 

E ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

D ND 

ND 

D-5-29 
Episode SCC Type Description 

3294 DJO22113 n Husse J 

3295 DJ022114 F UP Atlantic Salmon 

3296 DB040101 F W Uhite Sucker 

3297 DBO41501 F W Carp 

3298 DBO41601 F W Carp 

3298 OBO41604 F PF Lm Bass 

3299 DE040601 F W Uhite Sucker 

3299 DBO40604 F PF Lm Bass 

3299 PO040601 L W Sucker 

3300 DE040201 F W Uhite Sucker 

3300 DB040204 F PF Sm Bass 

3300 90021389 L W Channel Catfish 

3301 DB041101 F W Carp 

3301 DBO41104 F PF Northern Pike 

3301 CtDO3W89 L PF Northern Pike 

3302 DE041001 F W Uhite Sucker 

3302 DBO41W4 F PF Lm Bass 

3303 DE042301 F W Uhite Sucker 

3303 08042304 F PF Sm Bass 

3303 90102588 L W Uhite Sucker 

3304 DB041001 F PF Northern Pike 

3304 DBO41004 F W Uhite Sucker 

3304 QDO41004 L W Uhite Sucker 

3305 DE042001 F W ChenneL Catfish 

3305 08042004 F PF Sm Bass 

3305 OD11038B L W Channel Catfish 

3306 DBO41801 F W Uhite Sucker 

3306 DBD41804 F PF Sm Bass 

3306 oDO41801 L W Uhite Sucker 

3307 DBO42101 F W White SuEker 

3308 DBO40001 F PF Northern Pike 

3309 08041301 F W Uhite Sucker 

3310 DC032701 F W Bullhead 

3310 DC032702 F PF Ualleye 

3311 DC032801 F W Redhorse Sucker 

3311 DC032802 F PF Sm Bass 

3312 DC033101 F W Redhorse Sucker 

3312 DC033102 F PF Sm Bass 

3313 DC033201 F W Redhorse Sucker 

3313 DC033202 F PF Sm Bass 

3314 DC033301 F W Channel Catfish 

3314 DC033302 F PF Uhite Bass 

3315 DC033401 F W Carp 

3315 DC033402 F PF Lm Bass 

3316 DC033501 F W White Sucker 

OXY CJS 

CHLOR NON 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

9.83 

ND 

ND 

ND 

ND 

ND 

7.89 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

36.1 

ND 

43.3 

ND 

ND 

::02 

ND 

ND 

ND 

:“96 

ND 

ND 

1.99 

3.33 

2.03 

9.51 

1.93 

2.41 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

10.9 

ND 

ND 

23.3 

ND 

ND 

18.7 

ND 

ND 

ND 

ND 

ND 

ND 

6.29 

29.0 

ND 

28.9 

ND 

ND 

55 

ND 

ND 

ND 

ND 

4.54 

ND 

20.3 

ND 

6.35 

ND 

50.9 

D 7.53 

D ND 

ND 

ND 

TRAMS HEPl 

NON 

ND ND 

1.22 D ND 

6.99 ND 

9.59 ND 

29.2 ND 

0.83 D ND 

27.1 ND 

3.63 ND 

17.6 ND 

26.7 ND 

4.97 ND 

3.80 ND 

68.7 ND 

3.03 ND 

3.69 ND 

39.4 ND 

2.16 D ND 

ND ND 

ND ND 

ND 

::04 D ND 

8.03 ND 

16.1 ND 

77.1 ND 

ND ND 

77.2 ND 

3.93 ND 

1.53 D ND 

5.90 ND 

5.98 ND 

ND ND 

ND ND 

30.8 ND 

ND 0.28 

13.2 ND 

3.95 ND 

53.9 ND 

12.83 ND 

26.4 ND 

4.16 ND 

185 E ND 

24.1 ND 

22.1 

2.08 D :: 

1.84 D ND 

KENOBJOTICS CONCENTRATIONS, rig/B 

HEPT 

EP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

N 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.51 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

5.17 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DDE DJELDRJN ENDRJN DJCDFOL ME 

D ND ND 

ND ND 

13.7 ND 

19.8 ND 

E 22.4 ND 

ND ND 

E 19.3 ND 

3.69 ND 

E 14.6 ND 

E 18.1 ND 

2.53 ND 

1.65 D ND 

E 85.4 

0.38 

31.0 

43.6 

58.2 

202 

11.5 

141 

21.7 

106 

267 

41.4 

30.9 

1005 

29.9 2.64 

35.5 3.86 

509 E 25.8 

19.8 ND 

31.0 ND 

1.81 D ND 

10.7 ND 

20.7 ND 

115 E ND 

207 E 12.5 

602 E 43.0 

9.75 ND 

607 E 42.9 

42.1 12.9 

13.5 ND 

63.4 12.6 

78.8 E 5.55 

2.49 D ND 

15.2 4.05 

100 E 12.4 

12.4 4.50 

6.28 3.74 

1.51 D 1.18 D ND 

22.6 5.69 ND 

5.33 4.55 ND 

200 E 7.75 ND 

19.48 ND ND 

51.7 19.6 118 

10.0 4.79 4.54 

14028 E ND ND 

915 ND ND 

3.92 ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CHL 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.95 D ND 

ND ND 

ND 

!!71 ND 

0.36 D NO 

0.57 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

PERTHANE HJREX NJTROFEN CHLDJf I SOPROP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND 

!?57 D ND 

2.78 0 ND 

ND ND 

ND 

0.75 D 1: 

0.28 D ND 

1.29 D ND 

37.9 12.8 

7.91 ND 

6.03 ND 

ND 

?i; NO 

6:87 ND 

65.6 10.6 

3.63 ND 

ND ND 

ND ND 

ND ND 

7.25 ND 

12.7 ND 

18.1 ND 

135 ND 

2.25 D ND 

137 ND 

5.53 ND 

4.10 ND 

8.84 ND 

18.8 ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.57 D ND 

0.18 D ND 

1.36 D ND 

1.14 D ND 

0.83 D ND 

ND ND 

ND ND 

0.22 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

12.0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

14.0 ND 

4.29 ND 

5.29 ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.34 D ND 

0.93 D ND 

ND ND 

2.86 ND 

1.23 D ND 

1.12 D ND 

ND ND 

17.2 

2.40 D w”: 

ND ND 

ND ND 

ND ND 

PYRJFOS 

D-S-30 
Episode SCC Type Description 

3317 DC033601 F W Uhite Sucker 

3318 DC033701 F W Uhite Sucker 

3319 DB041401 F UP Uinter Flder 

3320 DBO41412 F UP Bluefish 

3321 DE040401 F Up Uinter Flounder 

3321 QD1006J38 L UP Uinter Flcunder 

3323 DBO41206 F UP Uinter Flour&r 

3324 DB041252 F UP Bluefish 

3325 DB041218 F UP Bluefish 

3326 DE041208 F up BLuefish 

3327 DBO40301 F UP Bluefish 

3327 DE040315 F VP Bluefish 

3328 DDO29111 F W Carp 

3329 DD016003 F W Bwfin 

3330 DD029110 F W Spotted Sucker 

3331 DD016007 F W Carp 

3332 DD016OW F UP Spotted Drun 

3333 DDO16012 F W Sea Catfish 

3334 DDO16013 F W Sea Catfish 

3335 DD016015 F UP Spot 

3335 DDO29101 F UP Red Drun 

3335 DD029102 F W Southern Flounder 

3335 00029103 F Up She-head 

3335 POW1588 L UP Red Drun 

3336 Do016004 F UP Black Drun 

3336 DDO16006 F UP Sheepshead 

3336 DD016017 F UP Red Drun 

3336 DD016018 F PF Spotted Seatrout 

3337 DDO16019 F W Spotted Sucker 

3338 DD016022 F W Spotted Sucker 

3339 DDO16023 F W Carp 

3340 DD029114 F W Channel Catfish 

3341 DD016104 F W Catfish 

3341 00081788 L W Catfish 

3342 DDO16105 F W Spotted Sucker 

3343 DD016107 F W Uhite Sucker 

3344 DD0161W F W Carp 

3345 DDO16111 F W Redhorse Sucker 

3346 DD016113 F W Creek Chubsucker 

3346 DDO16114 F PF Lm Bass 

3347 DD016115 F W Carp 

3348 DD016117 F PF vhi te Perch 

3348 DD016118 F W Blue Catfish 

3349 DDOl6119 F W Carp 

3350 DDO16121 F W Carp 

OXY CJS 

CHLOR NON 

ND 

ND 

ND 

ND 

2.20 

2.13 

2.75 

4.56 

ND 

3.05 

ND 

ND 

ND 

!I?46 

ND 

ND 

1.70 

5.94 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:“52 

2046 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D 6.21 

D 5.47 

11.9 

4.14 

2.59 

6.11 

3.34 

t:: 

ND 

D ND 

ND 

ND 

D ND 

29.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

9.81 

19.6 

ND 

18.0 

16.2 

ND 

ND 

ND 

ND 

ND 

ND 

21.2 

ND 

ND 

1.13 D 7.86 

ND 29.6 

TRAMS HEPT 

NON 

ND 

:D56 ND 

li.5 ND 

12.3 ND 

20.6 ND 

20.9 ND 

39.4 ND 

8.77 ND 

7.12 ND 

14.6 ND 

8.90 ND 

17.1 ND 

18.2 ND 

ND ND 

6.59 ND 

ND ND 

ND 

?03 ND 

6j.O ND 

ND ND 

1.45 D ND 

1.12 D ND 

2.19 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 

:!.9 ND 

ND ND 

41.8 ND 

38.7 ND 

41.0 ND 

5.42 ND 

42.0 ND 

14.4 ND 

3.62 ND 

ND ND 

76.4 E ND 

::50 ND 

17.0 ND 

89.3 ND 

HEPT 

EP 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.46 

ND 

DDE DJELDRJN ENDiJN-.oJCOFOL ME 

CHL 

is.2 ::93 

25.8 14.1 

42.9 4.52 

26.2 12.1 

26.4 9.85 

29.5 8.18 

27.3 9.74 

15.9 2.78 

29.0 8.90 

46.2 4.82 

43.8 8.41 

247 E ND 

2.07 D 4.25 

15.1 1.84 

8.31 ND 

11.9 ND 

51.2 254 E :: 

6.32 37D ::76 

6.03 ND 

5.83 220D :: 

1.13 D ND 

3.49 1.71 D :: 

ND 

18.2 ?.46 

ND ND 

95.5 E 30.7 

15.9 7.75 

288 E 16.7 

265 E 14.3 

207 E 22.0 

9.57 229 E ii.4 

106 E 3.50 

17.7 ND 

4.45 178 E /: 

3.85 0.96 

13.8 6.06 

242 E 7.18 

146 E 47.0 

ND 

ND 

ND 

ND 

ND 

4.24 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?45 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?.39 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.53 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

PERTHANE HIREX NJTROFEN CHLOR I SOPROP 

PYR I FOS 

ND 

ND 

ND 

ND 

:!72 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.52 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND ND 

ND ND 22.3 

ND ND ND 

ND ND ND 

::30 ND 1.4561 

0.63 D ND 0.63 

ND ND 3.38 

ND ND 1.11 

ND ND 0.84 

ND ND 2.88 

0.32 D ND ND 

5.84 ND ND 

ND 

7.00 

2.39 

ND 

0.27 

a.17 

ND 

ND 

ND ND 

ND ND 

D ND ND 

ND ND 

D ND ND 

ND ND 

::51 D !: 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D 0.42 D ND 

7.22 ND 

ND 

1.41 D !! 

10.2 ND 

3.67 ND 

3.25 ND 

ND ND 

ND ND 

4.55 ND 

ND ND 

ND ND 

ND ND 

1.50 D ND 

ND 

!!27 D ND 

1.47 D ND 

ND ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.67 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.88 

ND 

ND 

0.98 

ND 

ND 

ND 

ND 

ND 

D ND 

D ND 

D ND 

ND 

D ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

D ND 

ND 

D-S-31 
Episode SCC Type Description 

3350 Do016122 F PF Lm Bass 

3351 DD016124 F W Cerp 

3352 DFD23R3 F PF Cramie 

3352 DFO23R4 F W Carp 

3352 PO022089 L PC Crawie 

3353 DF024121 F BF Bluc‘Catfish 

3353 DFO24T22 F W Sm Buffalo 

3354 DYO22 101 F W Cerp 

3354 01022 102 F PF Ln Bass 

3355 DYO22 

3355 

iO3 F W Carp 

DYO22 iW F PF Lm Bass 

33% DE030 101 F W Carp 

3357 DY022 124 F W Sacraatento Sucker 

336Owo29 17 F W Carp 

3375 Do016 05 F W Carp 

3375 DD016 1% F PF Lm Bass 

3375 90071 89 L PF Ln Bass 

3376 00016 107 F W Carp 

3376 DD016 808 F PF Lm Bass 

3377 Do016309 F W Carp 

3377 00016310 F PF Lm Bass 

3378 WOW311 F W Spotted Sucker 

3378 DDO29115 F W Greyfin Sucker 

3385 WO16401 F W Rcdhorse Sucker 

3385 PO101888 L B not available 

33% DDO 6421 F W Redtorse Sucker 

3401 DDO 6509 F W Carp 

3401 wo i6510 F PF Lm Bass 

3403 DDO 16513 F W River Carpsucker 

3403 wo 6514 F PF Lm Bass 

3404 DDO 6515 F W Carp 

3404 aD0 6515 F W Carp 

3409 DBO to701 F W Carp 

3409 DBO 10706 F PF Lm Bass 

3411 DBO .0501 F W Rcdhorse Sucker 

3412 DBO ,090l F PF Sm Bass 

3412 DBO ,09O7 F W Carp 

3414 DCD 6203 F PF Sm Bass 

3414 DC0 6206 F BF Channel Catfish 

3415 DC0 6205 F PF Sm Bass 

3415 DC0 6206 F BF Channel Catfish 

3419 DC0 6207 F W mite Sucker 

3419 DC0 6208 F PF Freshwater Drus 

3420 DC0 6209 F PF Greenfish 

3420 DC0 6210 F W Carp 

OXY CJS 

CHLOR NW 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.65 

ND 

ND 

ND 

ND 

ND 

0.88 

ND 

ND 

ND 

ND 

1.78 

ND 

ND 

ND 

2.77 

4.78 

ND 

ND 

14.4 

ND 

ND 

1.84 

26.5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

16.5 

ND 

ND 

ND 

ND 

ND 

14.1 

ii.4 

ND 

ND 

ND 

15.9 

ND 

0.38 

ND 

48.5 

ND 

123 

F.11 

ND 

6.76 

5.70 

23.7 

ND 

ND 

28.0 

Lo 

D 8.52 

25.2 

ND 

ND 

3.01 

19.2 

ND 

ND 

?45 

ND 

ND 

ND 

ND 

TRAMS HEPT 

NW 

4.21 ND 

ND ND 

ND ND 

6.17 ND 

ND 

?49 ND 

11.3 ND 

ND ND 

0.98 D ND 

53.9 ND 

2.02 D ND 

37.1 ND 

30.3 ND 

33.8 ND 

188 ND 

6.08 ND 

21.65 ND 

157 ND 

4.39 398 E :: 

13.70 No 

7.18 ND 

ND ND 

19.8 ND 

25.3 ND 

65.6 ND 

27.2 ND 

1.72 D ND 

99.8 ND 

8.36 ND 

19.2 ND 

22.0 ND 

78.0 ND 

3.17 ND 

ND ND 

6.58 ND 

47.2 ND 

ND ND 

13.4 ND 

ND ND 

20.7 ND 

9.20 ND 

4.88 ND 

4.12 ND 

11.4 ND 

HEPT 

EP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DDE DJELDRJN ENDRIN w I-- 0 JCOFDL HE 

6.27 ND 

559 E 3.30 

144 D ND 

2237 E ND 

118 E ND 

108290 E: 

835 2.29 

14.1 ND 

477 E 22.3 

22.1 

382 E ii.6 

207 20.5 

409 END 

447 E 94.1 

2.57 1.82 

a.22 7.06 

167 E 41.5 

4.30 ND 

632 E ND 

11.42 3.37 

175 E 6.77 

1% END 

17.5 ND 

18.6 ND 

174 E 28.7 

1157 ND 

68.0 E ND 

32.5 66.7 

3.40 3.97 

136 E ND 

185 E ND 

374 E 16.9 

14.3 ND 

17.2 12.3 

55.6 E 2.59 

671 E 29.3 

13.4 ND 

54.6 14.7 

8.56 ND 

81.9 11.4 

29.58 20.02 

9.47 4.78 

10.31 7.59 

36.9 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

8.80 

ND 

L3 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

CHL 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.54 0 ND 

ND ND 

1.73 D ND 

ND ND 

74.3 ND 

ND ND 

ND ND 

1.77 D ND 

ND ND 

ND 17.9 

&l3 D :: 

ND ND 

0.46 D ND 

ND ND 

1.25 D ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.19 D ND 

ND ND 

ND ND 

ND ND 

PERTHANE MJREX NJTROFEN CHLDR I SDPRCX 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

6.00 ND 

ND ND 

4.96 ND 

12.0 ND 

ND 17.9 

ND ND 

1.00 D ND 

ND 

1.45 D : 

ND ND 

10.2 ND 

14.4 ND 

ND ND 

ND ND 

20.9 ND 

ND 

ii.5 ND 

ND 

1.73 0: 

10.6 ND 

ND ND 

ND ND 

1.89 D ND 

4.83 ND 

0.21 D ND 

ND ND 

No ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

14.2 ND 

85.4 ND 

ND ND 

ND ND 

ND ND 

0.77 D ND 

ND ND 

ND ND 

1.03 D ND 

ND ND 

PYRJFOS 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

1.37 0 ND 

ND ND 

ND 

1.57 D : 

4.78 ND 

64.5 ND 

1.15 D ND 

2.72 ND 

45.6 ND 

0.90 D ND 

23.6 ND 

3.42 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

:"07 D : 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

o-5-32 
Episode SCC Type Description 

3421 DC036211 F PF Uhite Perch 

3421 DC036212 F W Carp 

3422 DC036213 F PF Lm Bass 

3422 DC036214 F W Yellow Bullhead 

3423 DC036216 F W bfhite Catfish 

3424 DC036218 F W Uhite Catfish 

3425 DFO25005 F W Carp 

3426 DE069102 F PF Bluefish 

3427 DE069103 F PF Bluefish 

3428 DE069104 F PF Bluefish 

3429 DE069105 F PF Ueakfish 

3430 DBO691D6 F W Uhite Catfish 

3431 DE069109 F W Red SnaDwr 

3433 DE069112 F UP Fbur~& 

3434 DE040801 F UP Flder 

3434 a0011889 L UP Flowder 

3435 DD016602 F W Bigncuth Buffalo 

3444 DDOl6603 F W Carp 

3444 DD016604 F BF Charnel Catfish 

3444 DD029512 F PF Lm Bass 

3445 DDO29513 F W Flounder 

3446 DDOl6605 F PF Striped Bass 

3446 DD016606 F W Carpsucker 

3446 90091889 F W Carpsucker 

OXY 

CHLDR 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

7.09 

8.39 

6.61 

ND 

ND 

10. 

1.87 

ND 

2.62 

2.52 

ND 

CJS 

ND 

ND 

ND 

::42 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3.94 

5.95 

7.09 

44.3 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

TRAMS HEPl 

NON 

3.38 ND 

ND ND 

ND ND 

ND NO 

10.3 ND 

1.75 D ND 

ND 

:“98 ND 

5:W ND 

11.6 ND 

ND ND 

7.51 ND 

5.01 ND 

8.48 ND 

14.2 ND 

20.1 ND 

115 ND 

76.4 ND 

109 END 

16.1 ND 

:“o 5 

26:9 

ND 

ND 

27.8 ND 

XENDBJOTJCS CDNCENTRATJDNS, rig/g 

HEPT 

EP 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::.7 

15.4 

10.5 

1.36 

ND 

ND 

ND 

ND 

DDE DJELDRJN ENDRJN 

2.76 ND 

22.2 13.4 

4.35 ND 

5.91 ND 

57.7 ND 

14.1 ND 

55.1 ND 

27.2 4.13 

ii.2 E ?.47 

10.2 ND 

28.7 ND 

8.33 ND 

36.8 5.05 

65.3 E 14.8 

88.1 E 16.5 

141 236 

2448 E 115 

2459 E 58.9 

28.7 14.3 

8.08 1.36 

11.1 1.22 

12.9 1.70 

13.2 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

162 

ND 

3.22 

ND 

D ND 

D ND 

D ND 

ND 

DJCOFOL ME 

CHL 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.53 

:T)83 

ND 

ND 

1.40 

0.43 

0.57 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.55 

0.88 

ND 

ND 

D ND 

D ND 

D ND 

PERTHANE MJREX NJTRDFEN CHLDR I SDPRCIP 

PYR I FDS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

0.38 D ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

0.24 0 ND 0.96 0 ND 

ND 0.24 D ND NO 

ND ND ND 

1.73 D ND :;.6 ND 

2.01 ND 21.7 ND 

3.49 ND 22.3 ND 

ND ND 1.53 D ND 

ND ND ND ND 

0.65 D ND 0.48 D ND 

ND ND ND ND 

ND ND 0.45 D ND 

D-5-33 
D-5-34 
Key for Xenobiotic Data Table (Units = rig/g)) (continued) 

TRIFLUR 

PCA 

BIPHENYL 

TOT PCBs 

1 Cl 

2 Cl 

3 Cl 

4 Cl 

5 Cl 

6 Cl 

7 Cl 

8 Cl 

9 Cl 

1OCl 

DIPHEN DIS 

HCBUT 

= Trifluralin 

= Pentachloroanisole 

Total Polychlorinated Biphenyls 

Total Monochlorobiphenyls 

Total Dichlorobiphenyls 

Total Trichlorobiphenyls 

Total Tetrachlorobiphenyls 

Total Pentachlorobiphenyls 

Total Hexachlorobiphenyls 

Total Hectachlorobiphenyls 

Total Octachlorobiphenyls 

Total Nonachlorobiphenyls 

Total Decachlorobiphenyls 

Diphenyl Disulfide 

Hexachlorobutadiene 

Number 

1582/09/8 

1825/21/4 

9UW4 

133613613 

27323/18/8 

255 l/42/9 

25323/68/6 

269 14/33/O 

25429/29/2 

2660 l/64/4 

286551-l/2 

3 1472/83/O 

53742/07/7 

205 l/24/3 

882/33/7 

8716813 

DATA FLAGS 

D = Value below limit of quantitation for all xenobiotics except mercury and PCBs, 

D = 2.5 rig/g 

For Polychlorinated Biphenyls 

ber of Cm 

l-3 1.25 

4-6T 2.50 

7-8 3.75 

9-10 6.25 

E = Value exceeds highest calibration standard 

See Dioxin/Furan Data Table Key for explanation of other codes. The tables include 

environmental samples (those starting with a sample number of D) and the duplicate samples 

(those starting with a Q) and confirmation samples (those starting with an S). The number of 

samples shown on the summary tables in Volume I does not include the duplicate and 

confirmation samples. 

D-5-35 
D-5-36 
Episode SCC Type Description 

2015 DFOOlOOl F UB Carp 

2016 DFOOllOl F LiB Sucker 

2017 OF001201 F LJB Carp 

2018 OF001301 F UB Sucker 

2023 OF001403 F UB Carp 

2026 OF001702 F UB Carp 

2027 DF001803 F UB Carp 

2037 DYOOO501 F UB not. available 

2056 DE000501 F b/B Care 

2057 DE000601 F UB Carp 

2059 DE000801 F UB Carp 

2060 DE000901 F UB Carp 

2070 DJOOO902 F UB Longnose Sucker 

2098 OH001501 F UB N/A 

2100 OH001703 F MB Catfish 

2105 OH002204 F UB Carp 

2109 OH002601 F UB N/A 

2110 DH002710 F UP Broun Trout 

2122 OH003904 F UB Uhite Sucker 

2126 DD000302 F UB Carp 

2133 DDOOlOO2 F BF BLw Catfish 

2139 DD001601 F UB Carp 

2142 DDD01902 F UB Catfish 

2148 00002501 F UB Saltuater Catfish 

2151 00002803 F IJB Spotted Sucker 

2152 00002903 F UB Lake Chubsucker 

2190 DC005101 F UB Carp 

2190 DC005104 F PF BLuegill 

2191 DGOO5205 F UB Carp 

2194 DC005501 F UB Carp 

2199 DC006001 F IJB Carp 

2199 DC006004 F PF Lm Bass 

2201 DC006201 F UB Carp 

2205 DG006601 F UB Carp 

2210 DC005401 F WB Catfish 

2211 DC005503 F b/B Redhorse Sucker 

2212 DC005602 F PF Sm Bass 

2212 DC005605 F UB White Sucker 

2215 DC005902 F UB Carp 

2216 DC006003 F UB Uhite Sucker 

2220 DC006405 F UB Catfish 

2227 DC007104 F UB Channel Catfish 

2228 DC007201 F PF Longear Sunfish 

2231 DC007503 F UB Gizzard Shad 

TRIFLUR PCA BIPHENYL TOT 1Cl 

PCBS 

XENOBlOTlCS CDNCENTRATIONS, t-q/g 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

16.4 

ND 

ND 

ND 

ND 

120 

ND 

ND 

4.62 

ND 

ND 

ND 

ND 

ND 

ND 

85.5 

ND 

458 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

7.41 0.57 D 924.75 ND 

1.82 D 0.34 D 142 ND 

2.85 ND 6.12 ND 

0.15 D 0.45 D ND ND 

0.33 D 0.13 D 101.67 ND 

2.31 D 0.59 D 106.85 ND 

0.82 D 0.29 D 7.64 ND 

ND 

13.6 ii.4 

ND ND 

1295.2 22.4 

4.47 1.05 D 1051 ND 

3.59 22.5 15897.3 ND 

3.06 0.56 D 461.7 ND 

ND 0.22 D ND ND 

ND 0.85 D 2.94 ND 

14.1 1.08 D 685.64 4.97 

ND ND ND ND 

ND 0.46 D ND ND 

ND 0.17 D ND ND 

ND 0.45 D 19.62 ND 

4.02 0.36 D ND ND 

1.70 D 0.13 D 30.74 ND 

ND 0.61 D ND ND 

ND 0.54 D 273.95 ND 

ND 24.66 

rti D ND 

ND 

ND 

2.01 D 0:66 D ND 

ND 

ND 

E 1.23 D 0.15 D 5.04 ND 

ND 0.49 D ND ND 

E 5.66 2.07 D 146.37 ND 

15.0 2.47 D 297 0.50 

6.28 2.63 26.64 ND 

ND 0.57 D 42.63 ND 

ND 0.86 D ND ND 

0.57 D 0.40 D 19.06 ND 

19.9 25.9 2313.5 ND 

0.87 D 0.89 D 1322.6 ND 

0.59 D 0.41 D 856.34 ND 

12.1 0.24 D 3804.1 ND 

23.8 10.2 9437 ND 

ND 0.29 D ND ND 

1.69 D 0.82 D 31.2 ND 

ND 0.87 D ND ND 

ND 0.10 D ND ND 

4.27 1.84 D 1228.9 ND 

2c1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.00 

ND 

46.3 

ND 

ND 

ND 

1.55 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

7.58 

ND 

ND 

10.4 

112 

ND 

ND 

ND 

ND 

ND 

3Cl 4Cl SC1 6Cl 7Cl 8Cl 

4.75 129 E 300 

ND 20.3 50.3 

ND ND 2.27 

ND ND 

1.17 D 13.9 ii.6 

1.11 D 4.61 33.0 

ND ND ND 

95:6 :: 4 

ND 

517 102 E 305 ii9 

1196 E 7183 E 4523 

32.5 

ND 

ND 

12.1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

9.37 

16.1 

!?18 

ND 

ND 

28.7 

3.71 

3.14 

206 

E 1689 

ND 

ND 

ND 

ND 

11.4 

147 

ND 

ND 

131 

ND 

ND 

ND 

ND 

:044 

:"85 

ND 

ND 

ND 

ND 

ND 

41.0 

54.0 

ND 

19.3 

ND 

ND 

229 

81.0 

86.9 

E 1032 

E 4112 

ND 

ND 

ND 

ND 

161 

147 

ND 

iis 

ND 

ND 

ND 

11.1 

ND 

D 11.6 

ND 

63.3 

6.06 

ND 

::06 

ND 

56.3 

106 

6.80 

7.88 

r74 

E 578 

E 242 

E 258 

E 1203 

E 2230 

?50 

ND 

::7 

E 367 E 124 ND 

54.7 16.7 ND 

D 3.85 ND 

ND ND 

41.0 21.0 

48.1 16.9 

7.64 ND 

ND ND 

E 552 E 328 

E 108 25.4 

E 2169 E 663 

109 

YD94 

E 213 

ND 

ND 

ND 

8.52 

ND 

16.7 

ND 

139 

18.6 

ND 

ND 

D 1.81 

ND 

28.9 

94.3 

16.0 

10.2 

ND 

10.8 

E 1017 

E 525 

E 340 

E 1005 

E 1063 

ND 

23.7 

ND 

ND 

E 445 

26.2 

ND 

ND 

E 54.2 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 58.3 

ND 

ND 

ND 

D 1.17 

ND 

10.8 

26.1 

3.84 

2.07 

ND 

1.52 

E 389 

E 346 

E 148 

E 309 

E 231 

ND 

ND 

ND 

ND 

E 171 

ND 

ND 

ND 

3.13 

ND 

ND 

E 53.4 

ND 

E 117 

ND 

ND 

iD82 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

10.5 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

D ND 

ND 

D ND 

E 64.2 

E 88.8 

E 20.3 

E 38.7 

E ND 

ND 

ND 

ND 

ND 

45.1 

9Cl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 27.1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

42.0 

1OCl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 8.99 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

16.4 

DIPHEN HCBU 

01s 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D-5-37 
Episode SCC Type Description 

2246 DJOO2302 F UB Bridgelip Sucker 

2247 DJ002404 F UP Mountain Whitefish 

2280 OF005201 F UB Carp 

2280 a0121688 L UB Carp 

2283 OF005501 F UB Gray Redhorse 

2290 00003403 F UB Spotted Sucker 

2294 00003804 F UB Carp 

2297 DD004102 F UB Carp 

2298 00004203 F Up Lm Bass 

2301 DDOO4504 F UP Rock Bass 

2302 DD004601 F UB PuiLLback Carpsucker 

2304 DD004801 F UB Carp 

2309 DD005301 F UB Carp 

2322 DBOOl301 F UB White Sucker 

2326 DBOOl701 F VB Uhite Sucker 

2328 08001904 F PF Chinook Salmon 

2329 DB002004 F PF Brown Trout 

2341 DD006003 F VB Carpsucker 

2355 DA001603 F UB White Sucker 

2356 DA001702 F PF Lm Bass 

2375 DA003803 F UB White Sucker 

2376 DA003903 F UB White Sucker 

2379 DE005404 F PF Lm Bass 

2380 DE005501 F VB Carp 

2383 DE005801 F UB Carp 

2385 DE006002 F UB White Sucker 

2394 DE006901 F UB Carp 

2394 QDOO6901 L VB Carp 

2394 blDO22189 L UB Carp 

2397 DE007201 F UB Sucker 

2410 DE008501 F UB Carp 

2410 DE008504 F PF Sm Bass 

2416 DE009101 F UB Carp 

2422 DE009702 F UB Carp 

2427 DE010202 F !dB Carp 

2429 DE010402 F UB Carp 

2430 DE010603 F UB Redhorse Sucker 

2430 GO121488 L F not available 

2431 DE010703 F UB Sucker 

2432 DE010710 F UB Redhorse Sucker 

2435 DE011001 F VB Longnose Sucker 

2437 DE011203 F UB Carp 

2439 DE011401 F UB Carp 

2439 DE011402 F UP Sm Bass 

TRIFLUR PCA 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

54.8 

ND 

ND 

ND 

ND 

ND 

ND 

iD7.9 

3.08 

ND 

ND 

ND 

::.5 

6.02 

0.33 

10.3 

0.70 

ND 

15.4 

4.14 

ND 

3.65 

11.6 

E.3 

42.7 

0.87 

25.8 

30.0 

25.8 

ND 

ND 

ND 

60.4 

ND 

ND 

XENOelOTlCS CONCENTRATIONS, t-q/g 

BIPHENYL TOT lr.1 

PCBS 

0.56 D 205.5 

0.49 0 82.24 

ND 5.48 

0.14 D 2.68 

0.51 D ND 

12.5 472.7 

0.82 D ND 

0.14 D 132.5 

0.22 D 4.52 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.15 D 28.24 ND 

0.22 D 26.21 ND 

0.72 D 1058.7 ND 

0.16 D 828.56 ND 

D 0.79 0 93.28 ND 

1.12 D 18.87 ND 

0 1.04 D 3937.2 ND 

1.17 D 2109.4 ND 

ND 1776.9 7.74 

0.86 D 84.6 ND 

0.32 0 39.62 ND 

0.58 D 796.74 ND 

3.59 1110.2 ND 

0.16 D ND ND 

1.71 D 8471.2 ND 

0.99 D 8783.1 ND 

D 0.92 0 343.1 ND 

2.05 D 7319.9 ND 

2.38 D 5332.9 ND 

1.13 D 4609.8 ND 

0.24 D 45.37 ND 

12.4 11119.2 ND 

0.19 0 422.66 ND 

7.54 3680.9 ND 

0.36 D 938.69 ND 

1.42 D 18490.5 ND 

1.70 D 1.35 D 29129.7 ND 

ND 0.32 D 10.15 ND 

0.56 D 0.40 D 9.27 ND 

ND 0.21 D 29.3 ND 

ND 0.64 D 1676.99 ND 

;:40 0.8227 D 789.5 115.18 ND 

44.5 0.55 D 7977.2 ND 

46.8 0.18 D 5444 ND 

2Cl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

9.82 

ND 

6.07 

ND 

ND 

2.04 

2.23 

iD31 

8.79 

ND 

21.5 

36.7 

30.9 

ND 

17.2 

ND 

32.0 

ND 

7.23 

81.7 

ND 

ND 

ND 

ND 

ND 

ii.2 

45.0 

3Cl at- SC1 6cl 7Cl 

ND 21.5 

ND 4.38 

ND ND 

ND ND 

ND ND 

11.8 88.7 

ND ND 

ND ND 

ND 

ND ::74 

:1)26 

ND 

109 

94.4 

37.0 

ND 

ND 

ND 

171 

ND 

33.1 

ND 

11.7 

4.08 

390 

E 77.7 11.9 

36.1 4.76 

5.48 ND 

2.68 ND 

ND 

170 K2 

ND ND 

83.3 E 16.1 

4.52 ND 

12.8 ND 

16.5 5.63 

E 435 E 105 

2.26 69.3 E 262 E 392 E 95.2 

2.11 D 19.9 41.3 25.8 4.17 

ND ND 9.16 9.71 ND 

63.7 E 557 E 1343 E 1455 E 442 

8.76 250 E 679 E 818 E 307 

34.5 313 E 507 E 625 E 245 

ND 18.1 44.5 22.0 ND 

ND ND 6.83 23.3 9.49 

D 19.8 270 E 323 E 162 E 19.9 

D 59.5 E 309 E 348 E 274 E 101 

ND ND ND ND ND 

184 E 20721 E 3142 E 2254 E 672 

323 E 1921 E 2803 E 2636 E 924 

ND 32.4 79.2 E 141 E 78.4 

1105 E 2740 E 2348 E 1048 E 57.4 

577 E 1576 E 1713 E 1198 E 202 

477 E 1262 E 1524 E 1100 E 190 

1.31 4.56 20.2 19.3 ND 

194 E 2789 E 3743 E 2872 E 1306 

3.46 45.7 91.4 E 188 E 82.3 

260 E 1030 E 1044 E 955 E 327 

2.69 81.7 264 E 378 E 174 

1108 E 12055 E 3699 E 1226 E 328 

2458 E 17379 E 6251 E 2147 E 619 

ND ND 2.15 D 8.00 ND 

ND ND 1.71 D 7.56 ND 

ND 

6.69 

:062 13.0 16.3 ND 

E 601 E 638 E 167 

ND 6.65 35.4 55.1 16.5 

ND 40.1 303 E 379 E 67.4 

647 E 2843 E 2745 E 1526 E 192 

E 616 E 1970 E 1718 E 982 E 113 

EC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

14.4 

E 7.80 

ND 

ND 

E 66.7 

E 46.6 

E 38.6 

ND 

ND 

ND 

E 16.5 

ND 

E 124 

E 159 

E 12.1 

ii.2 

25.9 

ND 

E 198 

E 11.8 

32.9 

38.3 

67.3 

E 169 

ND 

ND 

ND 

22.3 

1.53 

ND 

ND 

ND 

PC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

13.9 

8.28 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

it.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

lOC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DIPHEN HCBUT 

01.5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D-5-38 
Episode SCC Type Description 

2478 DJ003902 F UB Swker 

2500 DC010203 F UB Black Buffalo 

2532 DFOl9303 F bJB Carp 

2544 DFOl9202 F UB BLacktaiL Redhorse 

2608 DE014504 F UB Carp 

2618 DE015401 F UB Carp 

2618 DE015402 F BF Carp 

2618 DE015403 F UB OuiILbsck 

2651 DB008401 F UB Mite Sucker 

2653 DB008503 F UB Carp 

2654 DB008601 F UB Carp 

2709 DBOO5101 F UB Catfish 

2721 DA006502 F WB Sucker 

2721 ODD11089 L b/B Sucker 

2722 DA0066Dl F UB Sucker 

2725 DAD06301 F UB Sucker 

2748 DYOO6505 F MB Sucker 

2776 DY007101 F UB Carr, 

2776 OD010489 L UB Car; 

3001 DE019502 F IJB White Sucker 

3022 OA008401 F !dB White Sucker 

3023 DA008501 F PF Sm Bass 

3024 DA008601 F PF Lm Bass 

3025 DA008701 F UB tiite Sucker 

3028 DA008801 F PF Chain Pickerel 

3034 06025701 F UB Carp 

3035 DC025801 F UB Car; 

3036 DC025902 F UB Carp 

3037 DC026001 F UB Carp 

3038 DC026101 F UB Carp 

3039 DGO26201 F UB Carp 

3040 DGO26301 F UB Carp 

3041 DGO26402 F MB Carp 

3042 DC026501 F UB Carp 

3042 DG026502 F PF Northern Pike 

3042 PO026501 L M Carp 

3043 DGO266Ol F UB Carp 

3044 DG026701 F UB Carp 

3045 DC026801 F UB Carp 

3045 DG026802 F PF Flathead Catfish 

3046 DGO26901 F UB Bigmwth Buffalo 

3047 DG027DOl F UB Carp 

3048 DG027101 F UB Carp 

3048 06027102 F PF White Bass 

TR I FLUR PCA BIPHENYL TOT 1Cl 

PCBS 

XENcelOTlCS CDNCENTRATIONS. w/R 

ND 

ii.1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.79 

23.1 

117 

53.0 

222 

::.6 

ND 0.53 D 40.77 ND 

0.76 3.50 687.2 ND 

3.19 0.54 D 677 ND 

24.2 0.62 D 24.79 ND 

6.02 1.91 D 3955.98 ND 

122 ND 8706.3 ND 

33.1 0.20 D 2909.5 ND 

240 E 1.37 D 7091.4 ND 

2.91 0.71 D 480.04 

1.50 D 0.76 D 1833.2 

10.88 131.69E 20.5 

4.06 1.19 D 8444.1 

ND ND 460.31 

ND ND 38-4.89 

ND 0.08 D ND 

ND 2.16 D 321.71 

ND 0.24 D ND 

ND ND 21.2 

ND ND 32.69 

ND ND 10.2 

ND 0.75 D ND 

ND 0.11 D ND 

ND 0.53 D 30.78 

16.1 E -25 D 33.6 

ND 0.09 D ND 

D 2.97 0.72 D 872.12 

3.20 0.65 D 731.85 

E 6.21 0.64 D ND 

3.33 0.48 D 38.55 

6.49 70.2 148.7 

3.87 0.36 D 635.4 

E 1.01 D 0.29 D 58.26 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

14.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

6.15 27.70.30 343D 0.52 75.6D E8.9 285.12 ?32 

ND ND 0.52 D 3.96 ND 

25.9 ND 28.9 245.69 ND 

55.9 0.65 D 0.75 D 153.19 ND 

82.8 E 4.03 3.37 100.23 ND 

39.1 3.98 32.8 2220.99 ND 

5.58 0.60 D 13.2 121.03 ND 

ND 8.01 1.89 D 31.28 ND 

ND ND 1.17 D 192.3 ND 

ND 15.4 4.82 2472.5 ND 

1.64 D 0.96 D 0.37 D 80.31 ND 

2Cl 

ND 

ND 

ND 

ND 

6.28 

72.2 

27.4 

45.9 

:“29 

:049 

4.41 

12.6 

ND 

15.6 

ND 

ND 

ND 

10.2 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

20.7 

ND 

ND 

ND 

20.9 

ND 

ND 

ND 

ND 

17.1 

ND 

ND 

8.10 

12.9 

ND 

3Cl 

ND 

ND 

16.8 

::2 

1280 

455 

E 1022 

1.34 

82.5 

:!I3 

14.9 

4.29 

ND 

1.74 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

5.02 

6.75 

ND 

r80 

16.0 

ND 

1.54 

28.6 

ND 

8.29 

5.29 

::0 

8.98 

1.43 

ND 

263 

1.70 

4Cl 

ND 

ND 

91.9 

ND 

E 2341 

E 3140 

E 1162 

E 2514 

D 27.0 

E 461 

8.83 

E 2918 

21.6 

10.4 

ND 

D 28.D 

ND 

ND 

ND 

ND 

ND 

ND 

4.72 

ND 

ii.5 

87.2 

ND 

5.85 

D ND 

103 

3.16 

4.72 

34.3 

ii.8 

40.1 

12.2 

E 1104 

38.0 

9.26 

50.5 

E 1247 

D 23.7 

SC1 6Cl 7Cl 8Cl 9Cl 1OCl 

11.1 22.8 6.87 ND 

42.4 206 E 303 E 124 

201 E 254 E 96.5 16.8 

7.99 16.8 ND ND 

E 895 E 258 23.7 ND 

E 2594 E 1418 E 186 16.1 

E800 E419 E46.1 ND 

E 2014 E 1276 E 197 22.5 

114 E 220 EW.6 E18.1 

E 649 E 482 E 118 E 32.0 

11.67 ND ND ND 

E 2502 E 1963 E 620 E 121 

86.1 E 209 E 110 14.3 

84.9 E 180 E 92.7 ND 

z.4 

ND ND 

124 E 64.4 ::77 

ND ND ND 

5.32 12.4 :!48 ND 

9.01 19.1 4.58 ND 

ND ND ND ND 

ND ND ND ND 

ND ND ND ND 

16.9 9.16 ND ND 

18.2 E 15.4 E ND ND 

ND NO ND ND 

E 235 E 372 E 144 E 30.6 

244 E 330 E 63.9 ND 

ND ND ND ND 

17.2 15.5 ND ND 

17.3 94.8 15.1 ND 

264 E 199 E 53.4 ND 

E 23.7 E 31.4 E ND ND 

2.64 

111 “a”3 

ND ND 

ND ND 

ND 3.96 ND ND 

95.1 65.5 16.0 ND 

68.6 39.2 ND ND 

46.5 31.9 9.63 ND 

E 458 E 239 E 86.5 6.39 

31.2 33.1 9.75 ND 

9.17 9.87 1.55 D ND 

26.5 88.1 19.1 ND 

E 687 E 219 E 43.6 ND 

32.0 18.4 4.51 ND 

ND ND 

E11.8 END 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

5.37 ND 

ND ND 

11.6 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

DIPHEN HCBUT 

DIS 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D-5-39 
Episode SCC Type Description 

3048 QDOl26B9 L PF Uhite Boss 

3048 W027101 L IJB Carp 

3049 DC027201 F UB Csrp 

3050 06027301 F UB Bigmouth Buffet0 

3060 DF009101 F UB Flathead Cstfish 

3060 DF009102 F HI Sm Buffslo 

3060 40073189 L UB Flethead Catfish 

3061 DF0191D6 F UB Sucker 

3062 DFO24024 F UB Blue Catfish 

3063 DF023301 F UB Sea Catfish 

3063 DFD23302 F PF Spotted Seatrout 

3064 DFO23305 M Shellfish 

3065 DF023419 F BF Bigmouth Buffalo 

3065 DFO23420 F UB Flathead Catfish 

3065 W010788 F BF Bigmouth Buffalo 

3066 DFO23503 F UB Cstfish 

3066 DFO23504 F PF Freshweter Drum 

3068 DF024001 M Oysters 

3068 DFO24002 F PF Atl. Croaker 

3069 OF024007 F HI Sea Catfish 

3069 DFO24008 F PF Trout 

3069 a051788 F W Sea Catfish 

3070 OF024009 F LIB Croaker 

3070 DF024010 F PF Sheepshead 

3071 DF024014 F UB Carp 

3071 DF024015 F PF Lorgnose Ger 

3072 DF024017 F UB Carp 

3072 a0070688 L UB Carp 

3073 DF019221 F UB Uhite Sucker 

3074 DF026017 F PF Brown Trout 

3076 DFO28502 F UB CharmeL Catfish 

3077 DF019114 F UB Redhorse Sucker 

3078 OF009118 F UB Carp 

3078 DFO23815 F UB Sm Buffalo 

3078 DFO23816 F PF BLack Crappie 

3079 DF019205 F PF White Bass 

3079 DF019206 F UB Carp 

3080 DF023317 F UB Carp 

3080 OF023318 F PF Lm Bass 

3081 OF024105 F PF Uhite Boss 

3081 DFO24106 F UB Cetfish 

3082 OF023401 F lJ6 Carp 

3083 DFO23406 F PF Lm Boss 

3084 DF0241D9 F UB Channel Cstfish 

TRIFLUR PCA BIPHENYL TOT 1Cl 

PCBS 

XENDBIOTICS CONCENTRATIONS, rw/B 

1.43 

ND 

46.5 

27.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

5.23 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.90 

2.20 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

EOS 

ND 

16.0 

D 0.96 D 0.35 D 75.81 

9.14 4.69 1125.7 

10.5 1.10 D 1661.6 

7.31 0.58 D 15.55 

ND 0.15 D 4.96 

2.51 0.53 D 3960 

r:52 0.0643 D ND 3.96 

3.75 0.54 D 282.4 

ND 0.65 D 349.34 

ND 0.69 D 163.17 

ND 0.38 D 9.04 

ND 

ND 

ND 

ND 

ND 

1.96 

ND 

ND 

ND 

ND 

2.90 

ND 

0.48 D 0.38 D 92.73 ND 

1.47 D 0.59 D 180.95 0.45 

0.50 D 0.53 D 133.2 ND 

8.12 0.77 D 190.55 1.12 

0.87 D 0.43 D 21.16 ND 

3.25 ND 40.8 ND 

0.73 D 1.25 D 136.39 ND 

ND 0.19 D 216.37 ND 

ND 0.25 D 11.48 ND 

ND 0.24 D 324 ND 

ND 0.56 D 84 ND 

ND 0.21 D 141.08 ND 

3.09 3.06 278.89 ND 

8.03 2.25 D 859.56 4.19 

0.32 D 0.12 D 102.65 ND 

D 0.21 D 0.11 D 87.24 ND 

0.28 D 0.79 D ND ND 

ND 0.20 D 44.76 ND 

4.47 0.39 D 46 ND 

ND 0.13 D 1.43 ND 

ND 0.65 D ND ND 

11.8 0.98 D 114.89 ND 

0.31 D 0.17 D 10.53 ND 

1.27 D 0.25 D 55.21 ND 

2.77 0.20 D 97.67 ND 

8.30 3.52 337.71 6.00 

ND 0.16 D 10.34 ND 

0.38 D 0.34 D 10.45 ND 

3.39 0.51 D 12.3 ND 

3.44 1.11 D 7 ND 

:!61 0.33E D 239.7 1.49 : 

2Cl 3Cl 4Cl SC1 6Cl 7Cl 

ND 1.69 D 23.2 29.7 17.2 4.02 

1.96 D 66.4 503 E 347 E 167 40.3 

ND 26.7 231 E 4W E 652 E 238 

ND ND ND 5.58 9.97 ND 

ND ND 0.87 D 4.D9 ND ND 

D 13.52 1128.1E 1782.7E 937.37E 96.30 ND 

ND ND 0.79 D 2.75 

ND ND ND ND 

ND ND 45.0 92.6 

ND 2.54 35.9 84.7 

ND 4.97 22.4 66.5 

ND ND ND 4.80 

ND ND 2.63 22.8 

D ND 1.70 D 33.0 62.5 

ND ND 4.60 37.8 

D ND 9.33 31.5 45.1 

ND ND 2.61 D 14.3 

ND ND 24.1 16.7 

ND 7.29 46.2 48.7 

ND ND 3.17 48.7 

ND ND 3.88 6.48 

ND ND 11.7 85.7 

0.42 D ND 

ND ND 

124 20.8 

177 42.6 

55.9 10.5 

4.24 ND 

49.0 18.3 

69.1 14.2 

71.5 19.3 

78.5 25.0 

4.25 ND 

ND ND 

34.2 ND 

119 E 45.5 

1.12 D ND 

E 178 E 48.6 

ND ND 10.3 19.3 39.0 15.4 

ND 1.70 D 50.72 75.12 13.54 ND 

14.34 22.96 

1.65 D 17.47 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.10 D ND 

ND ND 

ND 7.98 

ND ND 

0.75 D 2.94 

ND ND 

18.0 8.81 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND 8.10 

8Cl 

ND 

ND 

E 14.9 

ND 

ND 

ND 

ND 

ND 

?60 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

76.06 137.27 28.26 ND ND 

78.44 219.80E 372.82E 144.40 20.79 

3.05 31.5 55.8 E 12.3 ND 

6.44 23.6 47.2 10.0 ND 

!“56 

ND ND ND ND 

18.9 18.3 ND ND 

ND 18.4 27.6 ND ND 

0.24 D 1.09 D ND ND ND 

::.8 ii.4 ND 29.9 ND 6.81 ND 

:;.98 3.47 24.98 5.77 356ND 1.29 D ND 

5.27 33.0 45.9 13.5 ND 

71.8 103 103 27.1 ND 

2.44 D 6.00 1.90 D ND ND 

0.81 D 3.61 6.03 ND ND 

ND 2.50 9.80 ND ND 

ND 7.00 ND ND ND 

0.75 D 0.74 D ND ND ND 

43.0 86.7 78.6 23.3 ND 

PC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

lOC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DIPHEN HCBUT 

DIS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

164 

88.31 

ND 

::54 

ND 

1.96 D 

ND 

ND 

0.81 D 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.27 D 

ND 

ND 

ND 

ND 

D-540 
Episode SCC Type Description 

3085 OF02 1113 F UB See Catfish 

3085 OF02 1114 F PF Black Drun 

3086 DFO2 I409 F UB Catfish 

3086 OF02 410 F PF Red Drw 

3087 OF02 1413 F UB Carp 

3087 OF02 414 F PF White Crappie 

3087 OF02 415 F UP Bluegill 

3088 OF02 417 F Id8 Channel Catfish 

3088 OF02 A18 F PF B\uegi\L 

3089 DF0192W F PF wit; Crappie 

3089 DFOl9210 F VB Cam 

3090 DF019213 F PF Vhiie Crappie 

3090 DF019214 F UB Channel Catfish 

3091 DF019217 F UB River Carpsucker 

3092 DF023501 F UB Carp 

3092 DF023502 F PF Usrmouth 

3093 OF024011 F PF Lm Bass 

3093 DFO24118 F UB Sm Buffalo 

3094 DC017201 F BF Channel Catfish 

3095 DC038801 F BF Brown Bullhead 

3095 DCO388O2 F IJB Channel Catfish 

3096 DC035OOl F BF Brown Bullhesd 

3096 DC035002 F UB Channel Catfish 

3097 DC038701 F BF Brou\ Bullhead 

3097 DC038702 F LIB Car0 

3097 a0071989 L BF B&n Bullhead 

3098 DC038601 F b/B Uhite Sucker 

3098 DC038602 F PF American Eel 

3098 DO051288 F IJB White Sucker 

3100 DC019701 F PF Uhite Perch 

3101 DCO199Ol F PF Brown Trout 

3103 DC036201 F UB Channel Catfish 

3103 DC036202 F VB Carp 

3104 DC020001 F PF Lm Bass 

3104 DC02OO02 F U8 Carp 

3105 OF025001 F UB Carp 

3105 OF025002 F PF Lm Bass 

3106 DEO2&301 F PF Ualleye 

3107 DE026901 F UB Carp 

3108 DE027001 F PF Walleye 

3108 DE027002 F UB Carp 

3109 DE025DOl F UB Carp 

3110 DE022501 F BF Carp 

3111 DH0158O2 F UB Silver Redhorse 

XENOBIOTICS CONCENTRATIONS, rig/g 

TRIFLUR PCA BIPHENYL TOT 1Cl 2Cl 3Cl 4Cl SC1 6Cl 7Cl 8Cl 

ND 

ND 

ND 

ND 

ND 

No 

ND 

No 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

PCBS 

ND 0.74 82.2 ND 

Ho 13.79 77.40 ND 

ND 0.61 D 1116.97 1.53 

No 2.76 14.63 ND 

1.05 D 1.68 D 142.6 ND 

ND 0.08 D 8.95 Wo 

1.60 D 0.70 0 86.56 ND 

w 0.45 D 8.86 ND 

ND 0.23 D ND ND 

ND 0.21 D 6.93 ND 

1.80 D 0.62 D 67.65 ND 

1.33 D 0.25 D 74.7 ND 

4.92 0.96 D 1887.6 ND 

0.11 D 0.16 D ND ND 

2.69 1.30 D 67.6 ND 

Ho 0.14 D 0.07 0.07 

:63 0 017:SO DND 4.5 No 

8.95 4.70 1961.6 :: 

3.92 no 838.8 ND 

13.2 0.98 0 2974.6 ND 

2.15 0 0.74 D 150.08 ND 

13.8 1.64 D 4412.9 ND 

;.“35p 

0144 

; &A? D 270.28 463540.21 w 

0 0.61 D 216.67 ND 

35.0 ND 809.24 ND 

17.4 0.98 0 809.26 ND 

39.9 ND lO42.7 9.71 

0.80 D 1.71 D 370.17 ND 

0.27 D 1.06 D 5148.1 ND 

0.64 0 0.35 0 1392.01 ND 

ND 0.34 D 778.7 ND 

ND 1.19 D 321.66 0.63 

4.76 5.07 1783.4 ND 

ND 0.68 D 8.62 ND 

ND 0.14 D ND ND 

0.90 D 0.19 D 231.79 ND 

3.38 0.32 0 761.4 ND 

0.33 D 0.20 D 37.85 ND 

4.49 0.61 D 483.7 ND 

13.4 0.50 D 5863.5 0.90 

ND 0.20 D 1804.4 ND 

1.92 0.60 D 271.46 ND 

ND 110 45.7 36.5 w 

2.25 0 13.89 

g.96 

21.69 1.61 D 

: 

Nm 

ND 8.94 98.7 E 399 E 455 E 98.8 E 24.4 

!:30 0.86 ND D ND 6.67 109 110 7.10 E.3 ND 

ND ND 1.59 D 1.81 D 5.55 m, ND 

ND 0.86 D 12.8 20.7 36.6 15.6 W 

ND ND ND 3.68 5.18 ND No 

ND ND Ho ND w No w 

ND ND PI5 1.68 0 5.25 m, Ml 

ND ND 21.9 29.2 11.4 ND 

No No li.5 42.1 20.1 Ml ND 

0.51 D 7.64 135 E 704 E 891 E 134 15.4 

ND ND ND ND 

3.70 ND ND 29.7 g.4 :“80 D ;I”: 

0 ND ND w ND ND ND MD 

ND ND No ND No w MD 

ND ND w 1.10 D 3.20 ND MD 

6.26 38.2 321 E 616 E 710 E 223 E 36.6 

9.09 30.0 E 171 E 282 E 244 E 86.4 E 10.9 

ND 72.1 E 551 E 877 E 1006 E 333 E 67.3 

2.77 0 5.04 24.78 54.76 43.19 11.71 2.62 

18.0 91.6 E 807 E 1556 E 1432 E 419 E M.6 

1.07 D 4.35 30.78 68.03 84.38 41 .S8 14.29 

3.94 1420 40.1.94 E 30.30 120 E 63.02 151 E 65.27 119 E 29.5840 :48 

6.87 45.8 379 E298 E 74.0 5.57 ND 

6.26 310 370 123 w ND 

4.46 62.1 473 400 6.00 ND 

12.71 66.64 105.01 123.28 43.51 11.16 5.24 

ND 2.79 80.75 129 1076 290.82 E 2634 542.44 E 271.36 1248 61.1 81.24 E.10 

ND 1.11 0 23.64 ND 77.0 106.43 95.67 234 384 10.04 83.7 2118 :96 

17.5 184 E 655 E 522 E 298 E W.5 10.4 

ND ND ND ND 8.62 E ND ND 

ND ND ND ND ND ND ND 

ND 18.5 124 E 62.7 E 22.3 4.29 ND 

ND 46.4 290 274 110 20.9 4.10 

ND 1.01 D 18.7 12.2 5.94 ND 110 

ND 25.1 164 185 86.5 23.1 W 

0 1.35 D 715 E 2833 E 2047 E 630 E 182 E 47.9 

ND 6.03 159 E8O7 E710 E 110 12.4 

ND 7.76 66.3 115 E 69.8 12.6 ND 

9Cl lOC1 

MD ND 

w w 

15.5 E 15.1 

ND No 

w MD 

w ND 

ND ND 

ND MD 

w ND 

w w 

Ml w 

w No 

w No 

ND ND 

ND ND 

ND ND 

w ND 

Ml No 

8.52 ND 

5.41 ND 

52.1 E 16.1 

3.28 1.93 

22.7 

17.30 r.29 

ND ND 

11.10 3.74 

ND ND 

ND ND 

110 

:62 w 

ND ND 

37.51 ND 

ND ND 

No ND 

No ND 

ND ND 

ND ND 

Ml w 

ND ND 

ND ND 

ND 

:31 ND 

w No 

No w 

DIPHEN HCBUT 

DIS 

ND 

w 

w 

ND 

ND 

ND 

ND 

MD 

No 

w 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

w 

w 

ND 

ND 

ND 

ND 

Ho 

No 

No 

w 

w 

MD 

ND 

ND 

ND 

No 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

w 

23.0 

3.53 

2.37 D 

No 

w 

ND 

ND 

ND 

w 

ND 

NO 

w 

ND 

ND 

ND 

ND 

ND 

ND 

w 

ND 

ND 

ND 

ND 

w 

ND 

ND 

w 

w 

w 

ND 

ND 

ND 

ND 

No 

w 

ND 

ND 

ND 

ND 

ND 

ND 

w 

ND 

ND 

D-S-41 
Episode SCC Type Description 

3fl2 DE022401 F VB Carp 

3112 DE022402 F PF Walleye 

3113 DE021101 F BF Channel Catfish 

3113 DED2llD2 F BF Carp 

3113 pDO30789 F BF Channel Catfish 

3114 DE021201 F BF Carp 

3115 DE021301 F WE Car; 

3115 DE021302 F RF Catfish 

3115 pO101689 L UE Carp 

3117 DE021501 F PF Lake Trout 

3118 DE021601 F PF Uatleye 

3118 DE021602 F UO Carp 

3118 DE021603 F WE Carp 

3118 DDOlO689 L WE Carp 

3118 QDD2048B L PF Ualleye 

3120 DE021801 F WE Carp 

3120 DE021802 f PF Bass 

3122 DE022001 F VB Cam 

3122 DE022003 F UB Re&orse Sucker 

3125 DE022301 F UE Carp 

3125 DE022302 F PF White Bass 

3132 DE023201 F UB Carp 

3132 ODD10588 L UB Carp 

3134 DE023403 F WE Carp 

3134 DE023405 F UB Carp 

3134 DE023406 F UB Sucker 

3135 DE023501 F WE Carp 

3136 DE023601 F PF Northern Pike 

3137 DE023701 F UB Redhorse Sucker 

3138 DE023801 F UB Carp 

3140 DE024001 F PF Walleye 

3140 DE024002 F UB Carp 

3141 DE024101 F PF Northern Pike 

3141 DE024102 F WE Carp 

3141 DE024103 F PF Northern Pike 

3142 DE022502 F U9 Carp 

3143 DE024401 F Rotten (catf) 

3143 DE024403 F UB Carp 

3144 DE024901 F UB Carp 

3145 DE026601 F UB N. Rcdhorse 

3146 DE026701 F VB Carp 

3146 DE026702 F PF Ualleye 

3147 DC035201 F WE Carp 

3148 DE027101 F UB Carp 

XENOBIOTICS COUCENTRATIONS, t-q/g 

TRIFLUR PCA BIPHENYL TOT 1Cl 2Cl 3Cl 4Cl SC1 6Cl 7Cl &cl 

ND 

No 

ND 

ND 

g.0 

58.5 

33.1 

52.5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::20 

6.03 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

PCBS 

0.77 D 1.79 D 176.1 ND ND 

ND 0.15 D 12.2 ND ND 

6.05 0.55 D 537.6 ND ND 

4.68 1.25 D 2658.9 ND ND 

5.26 1.30 0 570.79 ND ND 

1.27 D 0.52 0 74 

:;.l 

ND 

3.10 5.63 922.56 104 

ND ND 5108.2 ND 

ND 0.13 D 515.1 ND 

ND 0.68 D 2516.5 ND 

ND 0.18 D 832.6 ND 

ND 0.62 D 2744.8 ND 

0.19 D 0.11 D 666.3 ND 

2.32 D 0.90 D 1938.3 ND 

ND 0.26 D 854.05 ND 

1.37 D 1.23 D 17723.3 ND 

0.69 D 0.22 0 473.7 0.50 

5.68 53.8 757.5 34.3 27.5 

2.79 3.16 901.5 19.5 701 

ND 

ND 

ND 

ND 

ND 

L 

1.07 

ND 

D 2.66 

!:52 

4.40 

8.60 

3.46 

ND 

ND 

1.13 

ND 

11.5 1.80 0 3938.2 ND 

1.26 D 1.37 D 792.96 ND 

5.21 1.89 D 2804.3 ND 

7.30 2.13 D 3145.8 ND 

ND 0.38 0 9223.9 ND 

ND 0.33 D 13587.4 ND 

ND 0.69 D 25240 ND 

0.92 D 0.72 D 1521.4 ND 

ND 0.23 D 8 ND 

ND 1.01 D 38.19 0.62 D ND 8.82 19.0 8.67 1.08 DND ND 

0.59 0 0.50 D 13362 ND 79.1 E 1194 E 7801 E 2343 E 1228 E 570 E 133 

0.66 0 0.22 D 1467.4 1.41 

0.95 D 0.15 0 4390.3 0.95 

7.79 a.43 4117 ND 

0.86 D 2.14 D 22695.8 ND 

1.90 D 1.47 D 3678.1 ND 

ND 1.22 D 23809 ND 

ND 3.35 206.97 ND 

4.05 2.29 D 435.6 ND 

ND 0.93 D 22283.9 12.6 

0.76 D 0.37 0 643.2 ND 

23.0 3.58 4137.6 ND 

2.93 0.32 0 68.72 ND 

6.59 1.91 D 786.1 ND 

ND 0.72 0 1824.1 ND 

53.3 E38E E660 E 256 E 98.5 E 10.2 ND 

D 83.9 E 788 E 2093 E 1008 E 330 E 69.8 14.6 

50.5 E 609 E 1675 E 962 E 622 E 174 E 24.5 

283 E 3334 E 9981 E 5180 E 2816 E 946 E 150 

93 

fO2 

ND 

2.10 

267 

No 

ND 

FOO 

No 

ND 20.7 71.8 66.3 17.3 ND 

ND ND 5.30 6.90 ND No 

3.50 

37.5 

3.49 

ND 

E 259 

34.9 

E 250 

47.2 

5.10 

11.9 

24.6 

11.9 

8.10 

196 

D 63.7 

6.26 

ND 

100 

D 10.6 

127 

126 

298 

56.9 

253 

D 36.2 

ND 

52.9 132 E 234 E 97.8 

418 E 928 E 980 E 268 

54.8 141 E 249 E 104 

ND 36.4 37.6 ND 

E 231 E 220 E 86.1 5.36 

126 E 203 E 227 E 89.7 

E 217 E 204 E 91.1 18.9 

951 E 1744 E 1848 E 446 

138 203 142 27.0 

543 E 969 E 753 E 197 

280 302 184 42.0 

569 E 1058 E 839 E 221 

ii: 245 622251 161 66.2 34

313 293 151 28.2 

1102 E 7377 E 7159 E 1850 

20.5 131 231 78.4 

863 E 18% E 1005 E 74.2 

127 E 354 E 263 E 34.5 

684 787 700 404 

792 815 859 469 

E 2744 E 3656 E 2128 E 348 

E 2234 E 6093 E 4363 E 771 

4664 E 11880 E 7582 E 861 

273 E667 E478 E&l 

6.00 2.00 D ND ND 

17.4 

E 27.4 

18.5 

ND 

No 

15.1 

NO 

E 72.0 

ND 

42.6 

ND 

45.9 

ND 

FL8 

E 2;9 

9.60 

::34 

97.9 

76.2 

E 46.5 

E 65.5 

ND 

ND 

ND 

E 598 E 1639 E 824 E 414 E 102 E 8.1 

1114 E 9812 E 8766 E 3502 E 453 E 60.0 

4.87 64.2 87.0 50.9 ND ND 

20.6 125 167 108 12.9 ND 

E 3123 E 13038 E 5317 E 508 E 18.3 ND 

26.1 244 E 248 E 99.8 25.3 ND 

224 E 2149 E 1261 E 397 E 92.2 14.4 

6.71 39.2 17.2 5.61 ND ND 

53.7 E 131 E 227 E 312 E 57.4 ND 

13.7 267 E 792 E 613 E 125 13.4 

9Cl lOC1 DIPHEN HCBUT 

DIS 

ND 

ND 

ND 

No 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:or 

ND 

ND 

ND 

ND 

13.9 

::D6 

::85 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND ND 

No No ND 

ND ND ND 

ND No ND 

NO ND ND 

ND ND ND 

ND ND 8.53 

ND ND 10.5 

No ND 2.99 

ND No ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND NO 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

D ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

D ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

ND ND ND 

D-5-42 
Episode SCC Typt Description 

3148 DE027103 F PF Ualleye ND 

3149 DC038501 F w Uhitt Sucker ND 

3150 DA008901 F YB Uhitt Sucker ND 

3150 90120187 L UB Uhitt Sucker ND 

3151 DAOWlOl F UB Uhitt Sucker ND 

3152 DAOO92fM F YB Uhitt Sucker ND 

3161 DC019801 F BF Black Bullhead ND 

3161 DC019BD2 F UB Uhitt Sucker ND 

3162 DJ024DOl F UP Starry Flour&r ND 

3163 DJO24002 F hRJ Starry Flowdtr ND 

3166 DO015702 F bB Carp ND 

3165 DDOl5?04 F UB Rtdhorst Sucker ND 

3166 DDOl5706 F UB Uhitt Sucker ND 

3167 00015708 F I@ Blocgi II ND 

3167 #)062388 L UP Blutgill ND 

3168 DDOl5711 F UB Carp ND 

3168 00015712 F PF La Bass NO 

3169 DDOl5713 F UB Black Rcdhorst ND 

3169 ODD22789 L UB BLack Rtdhorst ND 

3170 DDOlS715 F UB Spotted Sucker ND 

3171 00015717 F UB Spotttd Sucker ND 

3172 00015719 F UB Carp ND 

3172 DD015?20 F PF Lm Bass ND 

3173 DDOlS722 F UB Chamel Catfish ND 

3174 00015724 F UB Chamel Catfish ND 

3175 DOOlS801 F UB Chtmtl Catfish ND 

3176 DDO15803 F L1B Spotttd Sucker ND 

3177 DDOlS805 F UB Carp ND 

31?7 ODlOO488 L UB Carp ND 

31?8 ODO15807 F Ml North Hogsucker ND 

3179 DO015809 F UB Golden Rtdhorst ND 

3180 DDO15812 F PF Lm Bass ND 

3181 00015814 F UB Carp ND 

3182 DO015815 F PF Rock Bass ND 

3182 00015816 F UB Carp 16.7 

3183 00015817 F UB Carp ND 

3183 00015818 F PF Saugtr ND 

3184 00015820 F PF Uhitt Crappie ND 

3185 DO015821 F UB Charnel Catfish ND 

3186 00015824 F UP Southern Fbundtr ND 

3187 00015902 F Up Sumner Flounder ND 

3188 Do015903 F HI Carp ND 

3188 DDOl5904 F PF Lm Bass ND 

3lB9 DDOlS9OS F UB Carp ND 

TRIFLLIR PCA BIPHENYL TOT 

PCBS 

1Cl 

XENOBIOTICS CONCENTRATIONS. ns/B 

ND 0.10 D 363.9 ND 

12.2 0.03 0 51 ND 

88.8 0.31 D 669.98 

87.4 0.32 D 646.07 

16.0 0.31 0 5365.9 

0.58 D 0.R 0 479.7 

23.19 4.29 198.1 

72.8 18.3 1697.5 

!:17 0 !!35 0 82.01 55.54 

47.4 2.08 1033.4 

7.74 0.65 0 548.2 

1.41 

1.75 

1.19 

2.02 

ND 

ND 

ND 

EO? 

1.95 

ND 

1.83 

:4s 

ND 

0 0.56 

D 0.14 

D 0.10 

0 0.36 

0.10 

0.47 

0.43 

0.48 

0 0.36 

D 0.50 

0.23 

0 1.50 

0.40 

D 0.53 

0.10 

D ii.8 

D 3.13 

0 14.43 

D 354.59 

D 1.36 

D 10.1 

0 9.55 

0 5.14 

D 2.03 

D 2803.4 

D 293.6 

0 485.52 

0 2.54 

0 170.6 

D 21.72 

1.73 0 ND 67.37 

1.30 D 0.21 0 63.79 

0.74 D ND ND 

0.96 D 0.19 D 79.63 

ND ND ND 

14.1 0.32 0 1367.4 

ND 

1.70 

2.13 

ND 

ND 

570 

ND 

L 

??6 

3.30 

2.86 

ND 

ND 

1.31 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

MD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2Cl 3Cl 4c1- SC1 6Cl ?Cl 

ND 3.40 82.7 139 115 23.8 

ND 3.00 12.5 18.3 17.2 ND 

1.08 0 61.8 256 172 96.5 47.4 

0.61 D 58.9 243 169 95.9 47.7 

4.43 403 E 3153 E 1388 E 332 E 68.1 

ND ND 19.2 80.6 218 139 

0 20.30 52.72 44.07 50.87 24.?2 4.11 

49.5 E 690 E 311 E 227 E ?2.3 

ND 

ND 

ND 

ND 

4.50 

ND 

1.10 

ND 

ND 

WD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.98 

ND 

Ho 

ND 

ND 

ND 

ND 

ND 

E 339 

Ho 

ND 

ND 

25.5 

ND 

ND 

D ND 

1.97 

ND 

ND 

ND 

ND 

ii.9 

ND 

ND 

:6? 

ND 

ND 

ND 

ND 

ND 

ND 

25.4 

26.5 

E 1754 

13.8 

ND 

ND 

37.2 

ND 

ii.3 

ND 

19.4 

47.1 178 

5.71 26.6 

299 EM6 

237 E 180 

ND 7.30 

Ho Ho 

ND 5.81 

D 27.0 98.6 

ND ND 

ND ND 

ND ND 

E 208 E 63.8 

38.6 11.1 

E 289 E 74.9 

E 87.1 E 18.6 

::13 ND 

7.52 ND 

E 151 E 58.1 

1.36 0 ND 

10.1 ND 

9.55 ND 

ND ND 4.22 0.92 D 

ND ND 2.03 0 ND 

298 E 1140 E 1021 E 280 E 

21.6 110 E 119 E 36.7 

10.3 97.9 265 E 103 

ND 18.7 42.0 ND 68.9 2.54E ii.9 

1.67 0 6.65 13.4 ND 

1.17 D 18.3 33.4 14.5 

1.09 D 15.5 32.5 14.7 

::13 :;.5 z.9 

ND 

15.1 

ND ND ND ND 

265 E 450 E 521 E 106 E ND 

E 322 E 356 E 65.2 E 8.89 ND 

E 9934 E 9872 E 2061 E 346 E 50.4 

167 E 393 E 456 E 160 E 19 

3.29 25.1 47.9 17.5 ND 

ND 

:8 

ND ND ND 

138 56.1 ND ND 

ND 10:1 8.98 ND ND 

ND ND ND ND ND 

443 E 1297 E 1270 E 234 E ND 

ND 11.6 16.9 3.52 ND 

154 E 344 E 396 E 103 E 12.9 

0.31 0 780.42 ND 1.83 

D 0.279 0 24118.2 0.792 0 100 

D 1.19 D 1218.02 5.02 4.20 

0.52 D 93.?9 ND ND 

0.31 0 ND ND ND 

4.43 315.1 ND ND 

0.24 D 19.08 ND ND 

0.12 D ND ND ND 

2.61 3309.2 10.4 26.5 

0.57 0 32.02 ND Ho 

0.99 0 1029.3 ND ND 

8Cl 

ND 

:6 

23:5 

17.4 

22.9 

L 

22.1 

:053 

ND 

ND 

ND 

ND 

15.1 

ND 

ND 

ND 

ND 

ES 

6.30 

9.32 

:71 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

4.30 D ND 

4.60 0 ND 

ND ND 

ND ND 

ND ND 

ND ND 

6.54 ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

2.82 MD 

ND ND 

ND ND 

ND ND 

ND w 

ND ND 

ND ND 

ND ND 

ND ND 

NO Ho 

2.74 0 ND 

ND ND 

ND ND 

ND ND 

NO ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

PC1 1OCl DIPHEN HCBUT 

DIS 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

MD ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND MD 

Ho NO 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

P5-43 
Episode SCC Typt Description 

3189 a0092168 L UB Carp 

3190 DDOlSW? F UB Carp 

3191 05024003 F UP Staby Flomder 

3191 DJO24OOS M Soft Shell Clams 

3192 DJ024007 F UP Starry Flomder 

3192 DJ024009 M Soft Shell Clams 

3193 DC039001 F PF Striped Bass 

31% DNO20104 F UB Cam 

3195 OH020105 F UB Ch& 

31% DH020188 F UB Sucker 

3198 DN020~11 F UB Sucker 

3199 ONOZOlOl F LIB Carp 

3199 DN020103 F UB Carp 

3200 OH020112 F UB Sucker 

3203 05024018 F UB Cam 

3205 DJO24024 0 Craif ish (whole) 

3206 DJO24103 F UB Sucker 

3208 DJO24109 F YB Sucker 

3212 05024120 F BF Catfish 

3212 DJO24121 F UB Carp 

3213 DJO24123 F UB Squtwfish 

3215 DJ023705 F UB Sucker 

3216 DJ023707 F PF Squtwfish 

3216 DJO23708 F UB Sucker 

3216 ODO22388 L UB Sucker 

3217 05023710 F UB Sucker 

3218 DJ023711 F PF Squswfish 

3219 05023713 F !dB Uhitt Sturgeon 

3219 DJ023714 F PF Uhitt Sturgeon 

3220 DJO23903 F UB Bridgelip Sucker 

3221 DJO23905 F UB Sucker 

3222 DJO23987 F LIB Sucker 

3223 DJO2371? F UP Starry Flow&r 

3224 DJO23715 W Soft Shell Clams 

3226 05023721 M Pacific Oysters 

3227 05023723 II Pacific Oysters 

3231 05023910 F PF Sm Bass 

3231 DJO23911 F tJB Carp 

3234 OH020301 F UP Squtwfish 

3235 OH020303 F NB Uhite Sucker 

3236 OH020305 F UB Largescale Sucker 

3237 OH020308 F UB Largescale Sucker 

3237 90088988 F UB Largescalt Sucker 

3238 05023918 F VP Dolly Vardtn 

TRIFLUR PCA EIPHENYL TOT 1Cl 

PCBS 

XENDBIOTICS CONCENTRATIONS. M/Q 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

20.0 

ND 

163 

ND 

ND 

ii.5 

64.8 

153 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

!!!I6 

ND 

ND 

ND 

ND 

ND 

ND 

4.48 1.44 0 1389.3 

1.07 D 0.16 D 541.5 

ND 0.25 0 8 

ND ND ND 

ND 0.21 0 7.27 

t1”9l 

O:S8 

0 0.11 35 D 5.79 1064.3 

0 3:64 382 

1.48 0 4.59 516.9 

ND 0.51 0 31.29 

29.7 8.85 256.6 

1.11 D 0.27 0 64.24 

0;21 0 23.47 

1.04 D 80.09 

2.13 D 3.41 2043.1 

ND 0.09 D ND 

5.24 7.33 1536.9 

ND 0.59 0 31.12 

E ND 0.33 0 ND 

ND 0.79 0 ND 

1.16 0 ND 102.74 

16.9 0.79 0 722.01 

ND 0.06 D 37.1 

0.92 0 0.73 D 127.9 

1.32 0 1.09 D I?3 

2.49 0 0.70 D 8.2 

ND 0.06 0 55.6 

0.18 0 0.31 0 190.84 

ND 

:?4 ND 

23.91 

174.72 

NO 

0.68 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

12.5 

8.55 

0.35 

1.47 0 265 

D 0.20 0 92.36 

ND 10.48 

1.20 D ND 

0.24 D 2.51 

0.14 D ND 

0.15 D 2.89 

0.89 D 330.9 

0.17 D 33.3 

0.68 0 22.01 

0.42 D 202.12 

D 0.45 D 741.17 

0.33 0 0.31 D 683.21 

Ho 0.19 D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.93 

ND 

ND 

ND 

ND 

1.32 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

2.34 

ND 

ND 

ND 

ND 

2Cl 

ND 

ND 

ND 

ND 

59 

ND 

ND 

ND 

0 3.62 

8.00 

ND 

ND 

6.50 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

3Cl 

29.4 

3.30 

ND 

ND 

ND 

ND 

20.7 

15.8 

20.6 

2.52 

23.9 

ND 

if!?9 

14.5 

ND 

ND 

NO 

ND 

ND 

0.98 

4.91 

ND 

ND 

ND 

ND 

ND 

ND 

&2 

ND 

0.63 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

R2 

15.9 

ND 

4c1- 

- - 

SC1 6Cl 7Cl 

206 E 484 E 519 E 132 

T5.4 E 166 E 212 E 74.0 

ND 3.30 4.70 ND 

ND ND ND ND 

No 1.60 0 5.67 ND 

ND ND ND ND 

456 E 420 E 140 E 27.6 

40.4 111 E 164 E 50.8 

73.1 152 E 205 E 66.2 

3.35 6.72 10.8 3.35 

59.6 81.2 66.9 17.0 

ND 24.1 30.9 9.24 

ND 8.36 12.5 2.61 

7.60 31.5 24.7 ND 

208 E 890 E 713 E 186 

:“,6 

ND 

ND 

ND 

D 9.86 

149 

ND 

15.0 

21.7 

ND 

701 

ND 

D 41.3 

11.7 

D 24.9 

ND 

ND 

ND 

ND 

ND 

13.3 

ND 

ND 

18.1 

205 E 311 E 197 E 6.97 

174 E 291 E 1% E 7.31 

ND ND ND ND 

ND ND ND 

E 702 E 502 E a4.3 

7.62 23.5 ND 

ND ND ND 

g.9 

ND ND 

45.5 13.5 

381 E 160 27.1 

12.4 19.8 4.90 

55.1 57.8 ND 

71.0 68.6 11.7 

:“0.8 8.20 29.7ND 5.10 

57.9 E 95.4 E 29.3 

4.97 15.4 3.54 

67.1 55.1 10.5 

129 107 17.3 

37.5 25.3 4.03 

2.50 7.98 ND 

ND ND ND 

ND 2.51 ND 

ND ND ND 

ND 73.5 2.89 163 ii.1 

14.0 19.3 ND 

14.9 4.77 ND 

105 E 72.5 6.52 

8Cl 

E 18.9 

10.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DND 

ND 

Ho 

ND 

ND 

E 30.3 

ND 

12.6 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.23 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

PC1 

ND 

ND 

ND 

ND 

MD 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1OCl DIPHEN HCBUT 

DIS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D-544 
Episode SCC Type Description TRIFLUR PCA 

3241 DJ023924 F UP Dolly Varden 

3245 05023624 F UP Flathead Sole 

3246 DJO22lW F UP Flathead Sole 

3248 DJ022502 F UB Cceposite Bottom 

3248 DO050588 F UB not available 

3249 DJO22503 F PF Brook Trout 

3249 DJO22506 F UB Sucker 

3250 05022506 F UB Sucker 

3252 DJO225W F PF Lm Bass 

3252 DJ022510 F UB Sucker 

3252 a0020989 L PF Lm Bass 

3252 PO052588 L WB Sucker 

3256 DJ022518 F UB Sucker 

3258 DC038901 F PF Spot 

3258 DC038902 F UB Croaker 

3259 DBODD466 F UB Goldfish 

3259 DBOOO473 F PF Lm Bass 

3259 DBO69101 F b/B Sucker 

3260 08000493 F UB Carp 

3261 DYD26002 F UB Striped Mullet 

3262 DY026004 F UB Tilapia Tilapia 

3266 DYD22701 F PF Black Crappie 

3266 DYO22702 F UB Channel Catfish 

3266 DO012389 L PF Black Crappie 

3267 DYO22101 F PF Rainbow Trout 

3267 01022102 F UB Sacramnto Sucker 

3270 DYO22108 F UB Sucker 

3271 DY022110 F UB Sucker 

3272 DY022112 F UB White Surfperch 

3273 DYO22113 F WB Sculpin 

32Z3 01022114 F UB Surf Smelt 

3274 DY022116 F UB Sculpin 

3276 01022119 F UB Ualleye 

3278 DYD22124 F UB Sacramento Sucker 

3281 DY022205 F !JB Sucker 

3282 01022206 F PF Flathead Catfish 

3282 01022207 F UB Carp 

3283 DYD222W F UB Carp 

3285 01022212 F UP Stingray 

3285 or022213 F UB Diamond Turbot 

3286 DY022215 F UB Carp 

3287 DY022216 F UB Tilapia Zilli 

3288 DYD22217 F PF Squawffsh 

3288 01022218 F UB Sucker 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

11.4 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

116 

43.8 

19.7 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

r22 

2:20 

1.15 

ND 

To5 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

XENOBIOTICS CORCENTRATIONS. rig/g 

BIPHENYL TOT 

PCBS 

1Cl 

0.53 0 142.92 ND 

ND 131.56 ND 

0.18 0 17.4 ND 

0.83 D 56.3 ND 

ND 112.32 ND 

0.09 D 1.27 ND 

0.25 0 563.8 ND 

0.14 0 313.6 ND 

0.14 D 1.38 ND 

0.28 0 182.29 ND 

0.07 0 3.18 ND 

0.90 0 ND ND 

D 1.03 D 53.9 ND 

D 1.15 D 629.76 1.87 

0 0.55 D 486.4 ND 

2.55 82276.6 235 

0.15 D 4539.4 4.41 

D 3.15 124192 ND 

0.31 0 293.2 ND 

ND 690.9 ND 

ND 6.3 ND 

0.10 0 ND ND 

0.69 0 13.6 ND 

0.12 0 ND ND 

0.11 D ND ND 

0.56 D ND 3.75 

0.62 0 ND 34.9 

ND 1.47 0 ND 

ND 1.27 0 126.72 

0.54 0 0.56 D 25.21 

ND 0.16 0 ND 

ND 0.10 D 76.21 

ND 0.88 0 4.98 

ND ND 121 .a 

ND 0.45 D 4.47 

E ND 0.25 D 6.1 

ND 0.57 D 16.79 

ND 0.95 0 41.42 

ND 0.33 0 725 

!:425 ND 0.700 60.3 199.63 

4.35 ::15 61 

ND 0 59 37 

ND 1.09 0 ,014 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3.69 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2Cl 

ND 

1.99 

ND 

ND 

1.10 

ND 

ND 

ND 

50 

ND 

ND 

::63 

ND 

E 1132 

32.0 

5072 

:Dg.l 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3Cl LC? SC1 6cl ?Cl acl 9Cl 

ND 2.72 38.1 81.5 20.6 ND ND 

D 5.02 10.1 47.3 51.3 15.0 0.85 D ND 

ND 

ND 

ND 

ND 

ND 

ND 

2059 

ND 

ND 

ES5 

ND ND 13.0 4.40 ND 

ND 20.4 21.3 14.6 ND 

1.62 D 22.1 70.1 17.4 ND 

ND ND 1.27 0 ND ND 

11.4 60.6 E 265 E 187 E 39.8 

10.9 92.4 E 157 E 53.3 ND 

ND ND 1.38 0 ND BD 

61.4 71.2 41.2 ND ND 

ND 0.80 D 2.38 D ND ND 

ND ND ND ND 

ND 69.26 30.5 215.80 :4 25i.35 ND 73.36 ::64 

10.6 94.6 E 192 E 155 E 34.2 

E 4748 E 42685 E 23843 E 7513 E 1663 

241 1929 E 14% E 660 E 137 

E 18344 E 60764 E 29578 E 8862 E 1332 

20.3 141 97.9 34.0 ND 

29.9 97.3 E 159 E 266 E 92 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

0.94 0 ND 

ND ND 

ND ND 

ND 8.35 

ND ND 

ND ND 

ND ND 

0.21 0 1.64 

1.05 D 23.2 

1.78 D 4.52 ND 

ND ND ND 

ND 13.6 HO 

ND ND ND 

ND NO 

ND :Sl ND 

17.9 17.0 ND 

ND 

:“p 1 

ND 

49.9 9.37 

12.1 11:7 1.41 

F31 

ND 

47.7 ii.2 

D 2.62 0.51 D ND 

50.1 42.4 5.05 

ND ND 2.02 0 2.45 0 ND 

ND ND 1.51 D 4.59 ND 

ND 

ND 

ND 

ND 

5.88 7.22 NO 

ND 32.6 8.82 

3.70 78.5 223 E 325 E 76.9 

ND ND 30.4 29.9 ND 

8.00 64.0 E 78.7 E 40.1 8.83 

2.30 D 11.4 25.1 22.2 ND 

ND ND 26.3 30.3 2.77 

ND ND 30.8 39.6 ND 

ND 

E 369 

41 .o 

l?? 

ND 

E 11.6 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

17.9 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 81.4 

ND 

63.1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

1OCl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E :18 

ND 

E ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DIPHEN HCBUT 

DIS 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D-5-45 
Episode SCC Type Description 

3289 or022219 F UP Bocaccio 

3289 01022220 F UB Sculpin 

3290 DY022221 F PF Redear Sunfish 

3290 01022222 F UB Blackfish 

3294 DJO22111 F UP True Cod 

3294 DJ022113 n Mussel 

32% 05022114 F Up Atlantic Salmon 

3296 08040101 F UB Uhite Sucker 

3297 DBO41501 F UB Carp 

3298 DBO41601 F UB Carp 

3298 08041604 F PF Lm Bass 

3299 DBO40601 F UB White Sucker 

3299 DBD40604 F PF Lm Bass 

3299 00040601 L UB Sucker 

3300 DBD40201 F UB Uhite Sucker 

3300 08040204 F PF Sm Bass 

3300 ODO21389 L LIB Channel Catfish 

3301 DBO41101 F UB Carp 

3301 DB061104 F PF Northern Pike 

3301 OOO3W89 LPF Northern Pike 

3302 DBO41Wl F UB Yhitt Sucker 

3302 DBO41904 F PF Lm Bass 

3303 08042301 F UB Uhite Sucker 

3303 08042304 F PF Sm Bass 

3303 OD102588 L UB Uhite Sucker 

3304 08041001 F PF Northern Pike 

3304 DBO41004 F UB Uhite Sucker 

3304 00041004 L LJB Uhite Sucker 

3305 DBO42001 F UB Channel Catfish 

3305 00042004 F PF Sm Bass 

3305 DD11038B L b/B Channel Catfish 

3306 DBO41801 F VB Uhite Sucker 

3306 DBO41804 F PF Sm Bass 

3306 PO041801 L UB Uhite Sucker 

3307 08042101 F UB Uhite Sucker 

3308 DB040001 F PF Northern Pike 

3309 06041301 F UB Uhitt Sucker 

3310 DC032701 F UB Bullhead 

3310 DC032702 F PF Ualleye 

3311 DC032801 F UB Redhorse Sucker 

3311 DC032802 F PF Sm Bass 

3312 DC033101 F UB Redhorse Sucker 

3312 oC033102 F PF Sm Bass 

3313 DC033201 F UB Redhorse Sucker 

TRIFLUR PCA BIPHENYL TOT 1Cl 

PCBS 

XENOBIOTICS CONCENTRATIONS, na/a 

x1 3Cl 4Cl -. TCl 6Cl 7Cl 8Cl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 0.45 D 35.5 

ND 1.14 D 90.57 

0.31 D 0.19 0 6.62 

64.2 1.55 0 1217.4 

ND 0.51 D 16.31 

ND 0.30 D 2.12 

ND 0.07 0 23.84 

ND 0.17 D 579.63 

:D?9 0.73 1680 D 3029.4 754.3 

ND 0.14 D 126.25 

ND 0.60 0 6345.8 

ND 0.42 D 610.32 

ND 0.24 0 4057 

0.28 0 0.13 D 1896.2 

ND 0.21 D 205.47 

ND 0.25 D 160.97 

4.21 12.1 9305.9 

1.28 D 0.18 D 399.86 

1.25 D 0.13 D 474.21 

0.39 D 1.41 D 2561.8 

ND 0.11 D 93.6 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

4.26 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 0.30 0 6055.6 ND 

ND 0.20 D 755.66 ND 

ND 0.81 0 8371 ND 

ND 0.09 D 127.2 ND 

1.31 D 0.46 0 4770.98 ND 

2.89 0.64 D 8811.7 ND 

ND 1.48 D 5579.1 ND 

ND 0.13 0 85.83 ND 

ND 1.56 0 5562.9 ND 

ND 0.43 D 7435.9 2.00 

ND 0.20 D 3172.03 1.27 

ND 0.50 D 12027 5.55 

ND 0.47 D 488.7 ND 

ND 0.12 0 ND ND 

1.93 D 0.37 D 62.47 ND 

1.23 0 1.70 D 372.6 ND 

1.08 0 1.63 D 101.01 ND 

1.37 0 0.15 0 285.95 ND 

0.37 0 0.24 D 83.22 0.18 

3.08 0.33 D 741.47 ND 

1.59 D 1.24 0 250.37 1.14 

0.62 0 0.21 D 326.61 ND 

ND 

ND 

ND 

ND 

ND 

0.06 

ND 

ND 

ND 

45.6 

ND 

109 

3.62 

24.0 

ND 

ND 

ND 2.76 13.8 15.8 3.14 ND 

2.08 D 17.6 39.5 29.3 2.09 D ND 

ND ND 2.41 0 4.21 ND ND 

12.1 199 E 505 E 412 E 84.7 4.60 

ND ND 6.86 9.45 ND ND 

D 0.32 D 0.88 D 0.86 D ND ND ND 

ND ND 8.87 13.4 1.57 D ND 

14.4 109 E 182 E 208 E 60.9 5.33 

42.3 300 E 260 E 125 27.0 ND 

243 E 1006 E 791 E 668 E 246 E 29.8 

1.75 D 24.5 40.7 43.0 16.3 ND 

E 437 E 2478 E 1901 E 1083 E 311 E 22.5 

43.7 E 247 E 193 E 97.5 E 25.5 ND 

E 160 E 1246 E 1401 E 887 E 300 E 39.0 

16.1 331 E 619 E 622 E 258 E 47.4 

ND 32.6 69.6 E 75.1 E 26.3 1.87 

.- -- _ 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::72 

D ND 

ND 1.62 D 27.6 53.9 E 56.9 E 19.8 1.15 0 ND 

46.7 1163 E 4133 E 2256 E 1313 E 357 E 37.2 ND 

5.16 60.5 E 175 E 98.8 E 50.2 10.2 NO ND 

4.81 68.6 E 207 E 119 E 62.5 E 12.3 ND ND 

PC1 

ND 30.8 407 E 926 E 910 E 262 E 26.0 ND 

ND ND 14.3 36.0 35.5 7.80 ND ND 

17.1 879 E 3813 E 1076 E 206 E 52.0 12.5 ND 

0.86 D 65.0 E 460 E 183 E 35.9 10.9 ND ND 

31.2 1302 E 5619 E 1106 E 243 E 56.2 13.6 ND 

ND ND 29.0 50.8 E 39.2 8.20 ND ND 

5.98 162 E 1526 E 1823 E 1013 E 211 E 30.0 ND 

16.1 364 E 3170 E 3316 E 1634 E 286 E 25.6 ND 

10.5 116 1154 E 1989 E 1635 E 580 E 94.6 ND 

::26 1.8105 22.9 1034 E 32.9 1925 E 22.5 173 E 5.?2 621 E ND 126 ND 10.6 

D 146 E 698 E 2477 E 2064 E 1280 E 586 E 168 E 14.9 

52.3 E 2?9 El127 E835 E 546 E 261 E 65.7 4.76 

249 E lt22 E 4490 E 3174 E 1890 E 880 E 203 E 13.5 

ND 3.20 77.6 E 169 E 172 E 55.4 11.5 ND 

ND ND 

::97 

ND ND ND ND ND 

ND ND 29.3 27.0 3.20 ND ND 

:"40 D 19.569 62.8 29640.9 153 E 6.27 107 E 4.94 30.3 ND ND 

ND 6.55 35.6 81.4 E 110 E 44.3 8.10 ND 

0.63 D 2.75 14.89 25.30 29.97 9.07 0.43 0 RD 

ND 6.77 95.6 E 254 E 279 E 93.7 E 12.4 ND 

1.88 D 5.94 42.23 84.98 86.64 25.04 2.52 ND 

ND 0.61 D 20.8 116 E 141 E 37.8 10.4 ND 

lOC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DIPHEN HCBUl 

DIS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

No 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.84 D 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.36 D 

ND 

ND 

ND 

ND 

D-5-46 
Episode SCC Type Description 

3313 DC033202 F PF Sm Bass 

3314 DC033301 F UB Channel Catfish 

3314 DC033302 F PF Uhite Bass 

3315 DC033401 F b/E Carp 

3315 DC033402 F PF Lm Bass 

3316 DCo33501 F UB Uhite Sucker 

3317 DC033601 F UB Uhitt Sucker 

3318 DC033701 F UB Uhitt Sucker 

3319 DBO41401 F UP Uinter Flounder 

3320 08041412 F UP Bluefish 

3321 DBO404ol F UP Uinttr Flour&r 

3321 PO100688 L Up Uinter Floubr 

3323 DBO412O6 F UP Uinter Flounder 

3324 DBO41252 F UP Bluefish 

3325 DBO41218 F UP Bluefish 

3326 08041208 F UP Bluefish 

3327 DBO403ol F UP Bluefish 

3327 DBO40315 F UP Bluefish 

3328 DUO29111 F UB Carp 

3329 DD0160o3 F U8 Bonfin 

3330 DDO29110 F UB Spotted Sucker 

3331 00016007 F UB Carp 

3332 DD016OO9 F UP Spotted Drun 

3333 DDOl6Ol2 F UB Sea Catfish 

3334 DDol6Ol3 F UB Sea Catfish 

3335 00016015 F UP Spot 

3335 DD029101 F UP Red Drun 

3335 00029102 F UB Southern Flounder 

3335 DDo291o3 F Up Shtepshead 

3335 ODW1588 L VP Red Drun 

3336 DD016OO4 F Up Black Drum 

3336 DDO16OW F UP Sheepshead 

3336 DDO16O17 F UP Red Drum 

3336 DDOMO18 F PF Spotted Statrout 

3337 DDoMOl9 F UB Spotted Sucker 

3338 DD016O22 F UB Spotted Sucker 

3339 00016023 F UB Carp 

3340 00029114 F UB Channel Catfish 

3341 00016104 F UB Catfish 

3341 90081788 L UB Catfish 

3342 DD0161O5 F UB Spotted Sucker 

3343 DDO16107 F UB Uhite Sucker 

3344 DDO161W F UB Carp 

3345 DD016111 F UB Rtchorst Sucker 

TRIFLUR PCA BIPHENYL TOT lC1 

PCBS 

XENOBIOTICS CONCENTRATIONS, nB/B 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

FO? 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

0.42 D 24.98 ND 

1.95 0 3201.5 ND 

0.78 0 0.76 0 502.84 ND 

ND 0.18 D 65.9 ND 

ND 0.19 0 4.58 ND 

0.46 D 0.32 D 1783.5 ND 

1.78 0 4.93 6.38 ND 

1.50 D 1.53 0 51.5 ND 

ND 0.14 0 129.77 ND 

ND 0.70 0 2?9.?3 ND 

1.29 D 0.35 D 312 ND 

1.23 D 1.28 0 303.00 ND 

0.45 D 0.07 D 227.46 ND 

1.67 D 0.48 0 411.27 ND 

ND 0.08 0 184.81 ND 

0.35 D 0.19 D 394.07 ND 

::63 2.37 065D 628.2 1319.2 ND 

0.67 D 0.67 D 3305.7 ND 

8.11 1.05 0 26.3 ND 

2.32 D 1.47 D 144.85 ND 

0.85 D 0.28 D 144.3 ND 

ND 0.3985 D 89.57 12.3 1: 

1.34 D 2.95 1066.2 NO 

11.7 1.83 0 344 ND 

1.99 D 0.67 D 522.57 ND 

1.17 D 0.43 D 48.98 ND 

1.19 D 0.74 D 1327.8 NO 

0.82 D 0.31 0 611.44 ND 

ND 3.34 37.48 ND 

ND 0.42 0 210.12 ND 

ND 0.06 D 15.67 ND 

ND 0.23 0 15.25 ND 

1.45 0 1.33 D 41.47 ND 

121 E 2.30 0 429.25 3.35 

0.65 D 0.87 D 757.1 ND 

8.90 2.38 D 78.66 ND 

0.75 D 5.30 456.67 ND 

0.56 D 5.89 439.4 ND 

12.5 13.8 132.8 ND 

8.28 0.93 0 16.27 ND 

4.67 1.01 D 1444.3 ND 

1.49 D 0.80 0 86.21 ND 

2Cl 

0.23 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

?Ol 

ND 

:91 

ND 

ND 

ND 

ND 

ND 

ND 

0.24 

ND 

ND 

ND 

ND 

ND 

ND 

19.0 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3Cl 

D 1.46 

37.3 

4.39 

ND 

ND 

0.59 

ND 

ND 

3.92 

2.73 

12.0 

57-z 

9:?7 

2.74 

6.77 

17.6 

79.4 

27.0 

1.50 

D 5.37 

ND 

ND 

ND 

17.6 

ND 

1.88 

D 0.83 

ND 

ND 

2.12 

ND 

ND 

ND 

ND 

20.8 

13.9 

11.6 

ND 

ND 

ND 

ND 

7.19 

ND 

4c1- SC1 6Cl ?Cl 8cl 

D 10.01 11.49 1.?9 

403 E 1261 E 1229 

62.2 E 188 E 192 

11.6 27.1 22.2 

ND 1.11 D 3.47 

D 187 E 1019 E 517 

:068 6.38 27.3ND 16.9 

28.0 53.2 E 38.9 

43.2 111 E 108 

64.8 E 113 E 100 

62.8 113 98.5 

D ND ND 

E 260 E 11.2 

E 51.9 4.35 

5.00 ND 

ND 

E 52.7 F25 

ND 

iD.62 ND 

5.?5 ND 

E 14.8 ND 

E 22.2 ND 

21.0 ND 

45.4 88.3 E 77.6 E 12.2 ND 

95.5 E 157 E 122 E 27.0 ND 

38.8 84.0 E 51.9 E 7.37 ND 

87.2 E 161 E 121 E 18.1 ND 

164 E 221 E 186 E 39.6 ND 

493 395 E 2?5 62.2 11.6 

368 E 987 E 1371 E 439 E 96.3 

6.41 8.73 9.66 ND ND 

22.9 54.1 E 52.3 E 8.71 0.56 

ND 30.5 90.0 23.8 ND 

ND ND 12.3 ND ND 

1.77 D 25.9 51.1 10.8 ND 

14.7 138 E 539 E 259 E ?9.1 

ND 22.0 45.8 64.8 150 

0 14.4 

0 4.62 

8.60 

2.31 

0 ND 

3.22 

ND 

ND 

2.98 

90.7 

51.2 

47.3 

21.2 

;: 6 

3.il 

22.2 39.9 

6.91 5.46 

27.4 70.3 

0 7.73 28.5 

ii.6 k”: 

4.49 9.i9 

2.55 8.81 

5.27 12.6 

E 142 E 146 

9Cl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

17.4 

ND 

D ND 

ND 

ND 

ND 

18.8 

61.4 

97.7 E 239 E 102 

17.14 13.78 ND 

186 E 593 E 413 

98.7 E 327 E 135 

4.28 14.4 12.8 

E 51.1 30.0 14.7 

1.89 D ND ND 

3.89 ND ND 

1.62 D ND ND 

E 26.4 ND ND 

E 218 E 251 E 88.8 12.4 ND 

24.6 25.9 7.49 ND ND 

114 E 227 E 57.8 6.67 ND 

104 E 219 E 58.5 10.6 ND 

64.2 47.4 ND ND ND 

12.0 4.27 ND ND 

E 249 E 322 E 192 E 379 E ::? 

23.2 44.4 15.5 ND ND 

1OCl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E ND 

ND 

ND 

ND 

ND 

ND 

ND 

E ND 

E 5.49 

ND 

E 29.5 

E 12.2 

E ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

E 16.5 

ND 

DIPHEN HCBUT 

DIS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

3.24 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

2.50 

ND 

D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

D-547 
Episode SCC Type Description 

3346 DD016113 

3346 000161~4 

3347 DD016115 

3348 DDOl6117 

3348 DDOl6lll 

3349 00016119 

3350 DDO16121 

3350 Do016122 

3351 DD016124 

3352 OF023723 

3352 DFO23724 

3352 ODO22089 

; F UB Creek Chubsucker 

F PF Lm Bass 

1 F UB Carp 

’ F PF tiite Perch 

I F UB Blue Catfish 

1 F UB Carp 

F UB Carp 

! F PF Lm Bass 

F UB Carp 

1 F PF Crappie 

F UB Carp 

I L Pi Crappie 

3353 OF024121 F BF BIGCatfish 

3353 OF024122 F UB Bm Buffalo 

3354 DYO22 101 F UB Carp 

3354 01022 102 F PF Lm Bass 

3355 DYO22 103 F UB Carp 

3355 DID22 iD4 F PF Lm Bass 

3356 DE030 !Ol F IJB Carp 

3357 DYD22 !24 F UB Sacramento Sucker 

3360 DUO29 17 F UB Carp 

3375 00016 05 F W Carp 

3375 Do016 106 F PF Lm Bass 

337S a0071 89 L PF Lm Bass 

3376 DOOld IO? F UB Carp 

3376 DO016 iO8 F PF Lm Bass 

3377 00016 109 F HI Carp 

33n 00016 110 F PF Lm Bass 

3378 DO016 ill F UB Spotted Sucker 

3378DDo29 15 F UB Creyfin Sucker 

3385 DO016 ,Ol F UB Redhorse Sucker 

338s 90101 I66 L B not available 

33% Do016 ,21 F UB Redorot Sucker 

3401 00016 iW F UB Carp 

3401 ODD16 i10 F PF Lm Bass 

3403 DO016 i13 F UB River Carpsucker 

3403 00016 i14 F PF Lm Bass 

3404 00016 il5 F UB Carp 

3404 DDO16515 F UB Carp 

3409 08040701 F UB Carp 

3400 DBO40?06 F PF Lm bass 

3411 DB040501 F UB Redtorse Sucker 

3412 DBO40901 F PF Sm Bass 

3412 DBO40907 F UB Carp 

XENOBIOTICS CONCENTRATIONS, rig/g 

TRIFLUR PCA BIPHENYL TOT lC1 2Cl 3Cl cc1 5Cl 6Cl ?Cl aci 

PCBS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

10.9 

ND 

40.3 

3.21 

ND 

ND 

26.8 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:"lo 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

1.44 D ND 74.65 

ND 0.10 D ND 

14.7 2.16 0 1935.1 

0.28 0 0.26 D 6.04 

2.82 0.18 D 38.22 

6.17 0.10 D 550.06 

ND 0.51 0 569.5 

:“lS 0.2468 0 D 34.07 1085.9 

ND 0.14 D ND 

0.29 D 0.19 D 22.79 

ND 0.18 D ND 

0.57 D 0.34 0 20.31 

5.95 0.29 0 213 

18.4 0.96 0 311.95 

1.44 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

3.55 

ND 

ND 

ND 

1.14 

3.06 

ND 0.14 D 25.58 

21.9 2.37 0 1950.8 

ND 6.15 65.3 148 E T9.5 13.0 ND 

ND ND 2.22 0 11.2 10.8 1.36 0 ND 

ND 0.13 D 113.45 

2.00 0 26.4 6819.1 

1.43 D 0.35 D 270.38 

16.4 0.51 D 843.09 

647 E 15.3 2847 

9.70 0.52 D 60.38 

14.45 0.80 0 176.6 

334 

0.60 

E 1.92 D 3030.3 ND s.?? 

3.09 0.15 D 

ND 

53.?7 0.15 0 1.44 

187 0.90 D 6061.6 

24.9 

7.56 

1.82 D 0.30 D 137.95 0.87 D ::32 

1.56 

ND 

0 0.52 D 89 ND ND 

4.14 4.20 

ND 

4.51 ND ND 

1.21 0 0.60 D 182.43 

45.0 

ND ND 

1.09 D 0.44 0 191.7? ND 

0 

ND 

9.59 

6.53 

0.73 D 926.8 ND ND 

1.67 

16.43 

0 1.07 0 1116.6 ND ND 

ND 0.17 D 29.66 ND ND 

27.7 70.6 E 2528.3 0.86 D ND 

0.36 D 3.66 80.05 ND ND 

ND ND 332.4 ND ND 

0.59 1920 0.2960 0 414.96 14323.3 ND zoo 

ND 0.73 D 256.9 ND ND 

13.0 12.0 207.43 ND ND 

ND 0.22 D 274.7 ND ND 

ND 0.69 D 3784.99 ND ND 

0 20.2 17.8 10.6 16.3 8.31 ND ND 

:!38 

ND 

!!.2 E 335 

ND ND ND ND 

E 503 E 720 E 289 E 53.5 

ND ND ND 2.56 3.48 ND ND 

0.81 D 2.63 7.41 8.07 14.2 5.10 ND 

ND 2.56 53.3 162 E 229 E 86.0 E 17.2 

ND ND 67.0 226 E 240 E 36.5 ND 

ND ND ND 10.8 18.3 4.97 ND 

ND 2.35 0 92.0 353 E 456 E 158 24.6 

ND ND ND ND ND ND ND 

1.17 0 9.26 2.42 0 2.45 0 7.49 ND ND 

ND ND ND ND ND ND ND 

ND ND 1.08 D 6.22 10.1 2.91 0 ND 

ND 10.8 49.7 61.5 74.2 16.8 ND 

73.1 

D 

508 

11.2 

E 

la4 

820 

600 

E 

ES11 

1042 

E296 

E 490 

E 

E 

48.0 

91.4 

0 

ND 

9.73 

2.35 

13.19 

D 20.9 

19.64 8.14 

59.7 E 29.2 

1.48 0 

1.30 

ND 

786 E 3517 E 1649 E 618 E 190 E 30.7 

2.48 0 41.6 98.1 105 23.2 ND 

4.w 99.0 E 253 E 364 E 123 ND 

258 E 799 E 756 E 747 E 242 ND 

63.15 22044.09 14.28 37.55 12.24 4.09 11.64 0.68 ND 0 :: 

104 E 1171 E 1960 E 2102 E 717 E ND 

31.83 36.23 45.39 17.18 3.13 ND 

5.70 16.3 30.1 36.9 ND ND 

4.51 ND ND ND ND ND 

0.63 0 16.2 7?.3 E 76.5 E 11.8 ND 

ND 21.2 91.8 E 72.2 E 6.57 ND 

ND 29.8 206 E 457 E 194 E 40.0 

2.63 66.9 293 E 643 E 106 5.10 

ND ND 8.10 19.4 2.16 D ND 

2.76 156 E 436 E 1515 E 335 E 76.3 

1 .?l 6.27 21.7 44.3 6.07 ND 

ND 26.4 81.0 E 142 E 68.2 14.8 

1.16 0 28.9 100 E 188 E 80.8 16.1 

1007 E 6345 E 4164 E 2225 E 475 E 87.3 

20.3 118 E 83.4 E 35.2 

14.0 62.5 T5.3 46.0 

:63 ND 

ND 

35.2 92.3 E 109 E 38.2 ND 

440 E 1397 E 1340 E 4% E 84.3 

9Cl 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0 ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

6.38 

ND 

ND 

ND 

12.0 

ND 

ND 

ND 

9.19 

lOC1 D I PHEN HCBUT 

01s 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

15.6 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

ND ND 

D-548 
Episode SCC Type Description 

3414 DC036203 F PF Sm Bass 

3414 DC036204 F BF Channel Catfish 

3415 DC036205 F PF Sm Bass 

3415 DC036206 F BF Channel Catfish 

3419 DC036207 F UB White Sucker 

3419 DC036208 F PF Frtshuater Drun 

3420 DC036200 F PF Greenfish 

3420 DC036210 F UB Carp 

3421 DC036211 F PF Uhite Perch 

3421 DC036212 F UB Carp 

3422 DC036213 F PF Lm Bass 

3422 DC036214 F WE Ytllou Bullhead 

3423 DC036216 F UB tdhite Catfish 

3424 DC036218 F UB White Catfish 

3425 OF025005 F U8 Carp 

3426 DBO69102 F PF Bluefish 

3427 08069103 F PF Bluefish 

3428 DBO69104 F PF Bluefish 

3429 DB069105 F PF Utakfish 

3430 08069106 F UB White Catfish 

3431 08069109 F UB Red Snapper 

3433 DB069112 F UP Flounder 

3434 08040801 F UP Flcuder 

3434 CID011889 L UP Flounder 

3435 00016602 F UB Bigmouth Buffalo 

3444 00016603 F UT3 CarD 

3444 00016604 F SF Chaknel Catfish 

3444 00029512 F PF Lm Bass 

3445 00029513 F UB Flounder 

3446 DD016605 F PF Striped Bass 

3446 00016606 F UB Carpsucker 

3446 90091889 F UB Carpsucker 

TRIFLUR PCA BIPHENYL TOT lC1 

PCBS 

XENOBIOTICS CONCENTRATIONS, rig/g 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

::.a 

13.4 

ND 

ND 

ND 

ND 

ND 

!“W 0.23 2700 586.95 1426 

::53 0.60 1.62 0 D 102.21 lOrZ.2 

ND 0.15 D 305.08 

ND ND 117.92 

10.54 0.13 0 82.35 

12.3 0.95 0 324.5 

0.33 0 0.21 0 ND 

2.92 2.22 0 33.99 

D.7? D 0.23 0 ND 

ND 0.09 0 13.25 

1.10 0 0.14 0 693.9 

0.86 0 0.13 D 76.4 

ND 0.44 D 187.07 

0.16 D 0.28 D 213.34 

ND 0.31 D 193.05 

ND 

ND 

ND 

!D41 

ND 

1.03 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND ND 697.8 ND 

ND 0.12 0 16.98 ND 

ND 0.17 D 107.04 ND 

ND 0.34 D 231.18 ND 

0.57 D 0.60 0 485.37 ND 

0.56 D 0.41 D Tj9.78 ND 

0.7, D 0.98 D 1082.5 ND 

85.1 7.11 593.6 ND 

57.3 Z.?? D 406.32 2.01 

48.6 1.44 D 470.16 3.49 

1.82 D 0.22 D 145.96 ND 

ND 0.44 D 18.57 ND 

ND 0.28 D 740.97 0.65 

ND 0.62 D 504.47 ND 

1.19 D 0.47 D 529.22 ND 

2Cl 3Cl 4Cl SC1 6Cl 7Cl 8Cl 9Cl 

ND 

ND 

ND 

ND 

0 3.12 

:D98 

5:51 

ND 

6.92 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

:"85 T9.5 11843.2 158 E 64.4 257 E 88.6 232ND ND 

ND 2.20 D 22.1 51.4 E 25.1 1.41 0 ND 

17.8 99.3 230 E 480 E 219 E 29.1 ND 

41.50 116.65E ll?.lM 26.24 ND ND ND 

5.59 29.62 57.09 22.05 3.57 ND ND 

3.22 13.60 22.73 28.39 9.91 0.49 0 ND 

7.99 65.0 132 E 93.3 E 20.7 ND 

ND ND ND ND ND 

2.47 D ND ii.6 ND ND ND 

ND ND ND ND ND 

ND ND 1.97 D 8.99 2.29 0 :: 

ND 17.0 111 E 334 E 196 E 35.9 

ND ND 15.4 43.8 17.2 ND 

1.37 0 17.4 33.8 TI.2 44.9 12.4 

5.64 49.6 81.2 E 66.5 E 10.4 ND 

6.93 47.4 73.0 E 57.2 8.52 ND 

24.4 246 E 260 E 151 E 16.4 ND 

ND ND 5.08 11.9 ND ND 

:“OS 

20.9 

0 5.74 18 6

122 

48.8 2754.8 118 E 40.8 17.8 ND 2.93 

E 154 E 139 E 42.3 7.17 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

39.3 E 240 E 264 E 1?5 E 39.6 1.88 D ND 

0.93 D 83.5 E 410 E 357 E 203 E 28.1 ND ND 

10.1 172 189 20.5 ND ND 

4.51 112 127 36.2 ND 

3.89 15.5 107 E 152 E 130 E 49.5 

!!?a 

ND 

5.74 39.1 50.2 39.7 10.4 0.82 D ND ND 

0.37 0 1.33 D 5.53 8.60 2.74 0 ND ND ND 

lOC1 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

DIPHEN HCBUT 

DIS 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

0.90 D 3.16 54.9 E 219 E 306 E 124 E 27.6 3.79 D 0.97 D ND 

ND 4.36 68.8 E 146 E 192 E 74.5 E 15.5 2.51 0 0.80 D ND 

ND 18.5 70.1 E 150 E 195 E 74.9 E 17.1 2.72 E 0.90 D ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

NO 

ND 

ND 

ND 

ND 

ND 

ND 

D-5-49 
D-5-50 
APPENDIX D-6 

Information on Fish Samples 
Key to Table D-6 

FISH AND SHELLFISH SAMPLE INFORMATION 

Episode Number 

SCC Number 

DioxinIFuran Analyses 

Percent Lipid Content 

Wet Weight of Sample Analyzed 

Xenobiotic Analyses 

Percent Lipid Content 

Wet Weight of Sample Analyzed 

Number of Fish Used to Make Composite Sample 

Date Sample Collected 

NA = Not Available 

NM = Not Measured 

Dd-1 
D-6-2 
Episode SCC Dioxin/Furans Xenobiotics No. of 

Sanples in 

Ccqositc 

MA 

MA 

WA 

MA 

MA 

03 

03 

01 

01 

01 

01 

MA 

MA 

WA 

MA 

WA 

MA 

MA 

MA 

MA 

MA 

WA 

MA 

04 

WA 

MA 

WA 

WA 

WA 

WA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

WA 

MA 

MA 

MA 

MA 

WA 

#A 

WA 

81 

MA 

#A 

it 

01 

WA 

MA 

WA 

WA 

WA 

WA 

WA 

MA 

WA 

MA 

MA 

HA 

MA 

WA 

MA 

Semp1it-q 

Date 

850617 

850617 

850617 

830527 

830527 

841117 

841117 

850522 

850522 

850531 

850531 

850309 

840722 

840722 

840905 

840905 

840905 

840816 

840816 

840801 

840801 

840808 

841017 

841009 

841016 

840820 

840820 

840820 

841004 

841004 

840920 

840920 

840920 

841004 

841004 

841004 

840906 

840906 

840913 

841017 

841017 

841002 

841002 

841002 

841114 

841023 

841023 

841017 

841017 

841017 

840918 

840918 

840725 

840725 

841030 

841030 

840918 

840918 

840807 

840807 

841009 

841009 

841009 

840906 

840906 

840911 

840911 

Xlipid 

NH 

NM 

NM 

NM 

:2 

NM 

7 

NM 

10.5 

NM 

3 

NM 

1.1 

7.6 

NM 

NH 

in7 

7 

NM 

11.2 

15.2 

17.4 

12.9 

2"8 

r8 

NM 

NM 

12.7 

NM 

!?l 

NM 

12.5 

:)114 

NM 

7.7 

4.9 

NM 

::1 

NM 

:2 

NM 

::9 

:"8 

NM 

NM 

6.2 

NM 

10.2 

4.8 

1 

21.1 

NH 

:1 

NM 

10.2 

2.1 

wet weight 

(8) 

NM 

NM 

NM 

NM 

NM 

20.01 

NM 

19.98 

Lt.09 

!i.W 

NM 

19.98 

20 

NM 

NM 

F.01 

20.04 

NM 

20.04 

20.03 

20.01 

20.21 

!.18 

NH 

20.15 

NM 

NM 

19.98 

NH 

::.09 

s: 

NM 

17.33 

ILo7 

20.12 

NM 

::.05 

NH 

NM 

20.04 

NH 

ri 

ii.07 

NM 

:k4 

NM 

20.13 

20.06 

20.16 

20.11 

NM 

I.14 

NM 

20.06 

19.99 

No. No. Xlipid net weight 

(a 

19.98 

20 

20.01 

20.02 

19.92 

20.00 

20.07 

19.98 

20.06 

19.95 

20.12 

20.01 

20 

20 

20 

5.67 

::.02 

20.1 

19.98 

20.09 

20.06 

20.06 

20.02 

20.07 

20.05 

20.01 

20.04 

19.99 

:: 04 

19:97 

20.04 

20.09 

20 

20.12 

20.06 

20 

20.06 

19.88 

20.03 

20.04 

20.04 

20.01 

20 

20.01 

20.22 

58.02 

20.02 

20 

20.06 

19.91 

19.99 

19.93 

19.98 

20 

20.3 

19.98 

20.02 

20.07 

20 

19.96 

19.93 

20.07 

19.95 

20.03 

1994 

1994 

1994 

1998 

1998 

2015 

2015 

DEDlT702 

DEOlTTO3 

poll0586 

13285 

NM 

NM 

NM 

NM 

NM 

5:: 

3.5 

1.8 

NH 

NM 

NM 

NM 

NM 

5 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

13 

13.3 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

:w4 

NM 

NM 

NM 

NM 

13421 

DFD01fi 

DF001002 

2016 

2017 

2026 

2017 

2026 

2016 

2018 

2027 

2023 

2027 

2023 

2037 

2026 

DF001201 

DFOO1101 

DFOO1202 

DFDO1301 

DF001102 

DF001402 

DF001703 

DF001706 

DF001403 

DF001702 

DF001802 

DF001803 

DY000501 

2037 DY000502 

2056 DE000501 

2057 

2059 

2060 

2070 

2070 

2070 

2098 

DE000601 

DE000801 

DE000901 

DHODl504 

DJOOO9Ol 

DJOOO902 

DH001702 

ml072186 

DH001501 

2098 

2100 

2100 

2100 

2105 

2105 

2105 

2lW 

2100 

2110 

2122 

2122 

2126 

2126 

2126 

2133 

2138 

2138 

DH001703 

DDlllO86 

DHOO2201 

OH002204 

aDo63D86 

DH002601 

DHO02602 

DH0027lD 

DH003901 

DH003904 

DDOOO3D2 

DD000303 

GDO62666 

DD001002 

DD001501 

DD001504 

DD001601 

DO001604 

PO071486 

DDOOl902 

DD001903 

DD002501 

DD0025D4 

DDOO2801 

DD002803 

DDOO2902 

DDOO2903 

DG005lOl 

DGOO5104 

2139 

2139 

2139 

2142 

2142 

2148 

2148 

2151 

2151 

2152 

2152 

2190 

2190 

2191 

2191 

2191 

2194 

2194 

DG005206 

PD 092486 

DG005501 

DGOO5504 

DGOO6001 

DC006004 

NM 

NM 

3.2 

::r 

NM 

NM 

NH 

0.9 

NM 

!?8 

NM 

NM 

NM 

NH 

NM 

NM 

NM 

NM 

NH 

NM 

NM 

NM 

::6 

NM 

NM 

2199 

2199 

D-6-3 
EDiSOde SCC 

i0. No. 

Dioxin/Furans 

Xlipid- net weight 

(0) 

2201 

2201 

2205 

2205 

2210 

2211 

2212 

2212 

2215 

2216 

2216 

2220 

2220 

2225 

2225 

2225 

2227 

2227 

2228 

2228 

2228 

2231 

2246 

2246 

2247 

2247 

2280 

2280 

2280 

2280 

2283 

2283 

2290 

fE 

2294 

2297 

2297 

2298 

2298 

2301 

2301 

2301 

2301 

2301 

2302 

2304 

2304 

2309 

2309 

2322 

2322 

2322 

2326 

2326 

2328 

2329 

2341 

2341 

2355 

2356 

2356 

2358 

2369 

2369 

DC006601 

DC006602 

DC005401 

DC005503 

DCW5602 

DC005902 

DC006002 

DC006003 

DC006405 

DC006002 

90101387 

DC007102 

DC007104 

DC007201 

DC007204 

90070286 

DCOD7503 

DJOO2301 

DJOO2302 

DJO02403 

DJW2404 

DFDO5201 

DFW5204 

mm 

PO121688 

DF005501 

DFW5502 

00003402 

DDW3403 

DDW3801 

DDW3804 

DOW1704 

DD004102 

DBW1904 

DDO04103 

DBW2004 

DD004201 

WOO6002 

DD004203 

DDOO6W3 

DDO04501 

DA001603 

DD004502 

DA001702 

DA001703 

DD004503 

DA001901 

DDOO4504 

DA003202 

00071786 

DA003203 

DDOO4601 

Qoo30387 

DDOO4801 

DA003802 

DDOO4804 

DDOO5301 

DD005304 

DEW1301 

DEW1304 

00082686 

DBW1701 

NM 

NM 

NM 

T2 

15.5 

3.8 

NM 

NM 

4 

NM 

NM 

NM 

NM 

NM 

F8 

8.8 

10.9 

NM 

MU 

NM 

nn 

16 

12.6 

NH 

NM 

NM 

NM 

NM 

10.9 

4.8 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

ii29 

25:7 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

10.4 

NM 

3:: 

16.6 

2.8 

NM 

20 

E.03 

20.01 

20.06 

19.98 

20 

20.04 

20 

20.08 

20.04 

20.06 

19.99 

19.96 

20.15 

::i 

Z3 

19.98 

20.01 

20.01 

20.02 

20.05 

20.01 

20.07 

20.1 

18.98 

19.97 

E.02 

20.18 

z.3 

20.09 

19.95 

20.14 

20.01 

18.83 

20.1 

nn 

NM 

NM 

20.02 

20.02 

20.11 

19.89 

20.03 

20.13 

20.21 

20.06 

20.16 

20.11 

20.05 

~~~ 

2o:or 

L8 

E5 

19.w 

4.75 

20.01 

20.1 

20.02 

20.02 

Xenobiotics 

Mipid wet weight 

(0) 

9.7 

:“I 

NM 

13.5 

3.9 

1.8 

7.7 

10.5 

NM 

4.8 

79 

NM 

NM 

NM 

a"6 

0:4 

NH 

NM 

18.6 

:'1'2 

F5 

2.6 

NM 

!?I 

6.3 

NM 

w 

15 

79 

2.1 

NW 

NM 

1.5 

NM 

NM 

:“I 

Y.3 

15.5 

!?6 

::9 

NM 

NM 

7.1 

::2 

11.9 

m 

10.3 

10.2 

0.6 

NM 

m 

NM 

NM 

NM 

NM 

19.98 

ii 

NM 

20.04 

20.17 

20.04 

20.1 

20.03 

NH 

19.99 

NM 

19.99 

NM 

NM 

NM 

NM 

19.94 

20.13 

NM 

El1 

NM 

19.97 

!L% 

20.04 

m 

EL% 

20.03 

NM 

iii 

m 

19.97 

20.11 

NM 

z.w 

NM 

NM 

E 

!LM 

20.04 

NM 

19.99 

NM 

19.94 

NM 

FL4 

ED1 

20.05 

ii 11 

20:14 

20.09 

m 

m 

m 

m 

NM 

NM 

No. of 

Samples in 

Composite 

MA 

MA 

MA 

MA 

MA 

01 

MA 

MA 

WA 

MA 

tt 

03 

05 

03 

03 

03 

02 

MA 

WA 

MA 

MA 

MA 

MA 

MA 

WA 

MA 

WA 

MA 

MA 

MA 

ii? 

ii 

8: 

01 

MA 

MA 

MA 

MA 

MA 

#A 

ii 

01 

03 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

it 

01 

01 

MA 

MA 

WA 

MA 

MA 

MA 

MA 

Sampling 

Date 

840919 

840919 

841027 

841027 

840829 

1984 

1984 

19fU 

1984 

1984 

1984 

840920 

840920 

840906 

Ez 

840817 

840809 

840809 

850918 

840918 

840918 

840919 

840919 

850507 

850507 

bD507 

850507 

841120 

a41120 

841127 

841127 

85D422 

850522 

a41128 

841128 

850410 

850410 

850116 

850116 

850116 

850116 

850116 

841101 

841102 

841102 

841026 

841026 

ww19 

840919 

8440919 

840926 

8450926 

840918 

840919 

850423 

840726 

84oEl4 

KY 

840917 

84wl7 

D-6-4 
EDisode SCC Dioxin/Fursns Xenobiotics 

i0. No. Xllpid 

2375 

2376 

2376 

2379 

2379 

2380 

2383 

2385 

2385 

2387 

2387 

2394 

2394 

2394 

2397 

2397 

2410 

2410 

2416 

2422 

2427 

2431 

2427 

2429 

2431 

2427 

2429 

2429 

2430 

2430 

2430 

2432 

2432 

2435 

2435 

2437 

2437 

2439 

2439 

2478 

2478 

2478 

2500 

2500 

2532 

2532 

2544 

2544 

2608 

2608 

2618 

2618 

2618 

2618 

2651 

2653 

2654 

2709 

2721 

2721 

2722 

2725 

2748 

2748 

2776 

2776 

2776 

01003803 

DA003903 

DE000702 

w111886 

DE005401 

DE010202 

DEW5404 

DE005501 

DEW5801 

DE006002 

pD101987 

DE006201 

DE006204 

DE006901 

QDOO6901 

90022189 

DE007201 

DE007204 

DE008501 

DE008504 

DEOWlOl 

DE010203 

PO102887 

DE010702 

DE010402 

DE010703 

DE010403 

GO010687 

DE010602 

DE010603 

GlD121480 

DE010710 

DE010713 

DE011001 

DE011004 

DE011202 

DE011203 

DE011401 

DE011402 

DJO03901 

DJOO3902 

DJO03903 

DC010201 

DC010203 

OF019302 

DF019303 

DFO19202 

DF019203 

DE014501 

DE014504 

DE015401 

DE015402 

OE015403 

pD102088 

D8008401 

DE008503 

D8008601 

D6005101 

DA006502 

a0011089 

DA006601 

DA006301 

131006505 

9‘1006506 

DIM)7101 

DY007103 

CID010489 

7.4 

NM 

NM 

NM 

NM 

NM 

NM 

4 

4.1 

8.5 

NM 

10.8 

NM 

NM 

NM 

NM 

Yl 

NM 

11.2 

24.4 

1.9 

1.7 

NM 

NM 

NM 

1.4 

NM 

NM 

5.6 

3.2 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

NM 

::3 

10.8 

NM 

NH 

1.7 

21.5 

14.7 

i:X 

8.8 

7.6 

3.9 

NM 

?2 

NM 

::3 

NM 

15 

NM 

NM 

net weight 

(9) 

20.09 

19.95 

20.03 

NM 

20.02 

20.03 

20.02 

20 

20.03 

19.98 

g.02 

NM 

:k5 

f8 07 

2o:OO 

20.09 

20.04 

20.12 

20.59 

20.06 

19.98 

20.06 

20.05 

20.06 

19.92 

NM 

20.07 

20.05 

20.75 

20.11 

k3 

20147 

20.16 

:x 03 

20:01 

20.07 

k1 

;:.I8 

20.37 

20.02 

z.07 

20.09 

20.1 

19.99 

:: 04 

20102 

20.48 

20.01 

20 

20.27 

Ko4 

20.05 

20.02 

20.04 

20.02 

20.01 

NM 

Xlipid 

6.8 

5.3 

NM 

3:6 

15.8 

16.9 

3.7 

NM 

NM 

NM 

14 

12.9 

11.4 

5.7 

z.8 

21 

13.7 

29.1 

NM 

NM 

17.1 

NM 

NM 

?I 

417 

!?4 

8.9 

?9 

NM 

m 

17.9 

16.2 

7.1 

:3 

NM 

?2 

NM 

11.4 

10.5 

NM 

g.5 

20.4 

6.3 

12 

!?.I 

3.4 

7.3 

9.3 

6.3 

E 

7.2 

6.3 

::6 

w 

2.6 

uet weight 

to) 

20.01 

20.06 

NM 

NM 

20.07 

20.12 

20.03 

20.09 

NM 

NM 

E.15 

20.05 

20.09 

20.11 

w 

19.99 

20.09 

19.99 

20.03 

20.11 

NM 

ii.1 

NM 

NM 

L7 

20.04 

g.05 

20.12 

NM 

19.w 

NM 

NW 

19.98 

20.15 

20.15 

NM 

20.18 

NM 

NM 

20.04 

:.*2 

20.03 

NM 

w 

19.96 

20.03 

20.06 

20 

NM 

19.97 

20.02 

ii804 

20:02 

20.01 

20.11 

19.93 

20.05 

ii 

NM 

20.11 

No. of 

Samples in 

Coqosite 

01 

MA 

MA 

05 

MA 

MA 

WA 

z 

01 

NA 

03 

03 

03 

MA 

MA 

MA 

MA 

MA 

Ii:. 

i; 

05 

05 

05 

01 

MA 

WA 

00: 

WA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

MA 

WA 

WA 

i: 

O? 

it 

2 

0t 

x: 

01 

MA 

02 

MA 

2 

03 

2 

MA 

MA 

MA 

MA 

MA 

Sampling 

Date 

840828 

840828 

840828 

840927 

840921 

840828 

840717 

840813 

840813 

840821 

840821 

841025 

841025 

841025 

:z 

850619 

850619 

841016 

1984 

841010 

841010 

841010 

840910 

840910 

840910 

841017 

841017 

841017 

841016 

841016 

850603 

850603 

850626 

850626 

841002 

841002 

841025 

841025 

841120 

841120 

841120 

841114 

041114 

850809 

850809 

85On5 

850725 

840801 

840801 

841025 

841025 

841025 

841025 

Kz 

840919 

850618 

850613 

850613 

85M13 

850613 

850630 

850630 

850914 

850914 

850914 
Episode SCC Dioxin/Furans Xencbiotics No. of 

Samples in 

Canposite 

WA 

:: 

02 

01 

2 

01 

02 

01 

02 

01 

8: 

05 

04 

04 

i: 

E 

05 

04 

05 

05 

05 

05 

ii 

Liz 

05 

E 

i5 

07 

05 

03 

05 

02 

03 

05 

05 

05 

05 

05 

ii 

05 

05 

05 

02 

02 

02 

01 

01 

07 

01 

01 

07 

01 

OS 

03 

30 

08 

03 

Sanpling 

Date 

851023 

851023 

860818 

860818 

860818 

EE 

z 

GE: 

860814 

860814 

Ez 

EE 

izE 

860827 

Ez5 

871014 

871014 

ZE 

iEi 

860020 

E 

zz 

860910 

860910 

860911 

860911 

860916 

860916 

871203 

860819 

860819 

860819 

860819 

860819 

860819 

860820 

EE 

871229 

861117 

861117 

861117 

861231 

861231 

861106 

871119 

871119 

861106 

871119 

870507 

830507 

870405 

870404 

870326 

No. No. Xlfpid uet weight 

(cl) 

20.01 

20.01 

20.23 

20.1 

20.02 

20.16 

20.19 

20.04 

19.99 

19.98 

20.13 

20.04 

20.6 

20.01 

20.06 

20.15 

20.1 

20.07 

19.85 

20.02 

20.05 

20.08 

20.02 

19.99 

20.1 

ii:: 

19.98 

20.09 

19.96 

20.11 

E:P 

:.I8 

20.07 

20.11 

19.99 

z.02 

20.06 

20.13 

19.95 

19.93 

20.01 

20 

m 

z.07 

20.03 

20.01 

20.01 

20.06 

20.06 

s.02 

20 

20.03 

20.02 

20.1 

::*02 

20.02 

20.14 

20.08 

20.16 

20.1 

Xlipid 

y6 

Ii.9 

NM 

7.2 

1.3 

4.3 

NM 

2 

NM 

NM 

0.2 

r6 

M 

13.5 

NM 

Y3 

NM 

10 

NM 

17.7 

NM 

9 

NM 

5.1 

NM 

:2 

NM 

14.1 

0.8 

15.5 

9.5 

NM 

::4 

::2 

2.5 

5.4 

10.3 

NM 

13.7 

2: 

14.5 

9 

NH 

NM 

16.4 

2.1 

19.9 

2 

!"2 

15.1 

NM 

NM 

w 

w 

10.3 

5.8 

3 

!Y9 

wet weight 

(0) 

NM 

20.07 

20.06 

tk38 

20.03 

20.18 

L 

NM 

w 

0.04 

NM 

20.11 

NM 

20.07 

NM 

El 

NM 

20.06 

NM 

20 

NM 

19.77 

EL04 

NM 

k6 

NW 

20.07 

20.08 

20.14 

20.12 

NM 

NM 

19.99 

NM 

19.97 

20.02 

20.12 

20.12 

::.01 

:x.12 

20.03 

20 

NM 

k8 

0.42 

0.62 

0.4 

:k4 

20.04 

NM 

NM 

NM 

FL04 

19.w 

20.14 

NM 

20.02 

3001 DE019501 1.6 

DE019502 8.2 

DA008401 21.8 

DA008402 1.4 

DA008501 1.6 

3001 

3022 

3oI2 

3023 

3024 

3025 

3025 

DA008601 0.9 

DA008701 5.2 

DA008702 

DA009001 f.1 

8:X 

3026 

3026 

3027 

3028 

3028 

3034 

3034 

3035 

3035 

DA009301 

DA008801 

00031787 

DC025701 

06025702 

DG025801 

DGO25802 

DGO25901 

1.3 

1.3 

7.9 

0.7 

NM 

1.1 

3036 2.5 

3036 06025902 

DC026001 

DGO26002 

GD120287 

DG026101 

9.5 

3.1 

1.5 

NM 

!!6 

2.2 

1.7 

5.7 

NM 

9 

2: 

lJ.2 

NM 

NM 

9.7 

NM 

NM 

NM 

NM 

4.5 

2.8 

5.7 

10.8 

1.4 

13.7 

1.8 

NM 

NM 

10.3 

0":: 

17 

1.6 

11.9 

NM 

3036 

3037 

3037 

3038 

3038 

3039 

3039 

3040 

3040 

3041 

3041 

3041 

3042 

DC026102 

DGO26201 

DC026202 

DG026301 

DG026302 

DC026402 

am1588 

DGO26501 

DG026502 

90026501 

DG026601 

3042 

3042 

3043 

3043 

3043 

3044 

3044 

3045 

3045 

DGO26602 

w111987 

DC026701 

DC026702 

DGO26801 

DC026802 

DGO26901 

DG027001 

DG027002 

DGO27101 

06027102 

am12689 

3046 

3047 

3047 

3048 

3048 

3048 

3048 

3049 

GDD27101 

DG027201 

DGO27202 

00111087 

DG027301 

DFOO9101 

DFOO9102 

90073189 

DC019105 

DF019106 

DFO24024 

DF024324 

CQO24324 

QDO71587 

SF024324 

DFO23301 

DF023302 

DF023305 

DFO23306 

DFO23419 

3049 

3049 

3050 

3060 

3060 

3060 

3061 

3061 

3062 

::: 

10.4 

5.2 

i:: 

5.2 

9.8 

6.7 

1.8 

6.4 

2.3 

3062 

3062 

3062 

3062 

3063 

3063 

3064 

3064 

3065 

D-6-6 
Episode SCC Dioxin/Furans Xenobi ot i cs 

Xlipid wet weight 

No. of 

Smples in 

Ceraposite 

03 

it 

x; 

E 

M 

05 

05 

04 

04 

8: 

04 

ii 

ii 

02 

03 

09 

: 

05 

:: 

x: 

03 

8: 

it 

03 

05 

MA 

04 

ii 

05 

05 

xz 

05 

ii 

06 

08 

04 

02 

8f 

02 

01 

01 

02 

05 

02 

z! 

ii 

8: 

x: 

San@ ing 

Date 

870326 

870320 

870326 

870409 

87Q4W 

87O320 

870320 

870225 

870225 

870225 

870303 

870303 

870721 

870721 

870623 

870610 

870610 

870623 

810423 

870423 

870423 

861112 

870218 

861203 

870127 

870409 

870409 

870409 

870306 

870306 

870306 

870306 

861125 

861125 

870211 

870211 

870211 

a61209 

a61209 

870212 

870212 

870212 

870305 

870212 

871208 

871208 

870625 

870625 

870625 

870507 

870507 

870507 

810213 

870213 

870213 

870213 

870213 

870213 

870213 

870213 

870508 

870508 

870113 

810113 

871203 

861201 

87O128 

iJ0. No. Xl ipid wet weight 

(6) 

20.04 

!z.2 

2o.ot 

20.03 

20.08 

20.01 

20.04 

19.95 

Z.09 

20.15 

20.07 

z 

20 

19.99 

NM 

19.97 

19.98 

20.02 

20.01 

$8 07 

20:04 

20.19 

20.17 

20.06 

20.03 

20.24 

20.07 

20.03 

20.16 

20.07 

19.98 

20.02 

20.06 

20.17 

20.1 

20.09 

20.28 

20.35 

20.07 

20.11 

19.99 

20.01 

20.02 

20.07 

20.02 

20.03 

!L 

20.1 

20.16 

20.06 

20.04 

20.08 

19.99 

20.08 

20.06 

20.04 

20.1 

20.08 

20.03 

20.17 

20.06 

20.03 

(0) 

20.04 

20.09 

NM 

20.04 

0.23 

0.49 

20.01 

20.13 

0.22 

20.04 

20.03 

0.13 

K 

20.16 

NM 

NM 

19.95 

19.98 

NM 

Et2 

NM 

19.98 

NM 

&6 

NM 

19.93 

20.11 

20.01 

?8l 

19.w 

19.96 

0.06 

:!.D2 

20.03 

19.92 

NM 

NM 

NH 

0.12 

19.73 

NM 

19.95 

0.27 

E.02 

19.99 

k8 

20.05 

20.12 

NM 

NM 

NM 

NM 

NM 

2o.w 

19.94 

20.11 

19.97 

19.96 

19.97 

19.98 

3065 DF023420 

3065 wo107aa 

3065 PO022588 

3066 DF023503 

3066 DFO23504 

8.7 

?6 

14.2 

1.3 

::: 

4.8 

1.5 

NM 

6.3 

6.8 

0.6 

NH 

8.6 

2: 

712 

4.9 

1.1 

4.9 

5.7 

0.7 

12.1 

:06 

NM 

NM 

2.4 

a.3 

NM 

NM 

1.7 

r2 

NM 

::3 

:I 

3.1 

0.8 

::9 

9.6 

11.9 

0.3 

:"I 

5.4 

8.3 

NM 

NM 

r6 

8.1 

!!6 

1.3 

NM 

8.9 

2 

75 

0.7 

3.9 

NM 

NM 

NM 

NM 

::4 

8:; 

4.3 

0.8 

7.8 

2 

3068 DF024Wl 

3068 DFO24002 

3069 DFo24007 

3069 

3070 

3070 

3069 

3071 

3071 

3072 

3072 

3072 

3072 

3073 

3073 

3073 

3074 

3075 

3076 

3076 

3077 

3077 

3077 

3078 

3078 

3078 

3078 

3079 

3079 

3080 

DF0240W 

DFO24DO8 

DF024010 

DF024014 

poo517aa 

DF024015 

DF024017 

DFO24018 

PO040788 

CKlO70688 

DF019221 

DF019222 

w121587 

OF026017 

OF024102 

DF028502 

DFO28503 

DF019113 

DFO19114 

Co12to87 

DFOW118 

DF023815 

OF023816 

SF000118 

DF019205 

DF019206 

DF023317 

DF023318 

QOO4W87 

DF024105 

DFO24106 

DFO23401 

DF023402 

PO120787 

DF023405 

DFO23406 

DFO241W 

cm072188 

DF024113 

DF024114 

SF024113 

DFO234W 

OF023410 

DFO23411 

DFD23413 

DF023414 

DFO23415 

DF023416 

PO023414 

pDoz7.387 

SF023414 

SFO234t5 

DF023417 

DFO234t8 

DF0192W 

DFO19210 

DF019213 

DFo19214 

DF019217 

1 

9.9 

Y2 

0.7 

0.7 

NM 

7.2 

2.1 

6.7 

2 

1.9 

6.3 

0.9 

3.6 

A-1 

418 

a.2 

12.3 

3080 

3080 

3081 

3081 

12.8 

3.1 

5.8 

8.3 

::: 

4.8 

1.3 

8.1 

3082 

3082 

3082 

3083 

3083 

3084 

3o85 

3085 

3086 

3086 

3086 

9.1 

NM 

1 

9.6 

1 

4.6 

1.4 

2 

9.6 

1 

4.6 

8.2 

1.4 

1.1 

4.1 

0.5 

7.2 

3087 

3087 

3087 

3087 

3087 

3088 

~~ 

3090 

3091 1.9 

D-4-7 
Episode SCC DioxitVFurans Xencbiotics No. of 

uet weight Samples in 

Sampling 

Date 

87Ol28 

870430 

87O430 

xz 

870603 

871001 

871001 

871001 

871001 

870930 

830930 

810930 

861118 

861118 

861118 

861024 

861024 

861024 

861024 

861120 

861120 

861118 

861105 

861105 

861217 

861217 

87lJ210 

870210 

860617 

851014 

860811 

860811 

860811 

860729 

EiEz 

861030 

861030 

860815 

860815 

8'10731 

87O731 

87O731 

830929 

870929 

860730 

866730 

860730 

860730 

860750 

860730 

850708 

850708 

850709 

850709 

861009 

861009 

861009 

87O819 

87O819 

87O819 

850917 

Xlipid 

NM 

9.7 

1.5 

0.6 

8 

?9 

NM 

2.9 

13.3 

1.3 

12.2 

m 

1.6 

7 

1 

2.1 

2.9 

NM 

:.3 

NM 

1.6 

4.3 

12.5 

0.6 

8.3 

4.7 

0.9 

2 

NM 

7.7 

0.6 

to 

2.5 

NM 

7.3 

NM 

9.9 

10.9 

0.3 

5.9 

6.3 

5.7 

11.8 

to 

7.8 

8.4 

17.5 

NM 

0.4 

15.8 

1.5 

18.7 

0.4 

NM 

NM 

NM 

5.9 

0.9 

17.4 

1.7 

NM 

22.6 

3.2 

)*I 

a.5 

No. No. Xlipid net weight 

(0) 

20.19 

20.04 

20.09 

19.99 

19-w 

20.02 

20.06 

20.01 

20.1 

20.03 

20.06 

20.05 

20 

20.07 

20 

z.02 

20.34 

20 

NH 

19.97 

19.3 

20.01 

20.05 

2o.w 

20.22 

20.24 

20.t4 

20.13 

19.99 

20.04 

20.14 

20.13 

19.94 

20.34 

20.2 

20.24 

20 

f8 

19.99 

20.16 

20.05 

NM 

20.02 

20.12 

20.05 

!.I3 

20.00 

19.97 

20.13 

2O.M 

NH 

ii 13 

2O:26 

19.99 

19.96 

SEi 

2o:O2 

20.03 

20 

20 

2o.w 

20.11 

(0) 

i&8 

0.3 

19.9 

19.97 

g.02 

NM 

20.05 

20.02 

0.26 

20.u 

:32 

19.96 

0.2 

20 

0.59 

Lo3 

0.46 

T33 

0.87 

20 

0.12 

20.06 

20.08 

19.98 

20.11 

z.13 

20.01 

19.94 

20.1 

NM 

19.99 

NM 

20.05 

19.95 

2O.W 

20.03 

20.02 

20.12 

20.1 

0.8 

0.87 

0.87 

20 

g.05 

19.97 

20.0s 

20.02 

20.06 

w 

NW 

NM 

20.11 

19.97 

Zi:: 

m 

19.99 

20.08 

g.07 

Co+osite 

07 

ii 

04 

04 

04 

05 

05 

02 

05 

03 

05 

05 

:5 

05 

03 

01 

ii 

04 

2 

05 

01 

05 

03 

05 

05 

03 

07 

ii 

ii 

03 

04 

04 

04 

05 

05 

07 

05 

07 

05 

ii 

2 

05 

05 

05 

05 

05 

05 

ii: 

05 

05 

05 

01 

x: 

OS 

z 

OS 

3091 

3103 

3092 

3092 

3093 

3103 

3093 

3093 

3094 

3094 

3095 

3095 

3096 

3096 

3096 

3097 

3097 

3097 

3098 

52 

3098 

3100 

3100 

3101 

DFOt9218 

DFO235Ot 

DF023502 

DFO24011 

DF024118 

QoO8O387 

DC017201 

POW2988 

DC038801 

DCO388O2 

DC035001 

DC035002 

am2488 

DCO387Ol 

DC0387Ot 

PO071989 

DCO386Ol 

DC038602 

CD032587 

CD051288 

DC0197Ol 

DC019702 

DCO199Ol 

0.7 

9.7 

1.7 

0.4 

8 

NM 

7.3 

::‘4 

11.5 

1.7 

11.2 

4.6 

11.2 

4.4 

7.5 

10.7 

NM 

1.9 

3 

2 

::4 

::!I 

DC020001 

DC036201 

DC020002 

DF025Wl 

OF025002 

DC036202 

DE0261101 

DEO268O2 

DE026901 

DEO27OOl 

DE027002 

DE025001 

DE025002 

DE022501 

DHOlS8Ol 

DH0158O2 

DE022401 

DE022402 

DE021101 

DE021102 

00030789 

DE021201 

DE021301 

DE021302 

3106 

3106 

3105 

3105 

3106 

3106 

3107 

3108 

3108 

3109 

3109 

3110 

3111 

3111 

3112 

3112 

3113 

3113 

3113 

3114 

3115 

3115 

3115 

3117 

3117 

3118 

3118 

3118 

3118 

3118 

3118 

3119 

3119 

3120 

3120 

3122 

3122 

3122 

3125 

3125 

3125 

3132 

1.2 

8.6 

4.9 

2.5 

NW 

NM 

7.8 

1.9 

9.1 

1.5 

2.2 

7.3 

1.2 

9.7 

11.8 

NM 

5.6 

7.9 

NM 

11.3 

9.1 

7.2 

NM 

16.3 

a.1 

2.6 

14.6 

7.6 

NM 

NM 

14.6 

2.1 

5.4 

6.3 

1.9 

NM 

1.6 

:i43 

3.; 

PO101689 

DE021501 

DE021502 

DE021601 

DEO216O2 

DE021603 

ooOlO689 

a0020488 

SE0216O2 

DE0217Ol 

DE021702 

DEDZlBOl 

DEO218O2 

DE022001 

DED22W3 

DEO22OO4 

DE022301 

DE022302 

aDc!o888 

DE023201 f :i 

D-6-8 
Episode SCC Dioxin/Furans Xenobiotics No. of 

Samples in 

C-site 

ii 

01 

02 

02 

02 

01 

02 

01 

05 

MA 

04 

01 

01 

04 

01 

03 

05 

03 

02 

01 

02 

03 

03 

04 

04 

03 

05 

03 

03 

05 

E 

01 

03 

03 

01 

01 

01 

03 

02 

05 

2 

05 

01 

09 

ii 

05 

05 

ii 

E 

: 

: 

02 

ii 

E 

06 

02 

05 

Swrpling 

Date 

850916 

850917 

870513 

860513 

860513 

860513 

1986 

830520 

87O520 

890508 

890508 

870903 

870903 

87O902 

8709O2 

870729 

87O326 

870326 

87O326 

860920 

870616 

870616 

870615 

810521 

870910 

870910 

870904 

870904 

8310904 

810904 

861217 

870806 

861118 

861028 

861028 

861017 

861017 

861017 

861017 

a61218 

861218 

890222 

890222 

890222 

890222 

87O513 

890222 

890222 

890222 

890223 

870513 

890223 

870518 

870518 

870519 

87O519 

870519 

870527 

87O527 

am29 

870529 

810529 

870529 

870529 

8710t4 

871015 

Xlipid 

F5 

Y4 

::5 

11.4 

1.1 

:z 

:"I 

NM 

::'B 

3.9 

15 

2.5 

ii.5 

13 

NM 

10 

12.5 

11 

NM 

17.8 

I.9 

NM 

NM 

9;l 

12.7 

0.3 

2.9 

2; 

4.5 

w 

Y9 

2.6 

7.4 

NM 

NM 

MM 

NM 

1.4 

NM 

NM 

NM 

NM 

1.9 

NM 

w 

12.8 

?2 

w 

NM 

7.9 

r1 

T9 

wet weight 

(g) 

NM 

19.97 

::.27 

20.13 

20.06 

20.04 

20.03 

NM 

0.84 

!?I.16 

ii.07 

20.07 

20.02 

20.08 

19.98 

:I09 

20.09 

ii 

20.21 

20.01 

!Ko2 

19.99 

NM 

NW 

19.97 

20.02 

20.06 

20.05 

20 

20.08 

20.1 

NM 

NM 

20.02 

0.52 

20.02 

NM 

NM 

NM 

NM 

20.14 

NM 

NM 

w 

Lz.03 

NM 

Z.09 

K98 

NM 

NM 

19.96 

NM 

19.95 

NM 

20.02 

m 

20.19 

20.06 

No. No. Xlipid wet weight 

(gl 

20.18 

NM 

19.02 

20.33 

20.16 

20.03 

20 

L5 

20.14 

20 

20.06 

20.08 

w 

20.02 

::.03 

19.97 

20.03 

20.1 

20.15 

19.99 

20.18 

20.05 

20.06 

20.01 

20.01 

20.01 

20.05 

20.01 

19.96 

20.2 

20.11 

fX.08 

m 

20 

20.16 

20.05 

20.1 

20.23 

19.99 

20.04 

20.13 

20.04 

20.18 

20.02 

20.01 

20.03 

20.04 

20.13 

20.01 

20.02 

20.06 

20.04 

20.06 

20.02 

20 

19.98 

19.99 

20.04 

20.02 

2O.W 

ii.02 

20.06 

20 

3132 

3132 

3134 

3134 

DE023202 9.1 

90010588 NM 

DE023401 1.9 

DE023403 

DE023405 

DE023406 

DE023501 

DE023601 

DE023602 

DE023701 

DE023702 

DE0238Dl 

DE023802 

DE024001 

DE024002 

DE024101 

DE024102 

5 

3134 

3134 

4.3 

5.2 

3135 11.1 

F9 

9.7 

I.3 

7.9 

2.5 

m3 

NM 

15.8 

2.6 

15.8 

19.6 

10.4 

3 

10.8 

11.1 

10.8 

10.9 

16.3 

1.3 

16.3 

16.3 

9.6 

NH 

1.7 

2.8 

4 

NH 

1.4 

1.4 

3.7 

3.5 

8.2 

3.4 

10.6 

0.8 

0.5 

1.9 

4 

5 

4.1 

0.7 

1.5 

2.6 

2 

14.7 

2.1 

4.6 

1.9 

1.8 

7.2 

1 

2.4 

0.8 

NH 

2.4 

5.3 

0.8 

3136 

3136 

3137 

3137 

3138 

3138 

3140 

3140 

3141 

3141 

3141 

3141 

3142 

DE024103 

SE024102 

DE022502 

DE024401 

DE024402 

DE024403 

DE024901 

DE026601 

90071988 

DE026701 

DE026702 

am6o288 

SE026701 

DC035201 

DE027101 

DE027103 

DC038501 

DA008901 

QD120187 

DA009101 

DA009102 

00072887 

DA009201 

DC019801 

DC019802 

05022121 

DJD22122 

05022123 

05022403 

DJ024001 

05025103 

cQD4w389 

3143 

3143 

3143 

3144 

3145 

3145 

3146 

3146 

3146 

3146 

3147 

3148 

3148 

3149 

3150 

3150 

3151 

3151 

3151 

3152 

3161 

3161 

3162 

3162 

3162 

3162 

3166 

3162 

3162 

3166 

3162 

3163 

3163 

3163 

3163 

3164 

3164 

3165 

3165 

3165 

DJ022402 

DJO22404 

DJ024002 

00015705 

DJ025102 

DDo15701 

DDO15702 

DDO15706 

wo157o3 

DDO157D4 

aDo 

3167 

3167 

3167 

3167 

3167 

3168 

3168 

DD015707 

DD0157O8 

aDo4058a 

am62388 

sD015708 

w015711 

WO15712 

D-6-9 
Episode SCC Dioxin/Furms Xenobiotics 

No. No. Xlipid 

3168 

3169 

3169 

3169 

3170 

31M 

3171 

3171 

3172 

3172 

3173 

3173 

3173 

3174 

3174 

3175 

3175 

3176 

3176 

3177 

3177 

3177 

3178 

3178 

3179 

3179 

3180 

3187 

3181 

3182 

3182 

3183 

3183 

3184 

3184 

3185 

3185 

3185 

3186 

3186 

3187 

3188 

3188 

3189 

3189 

3189 

3190 

31% 

3191 

3191 

3192 

3192 

3192 

3193 

3193 

31% 

31% 

31% 

31% 

3197 

3197 

3198 

3199 

3199 

3199 

3200 

3201 

SD015711 

DDo15713 

DW15714 

CDo227a9 

DD015715 

DDOl5716 

DO015717 

DO015718 

DDOl5719 

DD015720 

DDO15721 

DD015722 

COO70689 

DD015723 

DDOl5724 

DDO15801 

DD015802 

DDO15'303 

DD015804 

DD0158D5 

DDO158D6 

QDlDD488 

DDD15807 

DDO158D8 

DDOl58W 

DD015810 

DDOl5812 

OD015813 

DD015814 

00015815 

DD015816 

DD015817 

DDO158la 

DD015819 

DDO15820 

DDO15821 

DDOl5822 

SD015821 

DDD15823 

QDOl5824 

WO15902 

DDO15903 

DDO15904 

DDOl5905 

DO015906 

90092188 

DD015907 

DD015908 

DJO24003 

D JO24005 

DJO24W7 

DJO24009 

PO020789 

DC039001 

po039001 

OH020104 

DHO20105 

DH020107 

DHOMl08 

DHO201W 

DHOZDllO 

OH020111 

DHO2OlOl 

DHO20102 

DH020103 

DHO20112 

OJO24012 

5.3 

10.2 

NM 

NM 

5.5 

?9 

:c14 

0.6 

0.5 

20.3 

0.6 

0.7 

10.8 

3.4 

1.4 

4.6 

1.2 

9 

1.8 

::3 

0.7 

7.9 

2 

1 

::: 

1.1 

7.4 

7 

0.6 

6.5 

2.2 

6.3 

2.9 

1.7 

2.7 

4.5 

0.4 

4.8 

0.5 

NH 

6.3 

0.7 

1.4 

1.4 

i.2 

1 

3.5 

4.5 

3.9 

8.7 

NM 

1.4 

NM 

3.8 

11.5 

8.4~ 

NM 

4.9 

6.1 

10.3 

Yet weight 

(cl) 

20.06 

20.00 

w 

z.07 

i.02 

FL11 

19.99 

20.07 

20.05 

20.06 

20.09 

20.1 

20.01 

20.05 

l9.W 

20.07 

19.w 

20 

NM 

19.95 

19.w 

19.98 

20.06 

20.08 

20.01 

20.03 

E:E 

20.07 

20.04 

20.01 

20.01 

20.04 

20.21 

20.06 

20.07 

20.03 

20.02 

19.98 

20.1 

20.23 

20.13 

NM 

20.65 

20.1 

20.16 

20.11 

20.15 

20.06 

20.09 

20.02 

20.04 

20.05 

20.09 

Y-21 

:k6 

20.04 

20 

NM 

Xlipid 

NM 

11.3 

NM 

10.7 

6 

Y7 

:6 

0.7 

w 

19.7 

NM 

::9 

2.9 

NM 

3.2 

NM 

7 

NH 

6.7 

3.3 

T2 

:8 

6M8 

X:d 

6.9 

0.3 

IY9 

6.9 

NH 

NM 

NM 

::t 

10.8 

1.9 

6.2 

::8 

5.9 

T7 

1.8 

2 

1.5 

r6 

NH 

ii:: 

:"I 

NM 

NM 

10.2 

10.1 

NM 

4.8 

6.5 

NM 

uet weight 

(9) 

::.I 

:!.I 

19.97 

El04 

NM 

19.9 

19.92 

NM 

20 

NM 

:k8 

20.37 

NM 

19.98 

:L3 

NM 

20.16 

20.32 

NM 

20.08 

NM 

20.11 

i-07 

19.97 

19.97 

20.29 

20 

E 94 

20:12 

NM 

NM 

NM 

20.05 

20.05 

20.04 

20.03 

20 

NM 

19.99 

19.97 

z 02 

2011 

20 

20.14 

ii.09 

z 14 

2o:rt 

k3 

NM 

NM 

20 

20.01 

NM 

20.12 

20.04 

NM 

No. of 

Samples in 

Composite 

02 

05 

ii; 

04 

03 

05 

05 

04 

03 

D4 

02 

ii: 

05 

03 

03 

05 

05 

04 

04 

04 

20 

13 

04 

03 

06 

05 

03 

05 

03 

05 

04 

05 

05 

05 

01 

05 

04 

04 

03 

03 

04 

x: 

03 

04 

04 

05 

it 

WA 

WA 

05 

05 

2 

8: 

05 

05 

05 

02 

03 

02 

05 

MA 

Sampling 

Date 

871014 

871112 

871112 

871112 

871027 

871027 

871028 

871028 

871111 

871111 

870713 

870721 

870713 

87D623 

870623 

870915 

870915 

870626 

870626 

870914 

870914 

870914 

870911 

870911 

870915 

870915 

870923 

871006 

871006 

am13 

870813 

871008 

871008 

870903 

870903 

870915 

870915 

870915 

871124 

871124 

870819 

870707 

870819 

870708 

870708 

870708 

870709 

870709 

870625 

a70625 

a70625 

870625 

87fM25 

870526 

870526 

870819 

870819 

810823 

870823 

870826 

870826 

870822 

870817 

810817 

870817 

870824 

870714 

D-6-l 0 
Episode SCC Dioxin/Furans 

No. No. Xlipid 

3203 

3205 

3205 

3206 

3206 

3206 

3208 

3212 

3212 

3212 

3213 

3217 

3215 

3216 

3216 

3218 

3216 

3216 

3217 

3218 

3219 

3219 

3220 

3220 

3220 

3221 

3221 

3221 

3222 

3222 

3223 

3224 

3226 

3227 

3231 

3231 

3234 

3234 

3235 

3235 

3236 

3236 

3237 

3237 

3237 

3238 

3238 

3241 

3241 

3244 

3245 

3245 

3246 

3246 

3248 

3248 

3249 

3249 

3250 

3250 

3252 

3252 

3252 

3252 

3252 

3256 

3256 

05024018 

DJO24023 

DJ024024 

DJO22301 

05024102 

DJ024103 

DJ0241W 

DJ024120 

DJ024?21 

clDo50388 

DJ024123 

DJ023705 

D JO23707 

D JO23708 

PO022388 

oow1688 

DJ0237W 

DJ023712 

DJ023710 

DJ023713 

DJOU714 

OJO2371? 

D JO23902 

DJ023903 

a0012288 

DJ022405 

OJO23904 

DJO23905 

DJOt3906 

DJ023907 

DJ023717 

DJ023715 

05023721 

DJO23723 

DJ0239lD 

DJ023911 

DH020301 

OH020302 

DH020303 

OH020304 

OH020305 

DH020306 

DH020307 

DH020308 

am8o988 

05023918 

aowo8aa 

OJ023923 

DJ023924 

DJD23622 

DJO23623 

DJO23624 

DJO22108 

DJO221D9 

DJO22502 

clDo50588 

DJO22503 

DJO225D4 

DJO22505 

D JO22506 

D JO22509 

DJO22510 

PO020989 

00052588 

40082288 

05022517 

D JO22518 

4.3 

NM 

:::, 

2 

4.2 

14.1 

NH 

NM 

NM 

2 

9.6 

NM 

88:: 

9.6 

2.9 

7 

3.9 

0.7 

3 

11.4 

3 

25.1 

3.6 

10.9 

1.3 

9.2 

2.5 

9:; 

2.1 

NM 

12.1 

3.2 

NM 

7.4 

NM 

9.5 

3 

:::, 

Y9 

2:r 

Y2 

1.9 

1.1 

4.2 

1.3 

1.6 

6.2 

NM 

Y7 

!"3 

::.5 

NM 

NM 

?9.3 

wet weight 

(Q) 

19.88 

NH 

20 

20.1 

20.03 

20.44 

19.91 

NM 

19.98 

20.17 

NM 

:: 

19.94 

::.os 

20.42 

20.06 

20.09 

20.03 

20.1 

20.02 

20.1 

20.08 

20.11 

20.05 

20.02 

20.21 

sx 07 

2o:r 

20.13 

20.01 

20.02 

:: 08 

19:47 

NM 

19.86 

NM 

19.84 

19.98 

20.09 

20 

ii.03 

20.07 

Lx 

20.05 

20.27 

20.03 

20.04 

20.92 

20 

NM 

NM 

19.98 

::.12 

~~.Ol 

NM 

NW 

19.98 

20.09 

20.57 

Xenobiotics 

Xlipid wet ueight 

8.9 

in7 

NM 

NM 

6 

18.3 

3.4 

6.3 

NM 

5.8 

15.9 

i-t 

717 

NM 

r3 

218 

::3 

0.5 

NM 

15.9 

NM 

NM 

ii.7 

NM 

8 

2.4 

1.9 

2.8 

1.3 

0.7 

15.3 

2.8 

NH 

6.8 

NM 

8.5 

NM 

NM 

7.2 

7.1 

10 

NM 

in9 

NM 

NM 

3.9 

NM 

2.2 

6 

6.3 

0.7 

3.4 

:"8 

0:8 

25 

0.7 

26.6 

MU 

NM 

6.1 

(9) 

20.11 

NM 

19.9 

NM 

::.09 

20.14 

20.02 

20 

NM 

19.99 

20.11 

20.07 

20.06 

20.15 

NM 

NM 

19.98 

20.11 

:i 

20.1 

i2.W 

NH 

NM 

E-13 

:k6 

19.94 

20.18 

20.09 

20.03 

:x 05 

20:01 

:no.o8 

::.09 

NM 

:!I! 11 

20:12 

19.98 

NM 

kx 

NM 

ii.07 

::.01 

20 

20.15 

20.03 

19.97 

NM 

19.9a 

20.13 

20.1 

20.13 

20.12 

NM 

!z!i 

No. of 

Sseples in 

C-site 

03 

04 

01 

MA 

04 

04 

05 

07 

05 

MA 

WA 

WA 

04 

04 

04 

04 

05 

2 

05 

MA 

2 

04 

05 

03 

01 

z; 

05 

11 

2 

20 

04 

03 

04 

05 

02 

04 

02 

04 

zs 

02 

11 

11 

06 

05 

10 

04 

10 

ii 

04 

ii 

02 

10 

06 

04 

ii 

ii 

12 

06 

Sampling 

Date 

870714 

870813 

870813 

870722 

870722 

870722 

870804 

870804 

870804 

8% 

870811 

870819 

870819 

870819 

870819 

870729 

870729 

870819 

870819 

870630 

870630 

870818 

870818 

870818 

890328 

870804 

870804 

810903 

870903 

a70724 

870613 

870904 

870904 

870825 

870825 

870924 

870924 

870915 

870915 

870928 

870928 

870902 

870902 

870902 

870613 

am13 

870612 

870612 

871016 

870618 

870618 

870404 

870404 

870804 

870804 

870804 

EE 

m8o4 

870916 

870916 

870916 

870916 

am916 

871124 

871124 

D-6-11 
Episode SCC Dioxin/Furans Xsnobiotics 

Xlipid net weight 

(a 

No. of 

Samples in 

Composite 

03 

E 

03 

03 

03 

02 

01 

10 

06 

05 

05 

05 

04 

04 

i! 

04 

04 

E 

E 

22 

20 

ii 

iis 

07 

06 

06 

10 

:z 

03 

06 

03 

04 

: 

ifi 

10 

07 

ii 

:; 

20 

10 

03 

xi 

xi 

03 

tz 

03 

03 

ii 

03 

03 

03 

03 

Stapling 

Date 

870812 

870812 

810609 

870609 

870721 

878610 

878729 

870729 

870716 

871119 

871020 

871020 

871020 

871009 

871009 

871009 

871217 

871006 

871006 

871006 

870916 

871210 

871210 

870914 

870914 

870914 

870914 

870913 

870915 

870915 

871014 

871014 

810728 

810903 

870903 

870903 

870616 

830616 

870617 

810616 

878812 

870812 

87oal2 

ma13 

870813 

871119 

871119 

871121 

870921 

870921 

871021 

870714 

870731 

870731 

870731 

870724 

870724 

87o724 

870723 

870723 

870723 

870713 

870713 

870713 

870713 

870713 

a70713 

No. No. Xlipid wet weight 

(g) 

19.99 

19.98 

20.02 

Kl6 

19.w 

ii 14 

20:08 

20 

NM 

20.03 

NM 

20.86 

20 

20.01 

20 

19.99 

20.03 

20.03 

20.26 

20.08 

20.05 

20.01 

20.02 

NM 

19.86 

ii:: 

20.38 

NM 

20.04 

20.08 

w 

20.03 

19.71 

19.99 

20.34 

19.73 

20.07 

NM 

19.98 

20.15 

20.13 

20.1 

g.33 

19.99 

MM 

20.03 

:2 

20:04 

to.00 

20.04 

20.06 

20.04 

20.02 

E 

NM 

20.05 

20.04 

m 

20.23 

19.98 

20.03 

3.73 

20.04 

20.01 

20.07 

20.1 

20.02 

NM 

20.02 

20.34 

NM 

20.04 

20.3 

20.04 

20.13 

20.w 

NM 

NM 

EL9 

NM 

20.04 

NM 

2O.Dt 

19.94 

20.08 

K.11 

k9 

NM 

E 02 

20113 

20.04 

20.2 

20.08 

20.02 

19.91 

19.w 

20.07 

20.02 

20.03 

NM 

20.05 

20.11 

20.03 

19.98 

19.97 

F?7 

26.03 

E:E 

NM 

!.02 

20.09 

h8 

20.05 

19.9 

20.02 

19.98 

20 

NM 

20.07 

20.21 

3258 

3258 

3259 

3259 

3259 

3260 

3261 

3261 

3262 

3264 

3266 

3266 

3266 

3267 

3267 

3267 

3269 

3270 

3270 

3270 

3271 

3272 

3272 

3273 

3273 

3274 

3274 

3275 

3276 

3276 

3278 

3278 

3281 

3282 

3282 

3283 

3285 

3285 

3286 

3287 

3288 

3288 

3288 

3289 

3289 

3290 

3290 

3294 

3294 

DC038901 17 18.6 

a.3 

13.2 

X:i 

17.8 

NM 

7.6 

2 

NM 

0.5 

6.7 

0.7 

1.2 

9 

NM 

NM 

!!9 

z7 

T3 

4.7 

0.1 

!!9 

:"s 

NM 

y5 

8.1 

1.8 

5'-f 

714 

f.6 

i:: 

4.5 

NM 

:.6 

K7 

6.9 

:9 

i:: 

14.7 

NM 

NM 

15.8 

1.7 

5 

::s 

Z:Y 

2.t 

NM 

19.4 

0.6 

DC038902 a.4 

DBWO466 10 

DBWO473 

DBO69lOt 

DBOO0493 

DYO26Wl 

DYO26002 

DY026004 

DYO22602 

DYO22701 

DYO227D2 

90012389 

DYOZtlO? 

DYO22102 

a0020288 

DYD22106 

DYO22107 

DY022108 

SYO22108 

DYO22110 

DY022111 

DY022112 

OYO22113 

DYO22??4 

DYO22115 

DYO22116 

DY022118 

DYO22119 

01022120 

DYO22123 

DY022124 

NM 

8 

3.1 

a.4 

NM 

6.9 

!!4 

9.1 

5.6 

5.2 

::: 

7.2 

9.7 

1.1 

7.6 

6.7 

2 

y7 

11.2 

4.4 

3.3 

NM 

1.7 

10.9 

NM 

57:: 

6.3 

:-: 

214 

NM 

4.5 

4.5 

01022206 

DYO22207 

DY0222W 

DYO22212 

DY022213 

DYO22215 

DYO22216 

DYO22217 

DYO22218 

oD060188 

DY022219 

DYO22220 

DY022221 

DYD22222 

DJD22??? 

DJ022112 

DJD22113 

05022114 

08040101 

06841501 

DBD41504 

SBO41501 

OBO41601 

DBD41604 

pDll2988 

DBO40601 

DBO4WD4 

ul040601 

DBD40201 

DBD40204 

a0021389 

SBD40201 

DBWllOl 

DBD41104 

4.9 

3.6 

0.9 

18.4 

4.4 

NM 

1.5 

1.8 

6 

14.6 

1.1 

14.6 

16.8 

0.7 

:.s 

1.7 

::8 

1.1 

5"-s 

19.7 

0.8 

Z% 

3297 

3297 

3298 

3298 

3298 

3299 

zz 

33w 

3300 

3300 

3300 

3301 

3301 

D-4-12 
Episode See DioxitVFursns 

i0. No. Xlipid 

3301 

3301 

3301 

3302 

3302 

3303 

3303 

3303 

3304 

3304 

3304 

3305 

3305 

3305 

3306 

3306 

3306 

3307 

3307 

3308 

3308 

3309 

3310 

3310 

3311 

3311 

3312 

3312 

3373 

3313 

3314 

3314 

3314 

3314 

3315 

3315 

3316 

3316 

3317 

3317 

3317 

3317 

3318 

3318 

3319 

3319 

3320 

3321 

3321 

3322 

3323 

3324 

3325 

3325 

3326 

3327 

3327 

3328 

332t 

3328 

3328 

3329 

3329 

3330 

3330 

3330 

3331 

PDO3W89 

CID092088 

SB041101 

DBO419Ol 

DBO41904 

DBD42301 

DBO42304 

QDlO258B 

DBO41001 

DBO41004 

90041004 

DBO42DOl 

DBO42004 

QDll038B 

DBO41881 

DBO41804 

fXKl41801 

DBO42101 

CID100588 

DE040001 

PDO30689 

DBD41301 

DC032701 

DC032702 

DC032801 

DC032802 

DC033101 

DC033102 

DC033201 

DC033202 

OCO33301 

DC033302 

SC033301 

SC033302 

DC033401 

DC033402 

DC033501 

DC033502 

DC033601 

DC033602 

SC033601 

SCO336O2 

DC033701 

DC033702 

DBO41401 

90063088 

08041412 

DBO40401 

QDlOO688 

OB040412 

DBO41206 

DE041252 

DBO41218 

DBo41208 

DBO40301 

D8o40315 

DDO29111 

w029112 

SD029111 

SD029112 

DOGl6oo3 

SD016003 

wo291w 

DO029110 

DD029423 

DD016OOl 

NH 

20.4 

19.7 

6.7 

0.6 

5.2 

NH 

NH 

NM 

5.5 

:: 

NM 

Y5 

NM 

::7 

4.6 

0.6 

1.5 

8:: 

0.7 

3 

2; 

1.4 

1.9 

0.8 

10.9 

2.7 

10.9 

$2 

:115 

1:: 

4.7 

4.9 

4.7 

3.9 

0.8 

3.6 

3.8 

3 

3.2 

NM 

2.7 

2.7 

::i 

::: 

;!6 

5.8 

::t 

I.4 

X: f 

1.5 

3.5 

0.5 

3.2 

wet weight 

(cl) 

NM 

20.07 

19.98 

20.04 

20 

20.06 

NM 

:!.I? 

20.11 

?I.01 

20.18 

ii.07 

NM 

EL9 

20.06 

20.02 

20.02 

20 

20.08 

20.01 

20.1 

19.w 

20.01 

20.02 

20.04 

20 

20.05 

19.97 

20.05 

19.97 

20.11 

Y.05 

20.07 

20.07 

20.08 

20.07 

20.08 

20.08 

20.15 

19.98 

20.01 

20.02 

20.19 

:i 24 

20:02 

20.16 

20.06 

20.06 

20.07 

20.04 

20.03 

20.1 

20.1 

20.1 

20.1 

20.01 

20.01 

20.02 

20.12 

19.99 

20.08 

Xenobiotics 

Xlipid wet weight 

0.7 

NM 

NM 

7.1 

0.4 

6.1 

0.7 

6 

0.4 

t:: 

21.2 

1.2 

23.2 

:-: 

6:1 

3.7 

!!I 

r9 

516 

8:; 

9:: 

1.7 

1 

0.5 

10.7 

2.1 

NM 

r5 

:.2 

F.7 

NM 

NM 

:"5 

:16 

3" 

: 

r9 

4.7 

2.3 

212 

i:: 

6.1 

NM 

NM 

Fl 

NM 

r5 

NM 

NM 

(iI1 

20.02 

NM 

NM 

20.08 

20.14 

20.1 

20.1 

20.1 

20.05 

19.w 

20.06 

20.03 

20.14 

20.12 

19.95 

20.03 

20.07 

20.02 

::.03 

NM 

20.06 

20.15 

0.14 

19.93 

0.13 

19.83 

0.34 

%Ol 

19.84 

20.02 

NM 

NM 

19.81 

20.06 

20.24 

NM 

19.96 

NM 

NM 

NM 

19.83 

:: 

l!.Ol 

19.99 

19.99 

NM 

20.14 

20.03 

19.94 

NM 

20.15 

20.11 

20.03 

19.93 

NM 

NM 

:.I 

NM 

RI 

NM 

NM 

No. of 

Samples in 

Composite 

03 

:3A 

03 

03 

03 

03 

03 

03 

ii 

03 

04 

03 

04 

05 

04 

03 

03 

03 

03 

:: 

: 

ii: 

05 

05 

05 

04 

E 

05 

02 

02 

85 

05 

10 

05 

lti 

05 

11 

:A 

:: 

ii 

ii 

34 

10 

2 

E 

ii 

i: 

E 

Sampling 

Date 

870713 

810713 

870713 

870723 

870723 

870630 

870630 

870630 

870827 

870827 

870827 

8709O9 

870909 

870909 

880828 

880828 

880828 

870917 

870917 

870813 

870813 

870724 

871027 

871027 

870928 

870928 

870929 

870929 

871014 

871014 

871007 

871007 

871007 

871007 

870922 

870922 

870924 

870924 

a71015 

871015 

871015 

871015 

870923 

870923 

870616 

870616 

870915 

870630 

870630 

:z 

871002 

870921 

880921 

870921 

870929 

a71002 

880512 

880512 

880512 

880512 

880513 

880513 

88o419 

880419 

880119 

880108 

D-623 
Episode SCC Dioxin/Furene Xenobiotics 

Xlipid wt weight 

(!3) 

No. of 

Samples in 

Carpssite 

01 

02 

02 

i:: 

09 

03 

85 

03 

05 

05 

04 

05 

02 

01 

01 

01 

02 

04 

02 

x: 

02 

z 

08 

03 

ii 

10 

z 

07 

04 

03 

z 

05 

:: 

05 

05 

05 

03 

04 

02 

it 

05 

01 

it 

06 

01 

05 

01 

x: 

E 

z 

ii 

06 

06 

Sampling 

Date 

880108 

a80108 

8aoloa 

880108 

880621 

880621 

a80425 

a80425 

880425 

880425 

880425 

880425 

880425 

880425 

880519 

a80519 

a80519 

880519 

880519 

aaO519 

880407 

880407 

a80407 

a80129 

880129 

880129 

880524 

880524 

880524 

880428 

aa 

880428 

870929 

xz 

870929 

870929 

870929 

a71202 

871202 

871102 

871'102 

871028 

871028 

871028 

871103 

871103 

871103 

871214 

871214 

a71214 

871214 

871214 

880307 

a80307 

880307 

880318 

a80318 

a80318 

a80318 

a80318 

No. No. Xlipid wet weight 

(0) 

20.09 

20.02 

19.99 

19.99 

20.15 

20.18 

20.09 

20.13 

20.01 

20.11 

20.14 

20.11 

19.96 

20.08 

20.04 

20.07 

20.11 

20.23 

NH 

19.w 

20.02 

20.01 

20.09 

20.09 

20.04 

20.06 

19.95 

20.16 

20.08 

20.09 

19.98 

19.98 

20.12 

20.01 

20.1 

20 

19.94 

19.% 

20.04 

20.15 

NM 

19.98 

20.04 

20.15 

20.04 

20 

20.01 

10.01 

20 

20.04 

20 

s:.o5 

20 

20 

20.05 

20.06 

g.05 

20.03 

20.06 

20.03 

19.98 

20.02 

20 

19.98 

20.02 

NM 

20 

NH 

Lo7 

-ONM 

19.99 

NH 

EL6 

iz.04 

!.02 

0.23 

20 

NM 

19.81 

NM 

19.93 

z.02 

19.98 

20.04 

NM 

20.01 

NM 

NM 

L4 

wn 

20 

NM 

NM 

NM 

20.13 

NM 

NM 

20.01 

20.02 

NM 

NM 

z.03 

g.12 

%I4 

NM 

E.07 

NM 

w 

19.88 

20.12 

NM 

NM 

z.05 

NM 

L6 

20.03 

NM 

NM 

NM 

3331 

3331 

3331 

DDOl6002 

DO016007 

DD016008 

SO016008 

DDOlboW 

DD016010 

DDOlbOl? 

DDOl6012 

DDO29?08 

cm121588 

DD016013 

DD016014 

DD016015 

DDOl6016 

DD029101 

DD029102 

DDO29103 

90081588 

90091588 

50016015 

1.1 

5 

2.7 

2.7 

NM 

1.1 

NM 

NM 

14.2 

-ONM 

6.2 

NM 

P4 

NM 

11.3 

Y3 

i:: 

!:6 

NM 

1.6 

:!8 

3 

1.1 

Zl 

NM 

m 

5" 

NM 

7.3 

NM 

NM 

r2 

NM 

T8 

a:2 

NM 

NM 

NM 

13.9 

NM 

1.4 

:c 

NM 

!zl 

NM 

Y9 

2.6 

n 

Ma 

NM 

4.5 

NM 

Y.1 

5.1 

m 

w 

NW 

3331 

3332 13.4 

3332 f.2 

3333 

3333 

3333 

3333 

3334 

3334 

3335 

7.6 

NM 

12.2 

1.5 

13.2 

2.3 

4.8 

2: 

2.1 

NM 

13.2 

2.7 

7.6 

3335 

3335 

3335 

3335 

3335 

3335 

3335 

3336 

3336 

3336 

3336 

3336 

3336 

3337 

3337 

3337 

3338 

3338 

3338 

3339 

3339 

3339 

DDO?6005 

DDOl6006 

DDOl6017 

DDOl6018 

90092288 

DDOl6019 

DDOl6020 

PO051388 

DDOl6021 

DD016022 

DDO29107 

DDOl6023 

DD016024 

a0016023 

DDO29113 

DDO29114 

SO029114 

W016103 

DD016104 

poO8lTBB 

pow27a8 

SD016103 

SD016104 

DD016105 

DD016106 

DDOl6107 

DD016108 

DDDl6lW 

DOD16110 

SDOl6?W 

DDO16111 

DDOl6112 

SO016111 

DD016113 

DD016114 

Cm42088 

SDDl6113 

SD016114 

DD016115 

WOl6116 

SD016115 

D0016117 

WOl6118 

ODO72888 

SD016117 

SD016118 

2 

NM 

0.8 

4.9 

0.6 

7.4 

1.9 

7.3 

0.9 

8.8 

8.8 

0.7 

7.7 

T7 

a:7 

7.7 

0.9 

1.4 

6.9 

3340 

3340 

3341 

3341 

3341 

3341 

3341 

3341 

3342 

3342 

3343 

3343 

3344 

3344 

3344 

3345 

3345 

3345 

3346 

3346 

3346 

3.4 

8.2 

0.9 

8.2 

1.1 

0.5 

2.4 

3.9 

0.9 

4 

3.9 

0.9 

6.1 

1.4 

6.1 

2.1 

5.3 

5.7 

::: 

3346 

3346 

3347 

3347 

3347 

3348 

3348 

3348 

3348 

3348 

D-6-24 
Episode SCC DioxitVFurms Xembiotics No. of 

Staples in 

C-site 

03 

2 

04 

06 

8: 

02 

01 

03 

01 

03 

02 

03 

02 

:z 

ii 

03 

04 

04 

01 

01 

ii 

04 

03 

05 

05 

03 

05 

05 

iz 

i: 

02 

05 

03 

01 

05 

WA 

ii 

06 

03 

04 

05 

04 

05 

:i 

iz 

ii 

06 

03 

03 

MA 

MA 

05 

MA 

03 

SanpLing 

Date 

880218 

880218 

880406 

880406 

880406 

880202 

880202 

880202 

871211 

871211 

871211 

871211 

871210 

871210 

871210 

871114 

871114 

871119 

871119 

871119 

871118 

871118 

871202 

87?202 

880901 

EE: 

880914 

880914 

880914 

880914 

izz 

Ez 

2% 

880912 

880912 

880912 

a80912 

880901 

880901 

Ei: 

Ez: 

880421 

880810 

880810 

880810 

880810 

8808?D 

880810 

87Wt5 

870915 

870909 

87W?7 

870917 

87W?7 

871007 

871007 

878922 

870922 

No. No. Xlipid wet weight 

(BJ 

::.02 

20.07 

20.13 

%3 

20.12 

20.23 

20.18 

19.99 

$09 

20:1 

20.04 

19.98 

20.01 

20.02 

20.02 

20.06 

20.02 

20.05 

20.05 

20.06 

20.11 

20.01 

20.05 

20.03 

20.01 

20.08 

NM 

20.12 

20.09 

19.99 

19.99 

20.05 

20.04 

20.05 

20.07 

19.98 

20 

20.01 

20.1 

NM 

19.97 

20.03 

19.97 

20.15 

20.07 

20.12 

20.13 

20.?4 

20.05 

NM 

20.14 

20.07 

20.03 

20.03 

20.13 

20.03 

20.03 

20.09 

20.01 

20.04 

20.07 

20.09 

20.02 

20.06 

XLipid 

5.8 

NM 

10.4 

0.9 

NH 

NM 

9.7 

NM 

1 

E 

NU 

2.6 

6.3 

NM 

9.2 

0.8 

6.5 

0.6 

NM 

10.1 

NM 

NM 

22.7 

6.9 

NM 

NM 

19.3 

0.8 

1.4 

NM 

13 

0.5 

NM 

14.7 

1 

NM 

1.5 

NM 

12 

2'17 

617 

8.1 

NM 

NM 

12.3 

0.6 

11.7 

1.4 

6.1 

r2 

NM 

11.7 

0.6 

10.3 

2.1 

16.9 

NM 

2.3 

10.4 

i:: 

NM 

NM 

NM 

uet weight 

(0) 

20.05 

:i 

19.99 

NM 

NM 

19.99 

ii.09 

19.74 

20.05 

NM 

19.96 

19.74 

NM 

20.01 

19.99 

19.97 

19.98 

NM 

19.66 

NM 

:;.02 

20.06 

NM 

NM 

19.97 

0.16 

0.29 

g.03 

0.09 

z.12 

0.2 

NM 

f9.98 

NM 

19.96 

:!.OS 

20.11 

20 

NH 

m 

19.98 

20.1 

19.98 

20.01 

20.03 

!.I2 

:z 

20.08 

20 

20.02 

20.06 

Ku6 

20.12 

20.02 

20.04 

NM 

NM 

NM 

3349 DD016119 

DDO16120 

DD016121 

DD016122 

PO052688 

D0016123 

DD016124 

CID021888 

DFO23723 

DF02372h 

PO022089 

8.5 

1.5 

10.6 

0.5 

NM 

1.2 

10.3 

7.7 

3349 

3350 

3350 

3350 

3351 

3351 

3351 

3352 

3352 

3352 

3352 

3353 

3353 

1.3 

5.5 

NU 

NM 

3 

6.2 

2.9 

8.4 

1.1 

7.5 

CD091388 

DFO24121 

DF024122 

QDO24121 

DYO22301 

OYO22302 

3353 

3354 

3354 

3355 

3355 

3355 

3356 

3356 

3357 

3357 

3360 

3360 

Z% 

3375 

3375 

0‘1022303 

01022304 

SYO22303 7.5 

DE030201 10.4 

SE030201 10.4 

DYO22223 0.5 

DY022224 18.5 

DDO29?17 

cm022389 

DD0'16305 

DD029118 

DD016386 

a0071189 

po101188 

OD016307 

DD016388 

6.7 

5.9 

16.9 

1.4 

NM 

1.9 

18 

12.6 

2.4 

1.7 

12.7 

1.3 

12.7 

7.4 

1.6 

10.8 

2.7 

3375 

3376 

3376 

3376 

3377 

3377 

3377 

3378 

PO050389 

DDDl43W 

3378 

3378 

DO016310 

SD016309 

DD016311 

DDDl6312 

DD029115 

DD029116 

DD016401 

po101888 

DD016421 

OD016422 

3385 

3416 

3385 

3395 

3416 

33% 

33% 

3401 

3401 

3403 

3103 

3404 

2: 

zz 

3409 

341t 

3412 

3412 

3412 

3414 

3414 

3415 

3415 

3416 

SDOl642? 

DD0165W 

DD016510 

DD0'16513 

DD016514 

DD0?6515 

00016516 

PO016515 

SD016515 

DBO40701 

DE040706 

DBO40501 

DE040901 

DBO40907 

SBO40907 

DC036203 

DC036204 

DC036205 

DC036206 

DF025211 

DF025212 

DF025210 

4.8 

NM 

8.2 

0.8 

8.2 

11.1 

1.3 

10.7 

6.4 

6.2 

0.8 

NM 

6.2 

12.2 

i-: 

11s 

14.7 

14.7 

0.8 

9.6 

0.8 

11.5 

3.1 

2 

1.6 

D-6-15 
Episode SCC Dioxin/Furms Xenobiotics No. of 

Sanples in 

C-site 

08 

03 

05 

:: 

Flz 

05 

05 

03 

05 

05 

03 

05 

03 

03 

03 

03 

03 

03 

05 

iz 

02 

05 

05 

05 

2 

01 

:t 

it 

04 

x: 

i; 

05 

05 

2 

03 

05 

02 

ii: 

ii 

04 

04 

04 

04 

06 

E 

06 

SempLing 

Date 

890516 

890606 

890606 

881115 

881115 

EE5 

a8cwO7 

880420 

881006 

88O913 

880929 

880914 

88O914 

awl31 

890131 

890131 

Eiz 

GE 

a80927 

810927 

87O926 

87O820 

87O820 

810820 

870820 

890105 

890105 

87O822 

890321 

890327 

890527 

890328 

890328 

890426 

890426 

87O306 

890829 

890829 

890524 

890524 

890718 

890718 

890718 

890718 

890718 

1988 

=18 

8805ia 

890912 

890912 

890912 

890912 

No. NO. Xlipid wet ueight 

(0) 

20.03 

20.01 

20.13 

20.07 

20.01 

20.05 

19.99 

19.99 

19.97 

20.13 

20.02 

20.13 

20.08 

20.12 

20.01 

20.09 

20.03 

20 

20.01 

20.07 

20.05 

20 

19.99 

20.07 

20.05 

20.05 

20.05 

NM 

20 

20.02 

20.11 

20.15 

20.01 

19.99 

20.06 

20.01 

20 

20.11 

20.03 

20.03 

19.98 

20 

20.12 

20.06 

19.99 

20.13 

20.0s 

20.03 

w 

20.07 

20.02 

20.09 

20 

19.97 

20.04 

20.11 

20.02 

20.02 

Xlipid 

w 

7.3 

1.4 

::t 

0.9 

10 

NM 

0.3 

0.8 

7 

F2 

5:7 

w 

Pa 

1 

4.6 

1.7 

2.9 

2.9 

NM 

4 

NM 

4.2 

4.1 

y.6 

NM 

NM 

w 

NM 

NM 

NM 

w 

r1 

10.9 

6.4 

0.8 

NM 

2.2 

w 

0.5 

2.9 

r9 

NM 

w 

w 

w 

NM 

W 

W 

W 

NM 

wet might 

(0) 

0"L 

0127 

0.57 

20.08 

20.09 

20 

55 

20.15 

E.12 

NM 

20 

20.04 

NM 

W 

19.98 

20.01 

20.05 

20.1 

20.14 

20.11 

NM 

19.w 

MM 

19.95 

M.?? 

W 

20 

W 

W 

W 

NM 

W 

NM 

W 

NM 

19.93 

0.82 

0.8 

0.16 

W 

0.45 

71 

0:57 

F58 

W 

W 

W 

W 

W 

W 

W 

W 

W 

3418 

3419 

3419 

3420 

3420 

3421 

3421 

3421 

DFO25007 

DC036207 

DC036208 

DCO362W 

DC036210 

:3 

118 

2.9 

6.2 

DC036211 

SC036212 

DC036213 

DC036212 

DC036214 

DC036215 

DC036216 

DC036217 

DC036218 

OF025005 

DF025012 

wo31389 

DBO69102 

DBO69103 

DBO691O4 

DBO69105 

DBO69106 

DBO69lO9 

D8O69111 

DBO69112 

WO21689 

OBO4080? 

WOI 1889 

DD016601 

DDOl66O2 

DJO22302 

DJO22303 

DJ0223O4 

wQ62289 

DJD22305 

DJO223O6 

DF0243Ol 

WOalOa9 

DFOO9118 

DD016603 

DDO16604 

DD029512 

ww12E!9 

DDO29513 

DD0295?4 

DDOI66O5 

DD016606 

DD029511 

ww1889 

ww2089 

DYO22308 

DYO223W 

DYO223lD 

DY022314 

OF025218 

DFO25219 

DF025220 

90103189 

9.7 

1.2 

7.6 

::: 

9.7 

6.2 

2.1 

4.1 

5.6 

2.3 

2.1 

NH 

NM 

NM 

NM 

NM 

NM 

?!6 

3.6 

NM 

NU 

2.8 

22.6 

3.5 

3422 

3422 

3423 

3423 

3424 

3424 

3425 

3425 

3425 

3426 

3427 

3428 

3429 

3430 

3431 

3432 

3433 

3433 

3434 

3434 

3435 

3435 

3437 

3438 

3439 

3439 

3440 

3441 

3442 

3442 

3443 

3444 

3444 

3444 

3444 

3445 

3445 

3446 

Et 

3446 

3446 

3450 

f:8 

Z:Z 

4 

1.2 

1.1 

a.2 

12.1 

7.1 

1.2 

11.4 

ii:; 

1.2 

:-: 

Nil 

7.8 

1.3 

1.8 

2.1 

::; 

3 

1.2 

2.4 

3450 

3451 

3451 

3452 

3452 

3452 

3452 

D-4-26 
APPENDIX D-7 
TABLE D-7 

List of Confirmation Samples 

S CC No. for SCC No. for 

3062 

3085 

3087 

3087 

3118 

3141 

3146 

3167 

3168 

3185 

3297 

3300 

3301 

3314 

3314 

3317 

3317 

3328 

3328 

3329 

3331 

3335 

3340 

3341 

3341 

3345 

3346 

3347 

3348 

3348 

3355 

3356 

3377 

3395 

DFa24324 SFQ24324 

DFw4113 SF0241 13 

DF023414 SF023414 

DF023415 SF023415 

DE021602 SE021602 

DE024102 SE024 102 

DE02670 1 SE02670 1 

DDOl5708 sDO157os 

DDOl5711 SD01571 1 

DDOl5821 SD015821 

DBO41501 sBO41501 

DBO40201 SBO40201 

DBO41101 sBw1101 

DC033301 SC033301 

DC033302 SC033302 

DC033601 SC033601 

DC033602 SC033602 

DDO29111 SD029111 

DDO29112 SD0291 12 

DDOl6003 SD016003 

DDOl6008 SD016008 

DDOl6015 SD016015 

DDO29114 SD029114 

DDO16103 SD016103 

DDOl6 104 SD016104 

DDOl6111 SD0161 11 

DDO16113 SD0161 13 

DDO16115 SD0161 15 

DDO16117 SD0161 17 

DDOl6118 SD0161 18 

DYO22303 SYO22303 

DE030201 SE030201 

DDOl6309 SD016309 

DDOl6421 SD016421 

DDOl6515 SD016515 

DBO40907 S-7 

DC036212 SC036212 

DF009118 SF0091 18 

D-7-1 
D-7-2 
APPENDIX D-8 

List of Duplicate Samples 
TABLE D-8 

List of Duplicate Samples 

Episode SCC No. for 

1994 DE0 17702 

2070 DJOOO901 

2100 DHOOl703 

2105 DHOO2204 

2126 DDOOO302 

2139 DDOOl604 

2191 MOO5206 

2225 DC006903 

2228 DC007204 

2280 DFOO520 1 

2280 DFOOS204 

2301 D-504 

2322 DBOO1304 

2369 DA003203 

2376 DA003903 

2385 DE006002 

2394 DEOO6!?01 

2427 DE010203 

2427 DE010403 

2429 DE010403 

2430 DE010603 

2618 DE015403 

2721 DA006502 

2776 DYOO7 101 

3028 DA008801 

3036 DGO25901 

3041 DGo26401 

3042 Dam501 

3043 DGO26602 

3048 DGo27101 

3048 DGO27102 

3049 DGO27202 

3060 DlW9101 

3062 DFKMO24 

3062 DFW4324 

3065 DlW3419 

3065 DFO23420 

3069 DxTmm8 

3072 DFO24017 

3072 Dm24018 

3073 DFo19221 

3077 DP019113 

3080 DKl23317 

S CC No. for 

QDI 10586 

QDO72186 

QDlIlO86 

QDO63086 

QDO62686 

QD07 1486 

QDO92486 

QDl01387 

QDO70286 

QDl21688 

QDO62386 

QDO71786 

QDO82686 

QDO30387 

QD111886 

QD101987 

QDOMOl and QD022189 

QDlCn887 

QDOlO687 

QDOlO687 

QDl21486 

QDlO2088 

QDOI 1089 

QDOlO489 

QDO31787 

QD120287 

QDO31588 

QDO26501 

QDll1987 

QDO27101 

QDO12689 

QD111087 

QDO73189 

QDO71587 

QDO2432A 

QDO10788 

QDO22588 

QDO51788 

QDO70688 

QDO40788 

QDl21587 

QD121087 

QDO40987 

D-8-1 
TABLE D-8(Continued) 

Episode SCC No. for 

3082 DE023402 

3084 DFW4109 

3087 DFO23413 

3087 DF023414 

3088 DF023418 

3093 DFO24118 

3093 DFO24118 

3094 DC017201 

3096 DC035002 

3097 DC038701 

3098 DCII38601 

3113 DE021 101 

3115 DE021301 

3118 DE021601 

3118 DE021602 

3125 DE022302 

3132 DE023201 

3 145 DE026601 

3146 DE02670 1 

3150 DA008901 

3151 DA009101 

3 162 DJ025 103 

3165 DDOl5703 

3 167 DDOl5707 

3167 DDOl5708 

3169 DDO15713 

3177 DDOl5805 

3189 DDOl5905 

3192 DJOMO9 

3193 DC039001 

3212 DJO24121 

3216 DJ023708 

3220 DJ023902 

3237 DJO20308 

3238 DJ023918 

3248 DJ022502 

3252 DJ02.2509 

3252 DJO225 10 

3266 DY022701 

3267 DY022101 

3288 DYO22218 

3298 DBO41604 

3299 DBO41601 

3300 DBO40204 

SCC No. for 

QDl20787 

QDO72188 

QD072387 

QDO23414 

QDO91587 

QDO80387 

QDO80387 

QDO92988 

QDO52488 

QD07 1989 

QDO32587 

QW30789 

QDl01689 

QDo20488 

QDOlO689 

QDl20888 

QDOlO588 

QDO71988 

Q-8 

QDl20187 

QDO72887 

QDO41889 

QD03 1788 

QDO40588 

QDO62388 

QDO22789 

QDlOO488 

QDo92188 

QDO20789 

QDO39001 

QDO50388 

QDO22388 and QDO91688 

QDOl2288 

QDOsos88 

QDO80888 

QDO50588 

QDO20989 

QD082288 and QDO52588 

QDO12389 

QDO20288 

QDO60188 

QDll2988 

Q-1 

QDO21398 

D-8-2 
TABLE D-8 (Continued) 

SCC No. for SCC No. for 

3301 

3303 

3304 

3305 

3306 

3307 

3308 

3319 

3321 

3325 

3333 

3335 

3335 

3336 

3337 

3339 

3341 

3341 

3346 

3348 

3350 

3351 

3352 

3352 

3353 

3360 

3375 

3375 

3376 

3385 

3425 

3433 

3434 

3439 

3442 

3452 

DBO41101 QDO92088 

DBO42301 QDlO2588 

DBO41004 QDO41004 

DBO42001 QDllO388 

DBO41801 QDo41801 

DBO42101 QDlOO588 

DBO40001 QDO30689 

DE@41401 QDO63088 

DBO4MOl QD100688 

DBO41218 QDO82988 

DDOl601 I QDl21588 

DDO29101 QDO91588 

DDO29102 QDO81588 

DDOllmS QDO92288 

DDOMOl9 QDO51388 

DDOl6023 QDOl6023 

DIM16103 QDO92788 

DDO16104 QDO81788 

DDOl6113 QDO42088 

DDO16118 QDO72888 

DDOl6121 QDO52688 

DDO16124 QDOl2a88 

DFV23723 QDO22089 

DFO23724 QDO91388 

DFOLMl21 QDOUl21 

DDO29117 QDO2.2398 

DDOl6305 QDlOl188 

DIM16306 QDO71189 

DDO16308 QDO50389 

DDOl6401 QDl01888 

DDO16515 QDOl65 15 

DFO25012 QDO31389 

DBO69112 QDO21689 

DBMO801 QDOll889 

DJO22304 QDO62289 

DF?IMOl QDO81089 

DIWi6O3 QDO!31289 

DDO16606 QDO!Jl889 

DDO295 11 QDO92089 

DKI25218 QD103 189 

D-8-3 
APPENDIX D-9 

Comments Regarding Sample Analyses from EPA Duluth 

Laboratory 
TABLE D-9 

Comments Regarding Sample Analyses From EPA-Duluth Laboratory 

Episode SCC Ho. Comments 

2016 CONC OF DDE TAKEN FROM DILUTION 

2017 

2057 

2110 

2122 

2133 

DFOOllOl XC: 

DF001201 XC: 

DE000601 SC: 

DHOO2710 SC: 

DHOO3904 SC: 

DD001002 XC: 

CONCENTRATION FOR DDE TAKEN FROM DILUTION 

RERUN OF C102OS6LH 

2190 

2194 

DGOO5104 SC: 

DGOO5504 SC: 

xc: 

DC005602 SC: 

DFOO5502 SC: 

DDOO4201 SC: 

xc: 

DDOO5301 SC: 

DDOO5304 SC: 

DBOOl.304 SC: 

DBOO1904 XC: 

SAMPLE NUMBER ASSIGNED AT LAB AND DSR FILLED OUT AT LAB 

DHOO3905 WAS COMBINED WITH DHOO3904 TO MARE THIS SAMPLE 

DDE QUANT. ION SATURATED, DDE CONCENTRATION IS A MINIMUM 

VAL 

NS = NO MORE SAMPLE 

2212 

2283 

2298 

SAMPLE CONTAINER BROKEN POSSIBLE CONTAMINATION 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

RERUN OF D0702S6SN 

2322 

2328 

RERUN FROM CO82686CS,CO70786KJ 

RERUN FROM DO82686CSDO70786IU 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE. 

ORIGINAL WAS FO70786KJ 

ORIGINAL WAS GO707S6IU 

ORIGINAL WAS 1070786KJ 

DDE VALUE HIGHER THAN REPORTED, DUE TO TIME CONSTRAINTS 

UNABLE TO DILUTE SAMPLE 

2358 

2383 

2427 

2429 

2432 

3022 

3039 

3041 

3042 

DA001901 Xc: 

DE005801 Xc: 

DE010202 XC: 

DE010402 XC: 

DE010710 XC: 

DA008401 DC: 

SC: 

DC: 

DGO26202 DC: 

DC: 

QD03158S DC: 

DC: 

DG026501 XC: 

DGO27101 XC: 

QDO27101 XC: 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

CONC FOR DDE TAKEN FROM DILUTION 

CONC FOR DDE AND 4CL-PCB TAKEN FROM DILUTION 

CONC FOR 4CL-PCB TAKEN FROM DILUTION 

CONC FOR DDE TAKEN FROM DILUTION 

1234678 HPCDD HAS LEVEL OF CONTAMINATION BELOW 1.5 PPT 

LEVEL OF CONTAMINATION IN BLANK IS AT 0.6 PFT, 

(QA: 2.5 X BLANK LEVEL) 

PCDD/F BLANK SAMPLE INDICATED 0.5 PPT OF 123567 HXCDD 

AND 5 PPT OF 1234678 HPCDD 

234678 HXCDF CONTAIMINATION BELOW 0.5 PFT 

BLANK LEVEL AT 0.2 PPT (QA: 2.5 X BIhNK LEVEL) 

LOW CHRYSENE Dl2 INTERNAL STD. AREA WILL AFFECT VALUES 

LOW CHRYSENE D12 INTERNAL STD. AREA WILL AFFECT VALUES 

HIGH CHRYSENE DI2 RESPONSE MAY PRODUCE LOWER TA VALUE 

FOR THESE ANALYTES RELATED 

D-9-I 
TABLE D-9(Continued) 

Episode SCC No. Comments 

DM23504 DC: PCDD/F BLANK SAMPLE INDICATED 0.5 PPT OF 123678 HXCDD 

3069 

DC: 

DF024008 DC: 

3085 

3087 

DC: 

DFO23401 XC: 

DFO24109 XC: 

DFO24113 XC: 

DFm3416 xc: 

3092 DFO23502 XC: 

DC017201 XC: 

3095 DC038801 XC: 

3095 DC038802 XC: 

3098 DC038602 XC: 

3100 DC019702 XC: 

3101 DC019!301 Xc: 

3105 DFK25001 XC: 

3109 DE025001 XC: 

3125 DEO2l301 XC: 

31l5 DEO2U02 XC: 

3115 QD01689 XC: 

3117 DE021501 Xc: 

3l34 

3l.34 

3w 

3l38 

3151 

3167 

3168 

3172 

3175 

DE023401 XC: 

DE023402 SC: 

DE023406 XC: 

DE023801 Xc: 

DA009101 XC: 

DDOL5708 SC: ACTUAL OMNIVORE ANALYZED AS BOTTOM FEEDER 

DDOl.5711 XC: DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

DDOl5719 DC: PENTA WINDOW HAD CHROMATOGRAPHY PROBLEMS 

xc: DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

DDOl5802 DC: PCDDiF BLANK SAMPLE INDICATED 0.5 PFT OF 123678 HXCDD 

DC: PCDDiF BLANK SAMPLE INDICATED 0.5 PPT OF 1234678 HPCDD 

AND 0.5 PPT OF 1234678 HPCDD 

1234678 HPCDD CONTAMINATION BELOW 1.5 PPT, BLANK 

CONTAMINATION AT 0.6 PPT 

(GA: 2.5 X BLANK LEVEL) 

XENO SAMPLE DILUTED 10: 1 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

SAMPLE DILUTED 1O:l 

NS = NO MORE SAMPLE, XENO ANALYSIS WAS DONE BUT DID NOT 

MEET XENO QA 

HYDROCARBON PATTERN PRESENT 

DDE QUANT ION SATURATED DDE CONCENTRATION IS A MINIMUM 

VALUE 

CONC FOR DDE TAKEN FROM DILUTION 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

PCB AND DDE-P,P’ VALUES TAKEN FROM DILUTIONS 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

PCB VALUES ARE TAKEN FROM DILUTIONS 

SAMPLE DILUTED 1O:l 

4CLPCB SATURATED SO VALUE REPORTED IS A MINIMUM VALUE 

RECEIVED GROUND SAMPLE ID NUMBER IS 89-578-147 

RECEIVED GROUND SAMPLE ID NUMBER IS 89-567-150 

SAMPLE ID NUMBER IS 89-576-147 

DDE QUANT ION SATURATED DDE CONCENTRATION IS A MINIMUM 

VALUE 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

NS = RECEIVED GROUND. NOT ENOUGH SAMPLE FOR ANALYSIS 

ALL PCB CONCENTRATIONS TAKEN FROM DILUTION 

CONC OF 4CL-PCB TAKEN FROM DILUTION 

4CLPCB SATURATED VALUE REPORTED IS A MINIMUM 

CONCENTRATION 

D-9-2 
TABLE D-9(Continued) 

Episode SCC No. Comments 

3182 DDOl5815 DC: PCDD/F BLANK SAMPLE INDICATED 0.5 PFT OF 123678 HXCDD 

3185 

32M 

DC: 

DDOl.5821 XC: 

DJO24102 DC: 

PCDDn: BLANK SAMPLE INDICATED 05 PPT OF 1234678 HPCDD 

SAMPLE DILUTED 1O:l 

3206 DJ024103 XC: 

3212 DJ024120 XC: 

3212 DJO24l21 XC: 

32l3 DJO24l23 SC: 

3219 DJ0237l.3 XC: 

3231 DJ023911 Xc: 

3245 DJO23623 DC: 

3252 QDO20989 XC: 

3259 DBOOO466 XC: 

3254 DBOOO473 Xc: 

3259 DB069101 XC: 

324% DY022702 XC: 

3272 DY022111 DC: 

3272 DY02211.2 Xc: 

3282 DY02.2206 XC: 

3282 DYO22207 XC: 

3283 DY022209 Xc: 

3288 DY022217 Xc: 

3288 DY02.2218 Xc: 

3289 DYO22220 SC: 

3290 DY022222 XC: 

3299 QDO40601 Xc: 

3300 

3303 

3306 

DBO40201 Xc: 

QD102588 Xc: CONC FOR 4CLPCB TAKEN FROM DILUTION 

QD041801 XC: CONC FOR 4CLPCB AND SCL-PCB TAKEN FROM DILUTION 

PCDD/F BLANK SAMPLE INDICATED 0.5 PPT OF 123678 HXCDD AND 0.5 

PPTOF 1234678 HFCDD 

TO MUCH NOISE IN TRICHLOROBIPHENYL WINDOW (M/Z 256) TO 

QUANT 

CONCENTRATION FOR DDE TAKEN FROM DILUTION 

SAMPLE DILUTED lo:1 

WERE RECIEVED GROUND 

DDE CONCENTRATIONS CALCULATED FROM DILUTED SAMPLE 

DDE CONCENTRATIONS CALCULATED FROM DILUTED SAMPLE 

1234678 HPCDD CONTAMINATION BELOW 1.5 PF’T, BLANK CONTAMINATION 

AT 0.6 PFT, (GA:25 X BLANK LEVEL) 

DOES NOT PASS GA FOR IODONAPHTHALENE BUT CORRELATES WELL 

CONC FOR DDE, 4CL-PCB & SCLPCB ARE TAKEN FROM DILUTION 

CONC FOR ALL PCBS TAKEN FROM DILUTION 

CONC FOR DDE AND PCBS TAKEN FROM DILUTION 

DILUTED SAMPLE BY A FACTOR OF 1O:l 

PCDD/F BLANK SAMPLE INDICATED 0.5 PPT OF 123678 HXCDD AND 0.5 

PFT OF 1234678 HPCDD 

SAMPLE DILUTED 1O:l 

CONC FOR DDE TAKEN FROM DILUTION 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAh4PLE 

SAMPLE DILUTED lo:1 

CONC FOR DDE TAKEN FROM DILUTION 

SAMJ’LE DILUTED lo: 1 

NS = NO MORE SAMPLE 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL 

SAMPLE 

LOW CHRYSENE MAY PRODUCE ELEVATED VALUES FOR TA’S 

RELATED TO QUANTIFICATION 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL 

SAMPLE 

D-9-3 
Episode SCC No. Comments3 

3310 DC032701 XC: INTERNAL STD. AREA FOR CHRYSENE WAS LOW 

3315 

3315 

3317 

3331 

3333 

DC033401 XC: 

DC033402 XC: 

DC033602 SC: 

xc: 

DW16002 XC: 

DD016011 DC: 

3343 DW16108 xc: 

3333 QD12l588 DC: 

3335 DDO29101 Xc: 

3335 a3091588 xc: 

3345 DDo161l2 xc: 

3352 DM23724 Xc: 

3533 DM24121 XC: 

3353 DFO241Z.Z Xc: 

3354 DY022301 Xc: 

3355 DY022303 XC: 

3401 DD016509 XC: 

3401 DD016510 DC: 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

CONC FOR DDE TAKEN FROM DILUTION 

SAMPLE TO SMALL TO FILLET, GROUND WHOLE 

FAILED QA XENOBIOTICS, NO MORE SAMPLE FOR REANALYSIS 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

PCDD/F: DUPLICATE IS oOl2l588 PCDD/F BLANK SAMPLE INDICATED 

05 PPT OF 123678 HXCDD AND 0.5 PPT OF 1234678 HPCDD 

NS = NO MORE SAMPLE XENOBIOTIC ANALYSIS WAS NOT DONE 

PCDD/F: DUPLICATE OF QDO16011 PCDD/F: BLANK SAMPLE INDICATED 

0.5 PPT OF 123678 HXCDD AND 0.5 PPT OF 1234678 HPCDD 

XENO: DUPLICATE OF DDO9l.588, DUPLICATE NOT RUN WITH SET WAS 

MISTAKENLY REASSIGNED BUT DATA USED FOR PRECISION 

XENO: DUPLICATE OF QDCt29101 NOT RUN WITH SET WAS MISTAKENLY 

REASSIGNED BUT USED FOR PRECISION 

NS = NO MORE SAMPLE, XENOBIOTIC ANALYSIS WAS NOT DONE 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

CONC OF DDE TAKEN FROM DILUTION 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

DDE CONC. CALCULATED FROM DILUTED RUN OF ORIGINAL SAMPLE 

DDE CONC. CALCULATED FROM DILUTION RUN OF ORIGINAL SAMPLE 

DDE NUMBER TAKEN FROM DILUTION 

PCDD/F BLANK SAMPLE INDICATED 0.5 PI’T OF 123678 HXCDD AND 0.5 

PPTOF 1234678 HPCDD 

DDO16516 DC: 

3416 DFQ25212 DC: 

3433 DBO69112 Xc: 

PCDD/F BLANK SAMPLE INDICATED 0.5 PPT OF HXCDD AND 0.5 PPT OF 

1234678 HPCDD 

NO WEIGHTS GIVEN 

3443 DFI309118 Xc: 

3450 DY022308 DC: 

3450 DY022309 DC: 

3451 DYO22310 DC: 

3451 DYO22314 DC: 

CHRYSENE-D12 HIGH RESPONSE MAY GIVE LOWER VALUES FOR 

RELATED 

SAMPLE DILUTED 1O:l 

SAMPLE CONTAINS THE FOLLOWING ID NUMBERS: AA 948,949,950,951 

SAMPLE CONTAINS THE FOLLOWING ID NUMBERS: AA 952,953,954,955 

SAMPLE CONTAINS THE FOLLOWING ID NUMBERS: AA 3%,397,398,399 

SAMPLE CONTAINS THE FOLLGWING ID NUMBERS: AA 412,413,414,415 

TABLE D-9 (Continued) 

D-P4 
APPENDIX D-10 

Risk Information for All Sites with Fillet Data 
Table D-10 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Total PCBs 

(Consumption Rate 6.5 @day) 

Epbodt COIN. (D&j Estlmnted Risk Species Location 

3101 5148.1 

3117 5108.2 

3259 4539.41 

3141 4117 

2328 3937.22 

3306 3172.03 

2329 2109.36 

3094 1%1.58 

3110 1804.4 

3113 1614.8 

3193 1w.3 

3120 854.05 

3125 792.96 

3182 780.42 

3115 757.5 

3303 755.66 

3428 697.8 

3118 666.3 

3258 629.76 

3299 610.32 

3104/2212+ 589 

3415 588.7 

3314 502.84 

3301 474.21 

2410 422.66 

3444 380.1 

3100 370.17 

3414 364.8 

3148 363.9 

3172 293.6 

3412 274.7 

3097 270.28 

3409+/2709 256.9 

3312 250.37 

3106+/2608 231.79 

3426 213.34 

3300 205.47 

3427 193.05 

3375 176.6 

Brown Trout PA - Paoli - Little ValIey Creek 

Lake Trout IL - Waukegan - Lake Michigan 

Lm Bass NY -Fort Miller - Hudson R. 

Northern Pike WI - Milwaukee - Milwaukee R. 

Chinook Salmon NY - Olcott -Lake Ontario 

Sm Bass NY - Massena - Grass R. 

Brown Trout NY - Rochester - Lake Ontario 

Channel Catfish PA - Torresdale - Delaware R. 

Carp WI -Hudson - St. CroixR. 

Carp/Channel Catfish IL - Geneva - Fox R. 

Sm Bass VA - Brookneal - Roanoke R. 

Bass MI - Saugatuck - Kalamazoo R. 

White Bass MN - Red Wing - Mississippi R. 

Rock Bass KY - Russelltille - Mud R. 

Catfish IL - East St. Louis - Mississippi River below Sauget 

Sm Bass NY - Newton Falls - Oswegatchie R. 

Bluefish NJ - Newark - Passaic R. 

Walleye MI - E scanaba - Escanaba R. 

spot VA - Norfolk - S. Br. Elizabeth R. 

Lm Bass NY - N. Tonawanda - Niagara R. 

Sm Bass/Lm Bass PA - Philadelphia - Schuylkill R. 

Channel Catfish&m Bass PA - Ransom - N. Br. Susquehanna R. 

White Bass WV - Winfield - Kanawha R. 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Sm Bass MI - Riwr Rouge - Rouge R. 

Channel Catfish/Lm Bass TN - Memphis - Mississippi R. 

White Perch MD - Baltimore - Baltimore Harbor 

Channel Catfish&n Bass PA - Pittston - Susquehanna R. 

Walleye MI - Muskegon - Muskegon Lake 

Lm Bass AL /GA- State Line - Coosa R. 

Sm Bass NY - Oswego - Oswego Harbor 

Brown Bullhead DE - Tybouts Comer - Red Lion Creek 

Lm Bass NY - Peekskill -Hudson R. 

Sm Bass WV - Wheeling - Ohio R. 

Walleye WI - U. Pentenwell Flow - Wisconsin R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Sm Bass NY - Porter - Niagara R. Delta 

Bluefish NJ - Elizabeth - Newark Bay 

Lm Bass GA - Austell - Chattahoochee R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-1 
Table D-10 fCh (coot) 

Episode Cone. (n&g) Estimated Rlrk Species LocrtIon 

3063 163.17 

30% 153.09 

3070 141.a 

3377 137.95 

3068 136.39 

3065 133.2 

3304 127.2 

3298 126.25 

3419 117.92 

3355 113.45 

3310 101 .Ol 

3183 93.79 

3302 93.6 

3305 85.83 

3311 83.22 

3420 82.35 

3048 80.31 

3403 80.05 

3085 77.4 

30% 74‘7 

3114 74 

3146 68.72 

3288 59.37 

3218 55.6 

3079 55.21 

3376 53.77 

3046/2199* 42.63 

23.56 39.62 

3108 37.85 

3216 37.1 

3350 34.07 

3188 32.02 

31&t/2133’ 30.74 

3401 29.66 

3354 25.58 

3313 24.98 

3219 23.91 

3066 21.16 

3429 16.98 

3336 15.25 

3112 12.2 

3069 11.48 

3081 10.45 

3080 10.34 

1 .2x1o-4 

1.1x1o-4 

Spotted Seatrout 

Brown Bullhead 

1.Ox1o-4 

9.9x1o-5 

Sheepshead 

Lm Bass 

9.8~10.’ Atl. Croaker 

9.5x10” 

9. 1x1o-5 

Bigmouth Buffalo 

Northern Pike 

9.ox1o-5 Lm Bass 

8.4~10-~ Freshwater Drum 

8.1~10‘~ Lm Bass 

7.2x1o-5 

6.7x10-” 

Walleye 

6.7~10-~ 

Sauger 

Lm Bass 

6.1~10’~ Sm Bass 

5.9x1o-5 Sm Bass 

5.9x1o-5 Green Sunfish 

5.7x10” White Bass 

5.7x1o-5 Lm Bass 

5.5x1o-5 Black Drum 

5.3x10-’ 

5.3x1o-5 

White Crappie 

4.9xlo-s 

Carp 

4.2x1o-s 

Walleye 

4.Oxlo-5 

Squaw-fish 

4.0x10-~ 

Squawfish 

White Bass 

3.8~10” Lm Bass 

3.1x1o’5 Lm Bass 

2.8x10-’ L m Bass 

2.7x10-’ 

2.7~10.~ 

Walleye 

2.4~10” 

Squawfish 

Lm Bass 

2.3~10-~ Lm Bass 

2.2x10-j Blue Catfish 

2.1x1 o-5 Lm Bass 

1.8x1o-5 Lm Bass 

l.8?rlo-5 Sm Bass 

1.7x1o-5 

1.5?c1o-5 

White Sturgeon 

Freshwater Drum 

1.2x1o-5 Weakfisb 

1. 1x1o-5 

8.7x10a 

Spotted Seatrout 

8.2x10a 

Walleye 

Trout 

7.5x1o-6 White Bass 

7.4x1o-6 Lm Bass 

LA - Moss Lake - Calcasieu R. 

PA - Eddystone - Delaware R. 

TX - Port Arthur - Neches R. (tidal) 

GA - Franklin - Chattahoochee R. 

TX - Morgan Point - Houston Ship Channel 

LA - Baton Rouge - Mississippi R. 

NY - Dexter - Black River Delta 

NY - Buffalo - Buffalo R. 

PA -Erie-Lake Erie 

CA - Stockton - Old Mormon Slough 

PA - Easton - Lehigh R. 

KY - Catlettsburg - Big Sandy R. 

NY - Lewiston - Niagara R. 

NY - Massena - Raquette R. 

WV - New Martinstille - Ohio R. 

PA - Spring Grow - Codorus Creek 

MO - West Alton - Mississippi R. 

TN - Kingsport - S. Fork Holston R. 

TX - Freeport - Brazos R. 

OK - Pyrer Creek - Fort Gibson Resenoir 

IL - Quincy -Mississippi R. 

WI - Rothschild - Wisconsin R. 

CA - Salinas - Blanco Drain 

OR - Wauna - Columbia R. 

OK - Kaw Reservoir 

GA - Whitesburg - Chattahoochee R. 

MO - Lexington - Missouri R. 

ME - Lewiston - Androscoggin R. 

WI - Merrill - Wisconsin R. 

OR - St. Helens -Columbia R. 

TN - Calhoun - Hiwassee R. 

TN - Nickajack Reservoir 

MS - Redwood - Y azoo R. 

TN - Hardin Co. - Tennessee R. 

CA - Stockton - New Mormon Slough 

WV - Bedington - Opequon Creek 

OR - Dalles - Columbia R. 

LA - Union - Mississippi R. 

NJ - Salem - Delaware R. 

GA - St. Marys -North R. (mouth) 

MN - Little Falls - Mississippi R. 

TX - Corpus Christi - Inner Harbor 

TX - Lufkin - Lake Sam Raybum 

LA - Monroe - Ouachita R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-2 
Table D-IO PCBs (coat) 

Episode Cow. (nglg;l Estimated Risk Species lmatloa 

3089 6.93 

3290 6.62 

3282 6.1 

3348 6.04 

323 1 2.89 

3083 1.49 

3252 1.38 

3168 1.36 

3249 1.27 

3092 0.07 

2228 ND 

3036/2 190* ND 

3088 ND 

3093 ND 

3105 ND 

3180 ND 

3212 ND 

3266 ND 

3267 ND 

3308 ND 

3346 ND 

342 1 ND 

3422 ND 

5.ox1o-6 

4.7x1o-6 

4.4x1o-6 

4.3x1o-6 

2. lxlod 

1. 1x1o-6 

9.9x1o’7 

9.7x1o-7 

9. 1x1o-7 

5.0x10-* 

-- 

-- 

_- 

-- 

-_ 

-_ 

-_ 

-_ 

-- 

-_ 

-- 

-- 

-_ 

White Crappie 

Redear Sunfish 

Flethead Catfish 

White Perch 

Sm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Brook Trout 

Warmouth 

L ongear Sunfish 

Bluegill 

BIuegiIl 

Lm Bass 

Lm Bass 

Lm Bass 

Catfish 

Black Crappie 

Rainbow Trout 

Northern Pike 

Lm Bass 

White Perch 

Lm Bass 

OK - Muskogee - Webbers Falls 

CA - Stockton - Port of Stockton 

CA - Calipatria -Alamo R. 

SC - Georgetown - Sampit R. 

WA - Richland - Yakima R. 

LA - Oak Ridge - Bayou Bonne Idee 

ID - Parma - Boise R. 

AL - Mobile - Cold Creek 

ID - Coeur d’Alene - Coeur d’Alene R. 

LA - Hedge - Dugdemons R. 

VA - Carterstille - James R. 

IA - Hamburg - Nishnabotna R. 

LA - Deridder - Anacoco Bayou 

TX - Diboll - Neches R. 

OK - Fort Cobb - Fort Cobb Reservoir 

GA - Early County - Spring Creek 

OR - Owyhee - Owyhee R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

NY - Rouses Pt. - Richelieu R. 

NC - Plymouth - Roanoke R. 

VA - Covington - Jackson R. 

VA - Riwxdale - Backwater R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-3 

Table D-10 (coat) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with DDE 

(Consumption Rate 6.5 #day) 

Episode Cone (p&l EBtlmated Rlrk Speck8 Locatbn 

3282 2820 

3117 1891 

3288 

3444 

3094 

2328 

3113 

3212 

2329 

1 

I 

433 

243.8 

984 

682 

568 

517 

415 

3184/2133+ 343.2 

3141 291 

3193 201 

3118 180 

3219 136 

3115 104 

3083 93.2 

3110 91.5 

3148 85.7 

3252 84 

3097 77.72 

3266 77.1 

3105 75.9 

3401 68 

3168 65.4 

3231 63.6 

3428 60.2 

3258 58.31 

3412 55.6 

3218 52 

3OW21' 99+ 48.8 

3114 46.6 

3415 45.2 

3300 41.4 

3120 35.6 

3301 35.5 

3096 34.38 

3216 34.3 

3414 34 

3104/2212* 33.9 

3172 32.1 

89~10-~ 

6.Ox1O-s 

4.5x1o-5 

3.9xlo-s 

3. lxlo-5 

2.2xlo-s 

l.8xlO-5 

1.6~10-~ 

l.3xlo-5 

1. lxlo-5 

9.2x10d 

6.3~10~ 

5.7x10a 

4.3~10” 

3.3x10d 

2.9x10a 

2.9x106 

2.7~10~ 

2.7~10~ 

2.5~16~ 

2.4~10~ 

2.4~10-~ 

2. lxlOd 

2. lxlo-6 

2.0x10a 

l.9x10a 

1 .sxlO~ 

1.8x10” 

l.6x10a 

l.SxlO~ 

1.5xlO~ 

1.4x10& 

1.3xlO~ 

l.1x10‘6 

l.lxlOd 

l.lxlOd 

1. lxlOd 

1.1x10” 

1. 1xlo-6 

l.oXIOd 

Flathead Catfish CA - Calipatria - Alamo R. 

Lake Trout IL - Waukegan - Lake Michigan 

Squawfish CA - Salinas - Blanc0 Drain 

Channel Catfish/Lm Bass TN - Memphis - Mississippi R. 

Channel Catfish PA - Torresdale - Delaware R. 

Chinook Salmon NY - Olcott - Lake Ontario 

Carp/Channel Catfish IL - Geneva - Fox R. 

Catfish OR - Owyhee - Owyhee R. 

Brown Trout NY - Rochester - Lake Ontario 

Blue Catfish/W. Crappie MS - Redwood - Yazoo R. 

Northern Pike WI - Milwaukee - Milwaukee R. 

Sm Bass VA - Brookneal - Roanoke R. 

Walleye MI - Escanaba - Escanaba R. 

White Sturgeon OR - Dalles - Columbia R. 

Catfish IL - East St. Louis - Mississippi Riwr below Sauget 

Lm Bass LA - Oak Ridge - Bayou Bonne Idee 

Carp WI -Hudson - St. CroixR. 

Walleye MI - Muskegon - Muskegon Lake 

Lm Bass ID - Parma - Boise R. 

Brown Bullhead DE - Tybouts Comer - Red Lion Creek 

Black Crappie AZ - Gila Bend - Gila R. 

Lm Bass OK - Fort Cobb - Fort Cobb Resertroir 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass AL - Mobile - Cold Creek 

Sm Bass WA - Richland - Yakima R. 

Bluefish NJ - Newark - Passaic R. 

spot VA - Norfolk - S. Br. Elizabeth R. 

Sm Bass NY - Oswego - Oswego Harbor 

Squawfish OR - Wauna - Columbia R. 

Lm Bass MO - Lexington - Missouri R. 

Carp IL - Quincy - Mississippi R. 

Channel Cattish/Sm Bass PA - Ransom - N. Br. Susquehanna R. 

Sm Bass NY - Porter - Niagara R. Delta 

Bass MI - Saugatuck - Kalamazoo R. 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Brown Bullhead PA - Eddystone -Delaware R. 

Squawfish OR - St. Helens - Columbia R. 

Channel Catfish/Sm Bass PA - Pittston - Susquehanna R. 

Sm Bass&m Bass PA - Philadelphia - Schuylkill R. 

Lm Bass AL/GA - State Line - Coosa R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-5 
Table D-10 DDE (coat) 

Episode Cone. (pg/g) Esthnattd Risk Species Location 

3065 31.3 

3125 30.6 

3426 27.2 

3079 23.21 

3355 22.1 

3299 21.7 

3304 20.7 

3302 19.8 

3313 19.48 

3100 18.81 

3101 18.8 

2410 15.3 

3085 14.97 

3409+/2709 14.3 

3354 14.1 

3306 13.5 

3290 13.3 

3048 13.1 

3180 13.1 

3310 12.4 

3068 12.2 

3298 11.5 

3377 11.42 

3080 10.66 

3420 10.31 

3081 10.3 

3429 10.2 

3314 10 

3305 9.75 

3066 9.49 

3419 9.47 

3063 8.54 

3375 a.22 

3350 6.27 

3106*/2608 5.57 

3259 5.37 

3312 5.33 

3112 4.69 

3036/2190* 4.61 

3346 4.45 

3376 4.38 

3422 4.35 

3267 3.9 

3348 3.85 

9.9x10-’ 

9.7x10-’ 

Bigmouth Buffalo 

White Bass 

8.6~10-~ Bluefish 

7.3xlo-7 White Bass 

7.0x10-’ Lm Bass 

6.9~18 Lm Bass 

6.5~10.~ Northern Pike 

6.3~10.~ Lm Bass 

6.2~10-~ Sm Bass 

5.9x1o-7 White Perch 

5.9x10-’ Brown Trout 

4.8x10-’ Sm Bass 

4.7xlo-7 Black DNm 

4.5x10-’ Lm Bass 

4.5x10-’ Lm Bass 

4.3x1o-7 Sm Bass 

4.2x1o-7 Redear Sunfish 

4. lxlo-7 White Bass 

4. lxlo-7 L m Bass 

3.%lo-7 

3.9x10-’ 

Walleye 

Atl. Croaker 

3.6~10.’ Lm Bass 

3.6~10-~ Lm Bass 

3.4x10-’ Lm Bass 

3.3x10-’ Green Sunfish 

3.3x10-’ White Bass 

3.2x10-’ Weakfish 

3.2x10-’ White Bass 

3.1x10-’ Sm Bass 

3.0x10-’ Freshwater Drum 

3.Oxlo-7 Freshwater Drum 

2.7~10-~ 

2.6~10.~ 

Spotted Seatrout 

Lm Bass 

2.0x10-’ Lm Bass 

1.8x10-’ 

1.7x10-’ 

Walleye 

Lm Bass 

1.7x1 0.’ Sm Bass 

1.5xlo-7 

1.5x10-’ 

Walleye 

1 .4xlo-7 

Bluegill 

Lm Bass 

1.4x10-’ Lm Bass 

1.4xlo-7 Lm Bass 

1.2x10-’ Rainbow Trout 

12x10-’ White Perch 

LA - Baton Rouge - Mississippi R. 

MN - Red Wing - Mississippi R. 

NJ - Carteret -Arthur Kill R. 

OK - Kaw Resemir 

CA - Stockton - Old Mormon Slough 

NY - N. Tonawanda - Niagara R. 

NY - Dexter - Black Riwx Delta 

NY - Lewiston - Niagara R. 

WV - Bedington - Opequon Creek 

MD - Baltimore - Baltimore Harbor 

PA - Paoli -Little Valley Creek 

MI - Rkr Rouge - Rouge R. 

TX - Freeport - Brazes R. 

NY - Peekskill - Hudson R. 

CA - Stockton - New Mormon Slough 

NY - Massena - Grass R. 

CA - Stockton - Port of Stockton 

MO - West Alton - Mississippi R. 

GA - Early County - Spring Creek 

PA - Easton - Lehigh R. 

TX - Morgan Point - Houston Ship Channel 

NY - Buffalo - Buffalo R. 

GA - Franklin - Chattahoochee R. 

LA - Monroe - Ouachita R. 

PA - Spring Grove - Codorus Creek 

TX - Lufkin - Lake Sam Rayburn 

NJ - Salem - Delaware R. 

WV - Winfield - Kanawha R. 

NY - Massena - Raquette R. 

LA - Union - Mississippi R. 

PA - Erie - Lake Erie 

LA -Moss Lake - Calcasieu R. 

GA - Austell - Chattahoochee R. 

TN - Calhoun - Hiwassee R. 

WI - U. Pentenwell Flow - Wisconsin R. 

NY - Fort Miller - Hudson R. 

WV -Wheeling - Ohio R. 

MN - Little Falls - Mississippi R. 

IA -Hamburg - Nishnabotna R. 

NC - Plymouth - Roanoke R. 

GA - Whitesburg - Chattahoochee R. 

VA - Rixrdale - Blackwater R. 

CA - Anderson - Sacramento R. 

SC - Georgetown - Sampit R. 

I Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-6 
Table D-10 DDE (cant) 

Eplsodc Cow (pg@ Estimated Risk Specks LocatIon 

3403 3.4 

3069 3.33 

3182 3.16 

23% 3.02 

3188 2.85 

3421 2.76 

3308 2.49 

3089 2.46 

3088 2.09 

3108 2.06 

3183 2 

3249 1.99 

3303 1.81 

3146 1.78 

3311 1.51 

3090 1.48 

2228 1.09 

3092 0.81 

3093 0.76 

3070 0.56 

3336 ND 

3427 ND 

1.1x10-’ 

1.1x10-’ 

1.0x10-’ 

9.5x10-* 

9.0x10-* 

8.7x10-* 

79x10-* 

7.8x10-* 

6.6x10-* 

6.5x10-* 

6.3x10-* 

6.3~16~ 

5.7x10-* 

5.6x10-* 

4.8x10-* 

4.7x10-* 

3.4x10-* 

2.6x10-* 

2.4x10-* 

18X10-* 

-- 

mm 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Trout TX - Corpus Christi - Inner Harbor 

Rock Bass KY - Russellville - Mud R. 

Lm Bass ME - Lewiston - Androscoggin RI 

Lm Bass TN - Nickajack Reserwir 

White Perch VA - Covington - Jackson R. 

Northern Pike NY - Rouses Pt. - Richelieu R. 

White Crappie OK - Muskogee - Webbers Falls 

Bluegill LA - Deridder - Anacoco Bayou 

Walleye WI - Merrill - Wisconsin R. 

Sauger KY - Catlettsburg - Big Sandy R. 

Brook Trout ID - Coeur d’Alene - Coeur d’Alene R. 

Sm Bass NY - Newton Falls - Oswegatchie R. 

Walleye WI - Rothschild - Wisconsin R. 

Sm Bass WV - New Martinstille - Ohio R. 

White Crappie OK - Pyrer Creek - Fort Gibson Reserwir 

L ongear Sunfish VA - Cartersville - James R. 

Warmouth LA -Hedge - Dugdemona R. 

Lm Bass TX - Diboll - Neches R. 

Sheepshead TX - Port Arthur - Neches R. (tidal) 

Spotted Seatrout GA - St. Marys -North R. (mouth) 

Bluefish NJ - Elizabeth - Newark Bay 

* Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-io-7 
O-10-8 
Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Dieldrin 

(Consumption Rate 6.5 dday) 

Episode Cone. (a&$ Estimated Risk Specks Locatloa 

3117 405 6.OxlO-4 

3114 187 2.8x10q 

3288 174 2.6~10~ 

3094 83.5 I.2xlo‘4 

3212 74.3 1.1x104 

3046/2199* 70.4 l.1x1o-4 

3115 55.3 8.2~10-~ 

2328 53.5 8.0~10-~ 

3141 50 7.4xlo-5 

2329 47.3 7.ox1o-5 

3282 44 6.5x10-' 

3444 36.6 5.4xlo-5 

3048 26.2 3.9xlo-5 

3118 16 2.4x10-' 

3184/2133* 15.4 2.3~10‘~ 

3258 14.99 2.2?do-' 

3414 14.7 2.2xlo'5 

3036/2190* 14.7 2.2x1o-3 

3068 13.4 2.Oxx1o-s 

3101 13.1 2.Oxlo-s 

3415 11.4 l.7x1o-5 

3113 11.1 1.7xlo-s 

3079 9.96 1.5x10" 

3193 9.76 l.5x1o-5 

3148 9.37 l.4x1o-s 

3066 8.28 l.2x1O-5 

3110 7.73 1.1x10-’ 

3420 7.59 1. lxlo-5 

3100 7.47 1. lxIo-5 

3375 7.06 1 .Ox1o-5 

3096 6.89 l.oxlo-s 

3053 5.91 8.8x10d 

3104+/2212 5.6 8.3~10-~ 

3252 5.5 8.2x10d 

323 1 5.32 7.9x106 

3125 5.17 7.7xlo-6 

3314 4.79 7.1x10d 

3419 4.78 7. lxlo-6 

3312 4.55 6.8x10a 

3310 4.5 6.7x1 Od 

Lake Trout IL - Waukegan - Lake Michigan 

carp IL - Quincy - Mississippi R. 

Squawfish CA - Salinas - Blanco Drain 

Channel Catfish PA - Torresdale - Delaware R. 

Catfish OR - Owyhee - Owyhee R. 

Lm Bass MO - Lexington - Missouri R. 

Catfish IL - East St. Louis - Mississippi R&r below Sauget 

Chinook Salmon NY - Olcott - Lake Ontario 

Northern Pike WI - Milwaukee - Milwaukee R. 

Brown Trout NY - Rochester - Lake Ontario 

Flathead Catfish CA - Calipatria -Alamo R. 

Channel Catfish&m Bass TN - Memphis - Mississippi R. 

White Bass MO - West Alton - Mississippi R. 

Walleye MI - Escanaba - Escanaba R. 

Blue Catfish MS - Redwood - Yazoo R. 

spot VA - Norfolk - S. Br. Elizabeth R. 

Channel Catfish PA - Pittston - Susquehanna R. 

Bluegill IA - Hamburg - Nishnabotna R. 

Atl. Croaker TX - Morgan Point - Houston Ship Channel 

Browu Trout PA - Paoli - Little Valley Creek 

Channel Catfish PA - Ransom - N. Br. Susquehanna R. 

Channel Catfish IL - Geneva - Fox R. 

White Bass OK - Kaw Reservoir 

Sm Bass VA - Brookneal - Roanoke R. 

Walleye MI - Muskegon - Muskegon Lake 

Freshwater Drum LA - Union -Mississippi R. 

Carp WI -Hudson - St. CroixR. 

Green Sunfish PA - Spring Grow - Codorus Creek 

White Perch MD - Baltimore - Baltimore Harbor 

Lm Bass GA - Austell - Chattahoochee R. 

Brown Bullhead PA - Eddystone - Delaware R. 

Spotted Seatrout LA - Moss Lake - Calcasieu R. 

Lm Bass/Sm Bass PA - Philadelphia - Schuylkill R. 

Lm Bass ID - Parma - Boise R. 

Sm Bass WA - Richland - Yakirna R. 

White Bass MN - Red Wing - Mississippi R. 

White Bass WV - Winfield - Kanawha R. 

Freshwater Drum PA - Erie - Lake Erie 

Sm Bass WV - Wheeling - Ohio R. 

Walleye PA - Easton - Lehigh R. 

* Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-9 
Table D-10 Dkldrin (coat) 

Episode Cone. (II&) Estimated Risk Speck8 Loeatloa 

3428 4.47 

3120 4.36 

2410 4.3 

3426 4.13 

3403 3.97 

3301 3.86 

3299 3.69 

3065 3.61 

3377 3.37 

3412 2.59 

3300 2.53 

3311 1.18 

3348 O.% 

3081 0.62 

2228 ND 

23% ND 

3069 ND 

3070 ND 

3080 ND 

3083 ND 

3085 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

3097 ND 

3105 ND 

3 106+/X08 ND 

3108 ND 

3112 ND 

3146 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

3188 ND 

3216 ND 

3218 ND 

3219 ND 

3249 ND 

3259 ND 

3266 ND 

6.6x10& 

6.5~10-~ 

6.4~10~ 

6.1~10~ 

5.%10d 

5.7x106 

5.5x10a 

5.4x10d 

5.0x10d 

3.9x10d 

3.8x10” 

1 .8X10d 

1 .4x10d 

92x10-’ 

-_ 

-_ 

-- 

me 

-- 

-- 

__ 

_- 

-- 

-- 

-- 

-* 

_- 

-_ 

_- 

-- 

^* 

-_ 

-- 

__ 

__ 

_- 

-- 

-- 

-- 

-- 

-- 

-- 

-_ 

_- 

Bluefish 

Bass 

Sm Bass 

Bluefish 

Lm Bass 

Northern Pike 

Lm Bass 

Bigmouth Buffalo 

Lm Bass 

Sm Bass 

Sm Bass 

Sm Bass 

White Perch 

White Bass 

Longear Sunfish 

Lm Bass 

Trout 

Sheepshead 

Lm Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

Lm Bass 

Brown Bullhead 

Lm Bass 

Walleye 

Walleye 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

&luger 

Lm Bass 

Squaw&h 

Squawfish 

White Sturgeon 

Brook Trout 

Lm Bass 

Black Crappie 

NJ - Newark - Passaic R. 

MI - Saugatuck - Kalamazoo R. 

MI - Riwx Rouge - Rouge R. 

NJ - Carteret - Arthur Kill R. 

TN - Kingsport - S. Fork Holston R. 

NY - Olcott - Eighteen Mile Creek 

NY -N. Tonawanda - Niagara R. 

LA - Baton Rouge - Mississippi R. 

GA - Franklin - Chattahoochee R. 

NY - Oswego - Oswego Harbor 

NY - Porter - Niagara R. Delta 

WV - New Martinstille - Ohio R. 

SC - Georgetown - Sampit R. 

TX - Lufkin - Lake Sam Raybum 

VA - Carters&e - James R. 

ME - Lewiston - Androscoggin R. 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

LA - Monroe - Ouachita R. 

LA - Oak Ridge - Bayou Bonne Idee 

TX - Freeport - Brazos R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Reserwir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

DE - Tybouts Corner - Red Lion Creek 

OK - Fort Cobb - Fort Cobb Reservoir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

MN - Little Falls - Mississippi R. 

WI - Rothschild - Wisconsin R. 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Russellville - Mud R. 

KY - Catlettsburg - Big Sandy R. 

TN - Nickaj ack Reservoir 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R 

OR - Dalles - Columbia R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

NY - Fort Miller - Hudson R. 

AZ - Gil8 Bend - Gila R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-10 
Table D-10 Dleldrln (coat) 

Episode Cont. @g/g) Entlmded Rirk Specks Location 

3267 ND -- 

3290 ND _- 

3298 ND -- 

3302 ND __ 

3303 ND -- 

3304 ND -- 

3305 ND __ 

3306 ND __ 

3308 ND _- 

3313 ND __ 

3336 ND __ 

3346 ND __ 

3350 ND _- 

3354 ND _- 

3355 ND __ 

3376 ND -_ 

3401 ND -- 

3409+/2709 ND -_ 

3421 ND _- 

3422 ND __ 

3427 ND -- 

3429 ND _- 

Rainbow Trout 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Spotted Seatrout 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

White Perch 

Lm Bass 

Bluefish 

Weakfish 

CA - Anderson - Sacramento R. 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - Lewiston - Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black R&r Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

WV - Bedington - Opequon Creek 

GA - St. Marys - North R. (mouth) 

NC - Plymouth - Roanoke R. 

TN - Calhoun - Hiwassee R. 

CA - Stockton - New Mormon Slough 

CA - Stockton - Old Mormon Slough 

GA - Whitesburg - Chattahoochee R. 

TN - Hardin Co. - Tennessee R. 

NY - Peekskill -Hudson R. 

VA - Covington - Jackson R. 

VA - Ri\rerdale - Blackwater R. 

NJ - Elizabeth - Newark Bay 

NJ - Salem - Delaware R. 

l Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Combined Chlordane 

(Combined Chlordane is the sum of cis - and trans - chlordane, 

cis - and trans - nonachlor, and oxychlordane) 

(Consumption Rate 6.5 g/day) 

Eplaodc Coat (o&l Estfmated Risk Specks Lmatbo 

3117 770 9.3xlo-s 

3094 291.4 3.5x1o-5 

2328 206.28 2.5~10-~ 

3444 198.3 2.4~10.~ 

3114 160.5 I .9xlo-5 

3141 129.03 1 .6xlO-5 

3115 125.94 1.5x10-’ 

2329 114.41 1 .4xlo-5 

3113 97.6 l.2xlo-5 

3046/2199+ 89.84 1. lxlo-5 

3193 71.23 8.6xlo‘6 

3314 57.36 6.9xlO-6 

3118 53.6 6.5~10-~ 

3258 51.27 6.2xlO-6 

3079 49.72 6.OxlO-6 

3375 40.7 4.9xlo-6 

3415 40.08 4.8x10” 

3148 36.75 4.4x10” 

3312 30.35 3.7xlo-6 

3100 29.48 3.6xlO-6 

3068 28.36 3.4x10d 

3104/2212+ 28 3.4x1o-6 

3282 27.56 3.3x1o-6 

3414 24.3 2.9xlo-6 

3428 23.57 2.8xlo-6 

3377 23.09 2.8x1o-6 

3063 22.35 2.7~10‘~ 

3101 21.28 2.6~10-~ 

3048 20.59 2.5~10-~ 

3096 17.11 2. lxlOA 

3120 15.8 l.9xlo-6 

3097 15.02 l.8xlo-6 

3403 13.77 l.7x10d 

3184/2133+ 13.69 l.7x106 

3427 12.18 l.5xlo-6 

3412 11.31 1.4x10a 

3110 10.87 1.3x106 

Lake Trout 

Channel Catfish 

Chinook Salmon 

Channel Cetfish/Lm Bass 

Carp 

Northern Pike 

Catfish 

Brown Trout 

Carp/Channel Catfish 

Lm Bass 

Sm Bass 

White Bass 

Walleye 

spot 

White Bass 

Lm Bass 

Channel Catfish 

Walleye 

Sm Bass 

White Perch 

Atl. Croaker 

Sm Bass5m Bass 

Flathead Catfish 

Channel Catfish 

Bluefish 

Lm Bass 

Spotted Seatrout 

Brown Trout 

White Bass 

Brown Bullhead 

Bass 

Brown Bullhead 

Lm Bass 

Blue Catfish 

Bluefish 

Sm Bass 

Carp 

IL - Waukegan - Lake Michigan 

PA - Torresdale -Delaware R. 

NY - Olcott - Lake Ontario 

TN - Memphis - Mississippi R. 

IL - Quincy - Mississippi R. 

WI - Milwaukee - Milwaukee R. 

IL - East St. Louis - Mississippi R&r below Sauget 

NY - Rochester - Lake Ontario 

IL - Geneva - Fox R. 

MO -Lexington -Missouri R. 

VA - Brookneal - Roanoke R. 

WV - Winfleld - Kanawha R. 

MI - Escanaba - Escanaba R. 

VA - Norfolk - S. Br. Elizabeth R. 

OK - Kaw Reservoir 

GA - Austell - Chattshoochee R. 

PA - Ransom - N. Br. Susquehanna R. 

MI - Muskegon - Muskegon Lake 

WV - Wheeling - Ohio R. 

MD - Baltimore - Baltimore Harbor 

TX - Morgan Point - Houston Ship Channel 

PA - Philadelphia - Schuylkill R. 

CA - Calipatria - Alamo R. 

PA - Pittston - Susquehanna R. 

NJ - Newark - Passaic R. 

GA - Franklin - Chattahoochee R. 

LA -Moss Lake - Calcasieu R. 

PA - Paoli - Little Valley Creek 

MO - West Alton - Mississippi R. 

PA - Eddystone - Delaware R. 

MI - Saugatuck - Kalamazoo R. 

DE - Tybouts Comer - Red Lion Creek 

TN - Kingsport - S. Fork Holston R. 

MS-Redwood - Yazoo R. 

NJ - Elizabeth - Newark Bay 

NY - Oswego - Oswego Harbor 

WI - Hudson - St. Croix R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-13 
TaMe D-10 Cbbrdme (coot) 

Episode Coat (II&$ Estimated Rirk Specie8 lmrtba 

3212 10.61 

3426 10.14 

3065 10.02 

3313 8.95 

3376 8.88 

3311 8.81 

3310 8.36 

3419 6.8 

3288 6.11 

3300 6.05 

3299 5.59 

3301 5.55 

3350 5.5 

2410 5.49 

3125 5.37 

3183 4.61 

3081 4.5 

3066 4.39 

3420 4.12 

3218 3.4 

3219 3.4 

3421 3.38 

3409+/2709 3.17 

3302 2.76 

3090 2.46 

3401 2.15 

3304 2.04 

3355 2.02 

3267 1.94 

3188 1.83 

3216 1.75 

3306 1.53 

3182 1.38 

3354 0.98 

3298 0.83 

3336 0.69 

2228 ND 

2356 ND 

3036/2190* ND 

3069 ND 

3070 ND 

3080 ND 

3083 ND 

3085 ND 

l.3xlo-6 

l.2x106 

1.2X104 

1. lxlOd 

1. lxlo-6 

l.1xlo-6 

1.0x106 

82x10-’ 

7.4x10-’ 

7.3x10-’ 

6.7x10-’ 

6.7x10-’ 

6.6x10.’ 

6.6x10.’ 

6.5x10-’ 

5.6x10-’ 

5.4xlo-7 

5. 3xlo-7 

5.0x10-’ 

4.1x1 o-7 

4.1x10-’ 

4.1x10-’ 

38x10-’ 

3.3x10-’ 

3.Oxlo-7 

2.6x10-’ 

2.5x1 0.’ 

2.4x10-’ 

2.3~16 

2.2x10-’ 

2.1x10-’ 

1.8x10-’ 

1.7x10-’ 

1.2x10-’ 

1.0x10-’ 

8.3x10-* 

-- 

-- 

-- 

-- 

_- 

-- 

-- 

-- 

Catfish OR - Owyhee - Owyhee R. 

Bluefish NJ - Cartetet - Arthur Kill R. 

Bigmouth Buffalo LA - Baton Rouge - Mississippi R. 

Sm Bass WV - Bedington - Opequon Creek 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Sm Bass WV - New Martinsville - Ohio R. 

Walleye PA - Easton - Lehigh R. 

Freshwater Drum PA - Erie - Lake Erie 

Squawfish CA - Salinas - Blanco Drain 

Sm Bass NY - Porter - Niagara R. Delta 

Lm Bass NY - N. Tonawanda - Niagara R. 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Lm Bass TN - Calhoun - Hiwassee R. 

Sm Bass MI - Riwx Rouge - Rouge R. 

White Bass MN - Red Wing - Mississippi R. 

Sauger KY - Catlettsburg - Big Sandy R. 

White Bass TX - L&in - Lake Sam Raybum 

Freshwater Drum LA - Union - Mississippi R. 

Green Sunfish PA - Spring Grove - Codorus Creek 

Squawfish OR - Wauna - Columbia R. 

White Sturgeon OR - Dalles - Columbia R. 

White Perch VA - Covington - Jackson R. 

Lm Bass NY - Peekskill - Hudson R. 

Lm Bass NY - Lewiston - Niagara R. 

White Crappie OK - Pyrer Creek - Fort Gibson Reserwir 

Lm Bass TN - Hardin Co. - Tennessee R. 

Northern Pike NY - Dexter - Black Riwx Delta 

Lm Bass CA - Stockton - Old Mormon Slough 

Rainbow Trout CA - Anderson - Sacramento R. 

Lm Bass TN - Nickajack Resemir 

Squaw-fish OR - St. Helens - Columbia R. 

Sm Bass NY - Massena - Grass R. 

Rock Bass KY - Russellville - Mud R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass NY - Buffalo - Buffalo R. 

Spotted Seatrout GA - St. Marys -North R. (mouth) 

Longear Sunfish VA - Cartersville - James R. 

Lm Bass ME - Lewiston - Androscoggin R. 

Bluegill IA - Hamburg - Nishnabotna R. 

Trout TX - Corpus Christi - Inner Harbor 

Sheepshead TX - Port Arthur - Neches R. (tidal) 

Lm Bass LA - Monroe - Ouachita R. 

Lm Bass LA - Oak Ridge - Bayou Bonne Idee 

Black Drum TX - Freeport - Brazos R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-11 
Table D-10 Cblordane (cant) 

Epbode Cone (n&j Estimated Rlrk Specler Location 

3088 ND -- 

3089 ND __ 

3092 ND -- 

3093 ND __ 

3105 ND _- 

3 106*/2608 ND _- 

3108 ND -- 

3112 ND -- 

3146 ND __ 

3168 ND _- 

3172 ND _- 

3180 ND -- 

3231 ND -- 

3249 ND -- 

3252 ND _- 

3259 ND -- 

3266 ND _- 

3290 ND __ 

3303 ND -_ 

3305 ND -- 

3308 ND -- 

3346 ND -- 

3348 ND -- 

3422 ND -- 

3429 ND -- 

Bluegill 

White Crappie 

Warmouth 

Lm Bass 

Lm Bass 

Walleye 

Walleye 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Sm Bass 

Brook Trout 

Lm Bass 

Lm Bass 

Black Crappie 

Redear Sunfish 

Sm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

White Perch 

Lm Bass 

Weakfish 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

OK - Fort Cobb - Fort Cobb Reservoir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

MN - Little Falls - Mississippi R. 

WI - Rothschild - Wisconsin R. 

AL -Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

NY - Fort Miller - Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Stockton - Port of Stockton 

NY - Newton Falls - Oswegatchie R. 

NY - Massena - Raquette R. 

NY - Rouses Pt. - Richelieu R. 

NC - Plymouth - Roanoke R. 

SC - Georgetown - Sampit R. 

VA - Rivzrdale - Blackwater R. 

NJ - Salem - Delaware R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

o-10-15 
D-10-16 
Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Heptachlor Epoxide 

(Consumption Rate 6.5 g/day) 

Epbodc Coat. @B(I) E&km&d Rbk Specks L4bcrtkm 

3117 

3114 

311s 

3046/2199+ 

3444 

2329 

3048 

2328 

3079 

3101 

3104/2212* 

3118 

3148 

2228 

2356 

2410 

3036/2190+ 

3063 

3065 

40.7 3.4x1o-s Lake Trout 

25.3 2.2?clo*5 Carp 

10.2 8.6~10~ ChffiSh 

7.91 6.7~10~ Lm Bass 

5.9 5.OxlO~ 

5.06 4.3x10d 

Channel Catfish/Carp 

Brown Trout 

4.15 3.5x10a White Bass 

2.92 2.5~10” Chinook Salmon 

2.87 2.4x10d White Bass 

1.18 l.oxlOd Brown Trout 

1.07 9.0x10” Sm Bass 

0.97 8.2x10-’ 

57x10” 

Walleye 

0.67 Walleye 

ND -- Longear Sunfish 

ND -- Lm Bass 

ND -- Sm Bass 

ND -- Bluegill 

ND -- Spotted Seatrout 

ND me Bigmouth Buffalo 

ND __ Freshwater Drum 

ND -- Atl. Croaker 

ND _- Trout 

ND -- Sheepshead 

ND -- Lm Bass 

ND -m White Bass 

ND -- Lm Bass 

ND -- Black Drum 

ND -- Bluegill 

ND -- White Crappie 

ND -- White Crappie 

ND -- wemlouth 

ND w- Lop Bass 

ND -- Channel Catfish 

ND se Brown Bullhead 

ND -- Brown Bullhead 

ND -- White Perch 

ND -- Lm Bass 

ND -- Walleye 

ND -- Walleye 

ND -- Carp 

IL - Waukegan - Lake Michigan 

IL - Quincy - Misaisaippi R. 

IL - East St. Louis -Mississippi Riwr below Sauget 

MO - Lexington -Missouri R. 

TN - Memphis - Mississippi R. 

NY - Rochester - Lake Ontario 

MO - West Alton - Mississippi R. 

NY - Olcott - Lake Ontario 

OK - Kaw Remir 

PA - Paoii - Little Valley Creek 

PA - Philadelphia - Schuylkill R. 

MI - Escanaba - Escanaba R. 

MI - Muskegon - Muskegon Lake 

VA - Cartersville - James R. 

ME - Lewiston - Androscoggin R. 

MI - Riwzr Rouge - Rouge R. 

IA - Hamburg - Nishnabotne R. 

LA - Moss Lake - Calcasieu R. 

LA - Baton Rouge - Mississippi R. 

LA -Union -Mississippi R. 

TX - Morgan Point - Houston Ship Channel 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

LA - Monroe - Ouachita R. 

TX - Lufkin - Lake Sam Raybum 

LA - Oak Ridge - Bayou Bonne Idee 

TX - Freeport - Brazos R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Re4tIH)ir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Torresdale - Delaware R. 

PA - Eddystone - Delaware R. 

DE - Tybouts Comer - Red Lion Creek 

MD - Baltimore - Baltimore Harbor 

OK - Fort Cobb - Fort Cobb Reser\lloir 

WI -U. Pentenwell Flow - Wisconsin R. 

WI -Merrill - Wisconsin R. 

WI -Hudson - St. CroixR. 

Asteri& indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-17 
Table D-10 Hcptacbbr Eporlde (coat) 

Episode Cone. (a&j Estimated Risk Speck Location 

3112 ND 

3113 ND 

3120 ND 

3125 ND 

3141 ND 

3146 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

3184/2133+ ND 

3188 ND 

3193 ND 

3212 ND 

3216 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3258 ND 

3259 ND 

32f% ND 

3267 ND 

3282 ND 

3288 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3310 ND 

3311 ND 

3312 ND 

3313 ND 

3314 ND 

3336 ND 

-_ 

-- 

-* 

_* 

** 

*- 

** 

-* 

-* 

-* 

** 

** 

*- 

_* 

-* 

** 

** 

*- 

-- 

*- 

-- 

** 

*. 

** 

** 

*- 

** 

** 

** 

** 

-- 

_* 

-* 

*a 

-- 

*s 

-- 

_* 

*- 

-* 

-* 

*w 

ma 

-- 

Walleye MN - Little Falls - Mississippi Ri. 

Channel Catfish/Carp IL - Geneva - Fox R. 

Bass MI - Saugatuck - Kalamazoo R. 

White Bass MN - Red Wing - Mississippi R. 

Northern Pike WI - Milwaukee - Milwaukee R. 

Walleye WI - Rothschild - Wisconsin R. 

Lm Bass AL - Mobile - Cold Creek 

Lm Bass AL/GA - State Line - Coosa R. 

Lm Bass GA - Early County - Spring Creek 

Rock Bass KY - Russellville -Mud R. 

Sauger KY - Catlettsburg - Big Sandy R. 

Blue Catfish/W. Crappie MS-Redwood - Yazoo R. 

Lm Bass TN - Nickajack Reservoir 

Sm Bass VA - Brookneal - Roanoke R. 

Catfish OR - Owyhee - Owyhee R. 

Squawfish OR - St. Helens-Columbia R. 

Squawfish OR - Wauna - Columbia R. 

White Sturgeon OR - Dalles -Columbia R. 

Sm Bass WA - Richland - Yakima R. 

Brook Trout ID - Coeur d’Alene - Coeur d’Alene R. 

Lm Bass ID - Parma -Boise R. 

spot VA - Norfolk - S. Br. Elizabeth R. 

Lm Bass NY - Fort Miller - Hudson R. 

Black Crappie AZ - Gila Bend - Gila R. 

Rainbow Trout CA - Anderson - Sacramento R. 

Flathead Catfish CA - Calipatria -Alamo R. 

Squaw-fish CA - Salinas - Blanco Dram 

Redear Sunfish CA - Stockton - Port of Stockton 

Lm Bass NY - Buffalo - Buffalo R. 

Lm Bass NY - N. Tonawanda - Niagara R. 

Sm Bass NY - Porter - Niagara R. Delta 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Lm Bass NY - Lewiston - Niagara R. 

Sm Bass NY - Newton Falls - Oswegatchie R. 

Northern Pike NY - Dexter - Black River Delta 

Sm Bass NY - Massena - Raquelte R . 

Sm Bass NY - Massena - Grass R. 

Northern Pike NY - Rouses Ft. - Richetien R. 

Walleye PA - E aston - Lehigh R. 

Sm Bass WV - New MartinsviJJe - Ohio R. 

Sm Bass WV - Wheeling - Ohio R. 

Sm Bass WV - Bedington - Opequon Creek 

White Bass WV - Winfield - Kanawha R. 

Spotted Seatrout GA - St. Marys - North R. (mouth) 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-18 
Table D-10 Heptachlor Eposlde (cant) 

Ephode COIN. (n&) Estimated Rlrk Speck Location 

3346 ND me 

3348 ND -- 

3350 ND -- 

3354 ND -- 

3355 ND -- 

3375 ND __ 

3376 ND -- 

3377 ND -- 

3401 ND __ 

3403 ND -- 

3409*/2709 ND __ 

3412 ND -- 

3414 ND -- 

3415 ND -- 

3419 ND -- 

3420 ND -- 

342 I ND -- 

3422 ND -- 

3425 ND __ 

3427 ND -- 

3428 ND __ 

3429 ND -- 

3446 ND -- 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - Austell - Chattahoochee R. 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA -Franklin - Chattahoochee R. 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill -Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel Cattish/Sm Bass PA - Pittston - Susquehanna R. 

Channel CattishISm Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grow - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Riwxdale - Backwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

Striped Bass KY - Catlettsburg - Big Sandy R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

O-10-19 
D-IO-20 
Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Alpha-BHC 

(Consumption Rate 6.5 &day) 

Episode Cow. (II&) Estlmrtcd Rlrk Speckr Location 

3258 17.48 

3068 10.1 

3117 5.48 

2329 4.76 

3100 4.27 

3414 3.63 

3141 3.31 

3063 3.23 

3094 2.78 

3312 2.57 

2328 2.27 

3104*R212 1.58 

2410 1.45 

3114 1.45 

3415 1.43 

3184/2133+ 1.39 

3426 1.13 

3097 1.1 

3110 1.0s 

3377 1.02 

3299 0.9 

3113 0.79 

3048 0.76 

3412 0.73 

3444 0.73 

33&5 0.72 

3096 0.64 

3081 0.58 

3083 0.43 

3120 0.42 

3420 0.39 

3125 0.34 

3118 0.18 

2228 ND 

23% ND 

3036/2190+ ND 

3046/2199* ND 

3065 ND 

3056 ND 

3069 ND 

1 .ox1o-s 

5.%10d 

3.2x10a 

2.8x10d 

2.5~10~ 

2. lxlOd 

19x10~ 

19x10~ 

1.6~10~ 

l.5x10d 

1.3x10d 

92x16’ 

8.5~10” 

8.5x10-’ 

8.4x10-’ 

8.1x10-’ 

6.6x10” 

6.4~10” 

6.3x10” 

60x10-’ 

5.3x10-’ 

4.6x10-’ 

4.4x10-’ 

4.3x10.’ 

4.3x10-’ 

42x10-’ 

3.7x10.’ 

3.4x10.’ 

2.5~10” 

2.5x10-’ 

2.3x10-’ 

2.0x10-’ 

1.1x10-’ 

spot 

Atl. Croaker 

Lake Trout 

Brown Trout 

White Perch 

Channel Catfish 

Northern Pike 

Spotted Seatrout 

Channel Cattish 

Sm Bass 

Chinook Salmon 

Lm Bass 

Sm Bass 

Carp 

Channel Catfish 

Blue Catfish 

Bluefish 

Brown Bullhead 

Carp 

Lm Bass 

Lm Bass 

Channel Catfish 

White Bass 

Sm Bass 

Channel Catfish 

Sm Bass 

Brown Bullhead 

White Bass 

Lm Bass 

Bass 

Green Sutish 

White Bass 

Walleye 

Longear Sunfish 

Lm Bass 

Bluegill 

Lm Bass 

Bigmouth BuffaIo 

Freshwater Drum 

Trout 

VA - Norfolk - S. Br. Elizabeth R. 

TX - Morgan Point - Houston ship Channel 

IL - Waukegan - Lake Michigan 

NY - Rochester - Lake Ontario 

MD - Baltimore - Baltimore Harbor 

PA - Pittston - Susquehanna R. 

WI - Milwaukee - Milwaukee R. 

LA -Moss Lake - Calcasieu R. 

PA - Torresdale - Delaware R. 

WV -Wheeling-Ohio R. 

NY - Olcott - Lake Ontario 

PA - Philadelphia - Schuylkill R. 

MI - Riwzr Rouge - Rouge R. 

IL - Quincy - Mississippi R. 

PA - Ransom - N. Br. Susquehanna R. 

MS - Redwood - Yawo R. 

NJ - Carteret - Arthur Kill R. 

DE - Tybouts Corner - Red Lion Creek 

WI -Hudson - St. CroixR. 

GA -Franklin - Chattahoochee R. 

NY - N. Tonawanda - Niagara R. 

IL - Geneva - Fox R. 

MO - West Alton - Mississippi R. 

NY - Oswego - Oswego Harbor 

TN - Memphis - Mississippi R. 

NY - Massena - Grass R. 

PA - Eddystone - Delaware R. 

TX - Lufkin - Lake Sam Raybum 

LA - Oak Ridge - Bayou Bonne Idee 

MI - Saugatuck - Kalamazoo R. 

PA - Spring Grove - Codorus Creek 

MN - Red Wing - Mississippi R. 

MI - Escanaba - Escanaba R. 

VA - Cartersville - James R. 

ME - Lewiston - Androscoggin R. 

IA -Hamburg - Nishnabotna R. 

MO - Lexington - Missouri R. 

LA - Baton Rouge - Mississippi R. 

LA - Union - Mississippi R. 

TX - Corpus Christi - Inner Harbor 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-21 
Table D-10 Alpha-BHC (cod) 

Ephode Cow. @g/g) Eatimated Rink Spcckr Location 

3070 ND 

3079 ND 

3080 ND 

3085 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

3101 ND 

3105 ND 

3106*/2608 ND 

3108 ND 

3112 ND 

3115 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

3188 ND 

3193 ND 

3212 ND 

3216 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3259 ND 

3266 ND 

3267 ND 

3282 ND 

3288 ND 

3290 ND 

3298 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

-- 

-- 

-- 

__ 

-_ 

-- 

__ 

-- 

-_ 

_- 

me 

_- 

-- 

-_ 

_- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-- 

-_ 

_- 

-- 

-- 

-- 

_- 

_- 

-- 

mm 

_- 

-_ 

-- 

_- 

-- 

-- 

-w 

Sheep shead 

White Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

Lm Bass 

Brown Trout 

Lm Bass 

Walleye 

Walleye 

Walleye 

Catfish 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sauger 

Lm Bass 

Sm Bass 

Catfish 

Squaw-fish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Catfish 

Squawfish 

Redear Sunfish 

Lm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

TX - Port Arthur - Neches R. (tidal) 

OK - Kaw Resmir 

LA - Monroe - Ouachita R. 

TX - Freeport - Brazes R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson ReseI-croir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Paoli - Little Valley Creek 

OK - Fort Cobb - Fort Cobb Resemir 

WI - U. Pentenwell FIow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

MN - Little Falls -Mississippi R. 

IL - East St. Louis - Mississippi Riwr below Saugct 

WI - Rothschild - Wisconsin R. 

MI - Muskegon - Muskegon Lake 

AL - Mobile - Cold Creek 

AL /GA- State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Rusaellville -Mud R. 

KY - Catlettsburg - Big Sandy R. 

TN - Nickajack Resemir 

VA - Brookneal - Roanoke R. 

OR - Owyhee - Owyhee R. 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

NY - Fort Miller - Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanco Drain 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - Porter - Niagara R. Delta 

NY - Olcott - Eighteen Mile Creek 

NY - Lewiston - Niagara R. 

NY - Newtoa Falls - Oswegatchie R. 

NY - Dexter - Black River Delta 

NY - Massena - Raquette R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-22 
Table D-10 Alpha-BHC (coat) 

Episode Cont. (II&) Estimated Risk Speckr Locatbn 

3308 ND -- 

3310 ND -- 

3311 ND mm 

3313 ND __ 

3314 ND -_ 

3336 ND -- 

3346 ND -- 

3348 ND -- 

3350 ND -- 

3354 ND -- 

3355 ND -- 

3375 ND __ 

3376 ND __ 

3401 ND mm 

3403 ND -- 

34Q9+/2709 ND me 

3419 ND -- 

3421 ND -- 

3422 ND _- 

3427 ND -_ 

3428 ND -- 

3429 ND __ 

Northern Pike 

Walleye 

Sm Bass 

Sm Bass 

White Bass 

Spotted Seatrout 

Lm Bass 

White Perch 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Freshwater Drum 

White Perch 

Lm Bass 

Bluefish 

Bluefish 

Weakfish 

NY - Rouses Pt. - Richelieu R. 

PA - Easton -Lehigh R. 

WV - New Martinsville - Ohio R. 

WV - Bedington - Opequon Creek 

WV - Winfield - Kanawha R. 

GA - St. Marys - North R. {mouth) 

NC - Plymouth - Roanoke R. 

SC - Georgetown - Sampit R. 

TN - Calhoun - Hiwassee R. 

CA - Stockton -New Mormon Slough 

CA - Stockton - Old Mormon Slough 

GA - AusteU - Chattahoochee R. 

GA - Whitesburg - Chattahoochee R. 

TN - Hardin Co. - Tennessee R. 

TN - Kingsport - S. Fork Holston R. 

NY - Peek&ill - Hudson R. 

PA - Erie - Lake Erie 

VA - Covington - Jackson R. 

VA - Riwxdale - Blackwater R. 

NJ - Elizabeth - Newark Bay 

NJ -Newark - Passaic R. 

NJ - Salem - Delaware R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-23 
D-10-21 
Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Mirer 

(Consumption Rate 6.59Iday) 

EpLsodc Cone. (n&l Entfmated Risk Species Location 

2328 225 

2329 131 

3115 34.3 

3412 14.2 

3300 7.91 

3304 7.25 

3117 7.06 

3301 6.87 

3306 4.1 

3302 3.63 

318412133” 3.62 

3444 3.49 

3096 3.01 

3305 2.25 

3258 1.87 

3113 1.71 

3180 1.39 

3141 1.16 

3312 1.14 

3420 1.03 

3063 0.88 

3415 0.77 

3125 0.7 

3104*/2212 0.63 

3336 0.42 

3426 0.38 

3172 0.36 

3081 0.34 

3065 0.33 

3118 0.32 

3148 0.29 

3299 0.28 

3216 0.26 

3314 0.22 

3097 0.21 

3401 0.21 

3311 0.18 

2228 ND 

23% ND 

2410 ND 

3.8xlo-5 

2.2xlBS 

5.7x10& 

2.4~10‘~ 

1.3x1o-6 

1.2xlo-6 

1.2X106 

1.lXlO-6 

6.9x10-’ 

6. 1x1U7 

6.1x10-’ 

58x10-’ 

5.0X10” 

38x10-’ 

3.1x10-’ 

2.9xIo-7 

2.3x10-’ 

1.9x10-’ 

1.9x10“ 

1.7x10-’ 

1.5X10” 

1.3x10-’ 

1.2X10-’ 

1.1x10-’ 

7.0x10-* 

6.4x10-* 

6.0x10-* 

5.7x10-* 

5.5XlO-8 

53x10-* 

4.8x10-* 

4.7x10-* 

4.3x10-* 

3.7x10-* 

35x10-* 

3,5x10-* 

3.0x10-* 

Chinook Salmon NY - Olcott - Lake Ontario 

Brown Trout NY - Rochester - Lake Ontario 

Catfish IL - East St. Louis - Mississippi Riwx below Sauget 

Sm Bass NY - Oswego - Oswego Harbor 

Sm Bass NY - Porter - Niagara R. Delta 

Northern Pike NY -Dexter - Black River Delta 

Lake Trout IL - Waukegan - Lake Michigan 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Sm Bass NY - Massena - Grass R. 

Lm Bass NY - Lewiston - Niagara R. 

Blue Catfish MS - Redwood - Yazoo R. 

Channel Cattish TN - Memphis - Mississippi R. 

Brown Bullhead PA - Eddystone -Delaware R. 

Sm Bass NY - Massena - Raquette R. 

spot VA - Nortolk - S. Br. Elizabeth R. 

Carp IL - Geneva - Fox R. 

Lm Bass GA - Early County - Spring Creek 

Northern Pike WI - Milwaukee - Milwaukee R. 

Sm Bass WV - Wheeling - Ohio R. 

Green Sunfish PA - Spring Grove - Codorus Creek 

Spotted Seatrout LA - Moss Lake - Calcasieu R. 

Channel Catfish PA - Ransom - N. Br. Susquehanna R. 

White Bass MN - Red Wing - Mississippi R. 

Lm Bass PA - Philadelphia - Schuylkill R. 

Spotted Seatrout GA - St. Marys - North R. (mouth) 

Bluefish NJ - Carteret - Arthur Kill R. 

Lm Bass AL /GA- State Line - Coosa R. 

White Bass TX - Lufkin - Lake Sam Raybum 

Bigmouth Buffalo LA - Baton Rouge -Mississippi R. 

Waheye MI - Escanaba - Escanaba R. 

Walleye MI - Muskegon - Muskegon Lake 

Lm Bass NY - N. Tonawanda - Niagara R. 

Squawfish OR - St. Helens - Columbia R. 

White Bass WV - Winfield - Kanawha R. 

Brown Bullhead DE - Tybouts Comer - Red Lion Creek 

Lm Bass TN - Hardin Co. - Tennessee R. 

Sm Bass WV - New Martinstille - Ohio R. 

Longear Sunfish VA - Carterstille - James R. 

Lm Bass ME - Lewiston - Androscoggin R. 

Sm Bass MI -River Rouge -Rouge R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-25 
Table D-10 MLrer (cant) 

Episode Cone (n&I Enthated Risk Specita Locatba 

3036/2190+ ND 

3046l2199’ ND 

3048 ND 

3066 ND 

3068 ND 

3069 ND 

3070 ND 

3079 ND 

3080 ND 

3083 ND 

3085 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

3094 ND 

3100 ND 

3101 ND 

3105 ND 

3106+/26os ND 

3108 ND 

3110 ND 

3112 ND 

3114 ND 

3120 ND 

3146 ND 

3168 ND 

3182 ND 

3183 ND 

3188 ND 

3193 ND 

3212 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3259 ND 

3266 ND 

3267 ND 

3282 ND 

3288 ND 

3290 ND 

-_ 

-_ 

-- 

.- 

*- 

ma 

__ 

-_ 

-_ 

__ 

.- 

_- 

-a 

-- 

-w 

__ 

__ 

__ 

-- 

-_ 

-- 

_- 

mm 

__ 

_- 

__ 

-- 

-- 

-- 

-- 

me 

-- 

-- 

__ 

-- 

-- 

-- 

-- 

mm 

__ 

__ 

-- 

__ 

-- 

Bluegill 

Lm Bass 

White Bass 

Freshwater Drum 

Atl. Croaker 

Trout 

Sheepshead 

White Bass 

Lm Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

Lm Bass 

Channel Catfish 

White Perch 

Brown Trout 

Lm Bass 

Walleye 

Walleye 

Carp 

Walleye 

Carp 

Bass 

Walleye 

Lm Bass 

Rock Bass 

Sauger 

Lm Bass 

Sm Bass 

Catfish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Catfish 

SquawfIsh 

Redear Sunfish 

IA - Hamburg - Nishnabotna R. 

MO - Lexington - Missouri R. 

MO - West Alron - Mississippi R. 

LA = Union - Mississippi R. 

TX - Morgan Point - Houston Ship Channel 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

OK - Kaw Resenoir 

LA - Monroe - Ouachita R. 

LA - Oak Ridge - Bayou Bonne Idee 

TX - Freeport - Brazes R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Reserwir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Torresdale - Delaware R. 

MD - Baltimore - Baltimore Harbor 

PA - Paoli - Little Valley Creek 

OK -Fort Cobb -Fort Cobb Reservoir 

WI - l-J. Pentenwell Flow - Wisconsin R. 

WI -Merrill - Wisconsin R. 

WI -Hudson - St. CroixR. 

MN - Little Falls -Mississippi R. 

IL - Quincy - Mississippi R. 

MI - Saugatuck - Kalamazoo R. 

WI - Rothschild -Wisconsin R. 

AL - Mobile - Cold Creek 

KY - Russellville - Mud R. 

KY - Catlettsburg - Big Sandy R. 

TN - Nickajack Remir 

VA - Brookneal - Roanoke R. 

OR - Owyhee - Owyhee R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

NY - Fort Miller -Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanco Drain 

CA - Stockton - Port of Stockton 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-26 
Table D-10 Mlnr (cant) 

Episode Cone (o&@ Eatimattd Risk Specks Location 

3298 ND 

3303 ND 

3308 ND 

3310 ND 

3313 ND 

3346 ND 

3348 ND 

3350 ND 

3354 ND 

3355 ND 

3375 ND 

3376 ND 

3377 ND 

3403 ND 

3409+/2709 ND 

3414 ND 

3419 ND 

3421 ND 

3422 ND 

3427 ND 

342% ND 

3429 ND 

-- 

__ 

mm 

__ 

..- 

Lm Bass NY - Buffalo - Buffalo R. 

Sm Bass NY - Newton Falls - Oswegatchie R. 

Northern Pike NY - Rouses Pt. - Richelieu R. 

Walleye PA - Easton - Lehigh R. 

Sm Bass WV - Bedington - Opequon Creek 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon SIough 

Lm Bass GA - Austell- Chattahoochee R. 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA - Franklin - Chattahoochee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill -Hudson R. 

Channel Catfish/Sm Bass PA - Pittston - Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - RiwrdaIe - Blackwater R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-JO-27 
D-JO-28 
Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Gamma-BHC 

(Consumption Rate 6.5 dday) 

Epiaodt Cone (a&) Estimattd Risk Spttits Locatba 

3068 6.68 

3100 2.85 

3258 2.67 

3113 1.78 

3114 1.71 

3094 1.68 

3184/2133+ 1.64 

3079 1.59 

3377 1.56 

3104/2212+ 1.36 

2328 1.33 

3110 1.08 

3314 0.97 

2410 0.86 

3048 0.8 

3375 0.71 

3125 0.61 

3120 0.43 

3401 0.39 

3426 0.37 

3182 0.33 

3346 0.16 

2228 ND 

2329 ND 

2356 ND 

3036/2190* ND 

3046/2199* ND 

3063 ND 

3065 ND 

3066 ND 

3w9 ND 

3070 ND 

3080 ND 

3081 ND 

3083 ND 

3085 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

8.1x10-’ 

3.4x16’ 

3.2x10-’ 

22x10-’ 

2.1x10-’ 

2.0x10-’ 

2.0x10-’ 

19x10-’ 

19x10-’ 

1.6x10-’ 

1.6x10-’ 

1.3x10-’ 

1.2x10-’ 

I .0x10-’ 

9.7xlo-8 

8.6x10-* 

7.4x10-* 

5.8x10-* 

4.7x10-* 

4.5x10-* 

4.0x10-* 

1.9x10-* 

__ 

-- 

_- 

__ 

-- 

__ 

_- 

-- 

__ 

__ 

__ 

-- 

__ 

*_ 

__ 

__ 

me 

__ 

Atl. Croaker 

White Perch 

spot 

Channel Catfish/Carp 

Carp 

Channel Catfish 

Blue Catfish 

White Bass 

Lm Bass 

Sm Bass 

Chinook Salmon 

Carp 

White Bass 

Sm Bass 

White Bass 

Lm Bass 

White Bass 

Bass 

Lm Bass 

Bluefish 

Rock Bass 

Lm Bass 

Longear Sunfish 

Brown Trout 

Lm Bass 

Bluegill 

Lm Bass 

Spotted Seatrout 

Bigmouth Buffalo 

Freshwater Drum 

Trout 

Sheepshead 

Lm Bass 

White Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

TX - Morgan Point - Houston Ship Channel 

MD - Baltimore - Baltimore Harbor 

VA - Norfolk - S. Br. Elizabeth R. 

IL - Geneva - Fox R. 

IL - Quincy - Mississippi R. 

PA - Torresdale - Delaware R. 

MS - Redwood - Yazoo R. 

OK - Kaw Reservoir 

GA - Franklin - Chattahoochee R. 

PA - Philadelphia - Schuylkill R. 

NY - Olcott - Lake Ontario 

WI -Hudson - St. CroixR. 

WV - Wintield - Kanawha R. 

MI - Riwr Rouge - Rouge R. 

MO - West Alton - Mississippi R. 

GA - Austell - Chattahoochee R. 

MN - Red Wing - Mississippi R. 

MI - Saugatuck - Kalamazoo R. 

TN - Hardin Co. - Tennessee R. 

NJ - Carteret - Arthur Kill R. 

KY - Russellville - Mud R. 

NC - Plymouth - Roanoke R. 

VA - Carterstille - James R. 

NY - Rochester - Lake Ontario 

ME - Lewiston - Androscoggin R. 

IA - Hamburg - Nisbnabotna R. 

MO - Lexington - Missouri R. 

LA - Moss Lake - Calcasieu R. 

LA -Baton Rouge -Mississippi R. 

LA - Union -Mississippi R. 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

LA -Monroe - Ouachita R. 

TX - Lufkin - Lake Sam Raybum 

LA - Oak Ridge - Bayou Bonne Idee 

TX - Freeport - Brazos R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Resemir 

LA - Hodge - Dugdemona R. 

c Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-JO-29 
Table D-10 Gamma-BHC (coat) 

Episode Cont. @g/g) Eatinattd Rlrk Speckr Locatbn 

3093 ND 

30% ND 

3097 ND 

3101 ND 

3105 ND 

3 106*/2608 ND 

3108 ND 

3112 ND 

3115 ND 

3117 ND 

3118 ND 

3141 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3183 ND 

3188 ND 

3193 ND 

3212 ND 

3216 ND 

3218 ND 

3219 ND 

323 1 ND 

3249 ND 

3252 ND 

3259 ND 

3266 ND 

3267 ND 

3282 ND 

3288 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3310 ND 

_- 

__ 

__ 

-- 

__ 

_- 

-- 

__ 

-- 

-- 

_- 

-- 

__ 

__ 

__ 

-- 

-- 

-- 

-- 

__ 

-- 

-- 

-- 

__ 

-- 

-- 

__ 

__ 

__ 

-- 

__ 

__ 

_- 

__ 

__ 

__ 

-- 

_- 

-- 

-_ 

-- 

__ 

-- 

__ 

Lm Bass 

Brown Bullhead 

Brown Bullhead 

Brown Trout 

Lm Bass 

Walleye 

Walleye 

Walleye 

Catfish 

Lake Trout 

Walleye 

Northern Pike 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Sauger 

Lm Bass 

Sm Bass 

Catfish 

Squawfish 

Squaw-t% 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Cattish 

Squawtish 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Walleye 

TX - DiboU - Neches R. 

PA - Eddystone - Delaware R. 

DE - Tybouts Comer - Red Lion Creek 

PA - Paoli -Little Valley Creek 

OK - Fort Cobb - Fort Cobb Reserwir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

MN - Little Falls - Mississippi R. 

IL - East St. Louis - Mississippi Riwx below Sauget 

IL - Waukegan - Lake Michigan 

MI - Escanaba - Escanaba R. 

WI - Milwaukee - Milwaukee R. 

WI - Rothschild - Wisconsin R. 

MI - Muskegon - Muskegon Lake 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Catlettsburg - Big Sandy R. 

TN - Nickajack Reservoir 

VA - Brookneal - Roanoke R. 

OR - Owyhee - Owyhee R. 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R. 

OR - DalIes - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

NY - Fort Miller - Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanco Dram 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter - Niagara R. Delta 

NY - Olcott - Eighteen Mile Creek 

NY - Lewiston - Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black Riwx Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

PA - Easton -Lehigh R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-30 
Table D-10 Gamma-BHC (coat) 

Episode Coat. (q/g) Estimated Risk Species Location 

3311 ND -- 

3312 ND -- 

3313 ND -- 

3336 ND -_ 

3348 ND -- 

3350 ND -- 

3354 ND __ 

3355 ND -- 

3376 ND -- 

3403 ND -_ 

3409+R7# ND -_ 

3412 ND -_ 

3414 ND _- 

3415 ND -- 

3419 ND -- 

3420 ND -- 

3421 ND -- 

3422 ND -- 

3421 ND -- 

3428 ND -_ 

3429 ND -- 

3444 ND -- 

Sm Bass WV - New MartinswIle - Ohio R. 

Sm Bass WV - Wheeling - Ohio R. 

Sm Bass WV - Bedington - Opequon Creek 

Spotted Seatrout GA - St. Marys -North R. (mouth) 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peek&ill - Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel CattisNSm Bass PA - Pittston - Susquehanna R. 

Channel Catfish&m Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grow - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Riwxdale - Blackwater R. 

Bluefish NJ -Elizabeth -Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

Channel Catfish&m Bass TN -Memphis -Mississippi R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations 

Species listed is for the sample used. 

D-10-31 

Table D-10 (cant) 

Estimated Risks from Ingestion of Fish Contaminated with Heracblorobenzene 

(Consumption Rate 6.5 g/day) 

Epbode Cone (II&) Estimated Rlrk Specks Location 

3085 50.74 

3063 43.49 

2329 8.87 

2328 8.19 

3068 7.66 

3444 5.8 

3094 5.38 

3117 5.22 

3299 3.03 

3100 2.74 

3097 2.57 

3066 2.41 

2410 2.38 

3212 2.24 

3079 2. I 

3282 2.02 

3314 1.94 

3113 1.72 

3301 1.2 

3311 1.18 

3375 0.9 

3168 0.89 

3310 0.8 

3114 0.75 

3412 0.58 

3300 0.54 

3288 0.51 

3193 0.32 

3101 0.31 

3065 0.3 

3302 0.3 

3183 0.28 

3118 0.24 

3120 0.15 

3401 0.14 

3081 0.12 

2228 ND 

23% ND 

3036/2 190+ ND 

3046/2199+ ND 

8.0X10" 

4.9x10a 

1.4x10a 

1.3xlO‘(j 

1.2x1o-6 

9.2x10“ 

8.5~10.’ 

82x10-’ 

48x10-’ 

4.3x10-’ 

4.1x10-’ 

3.8x10-’ 

3.8x10-’ 

3.5x10-’ 

3.3x10-’ 

3.2x10-’ 

3.1x10-’ 

2.7x10-’ 

19X10-’ 

1.9i10-’ 

1.4x10” 

1.4x10-’ 

1.3x10-’ 

1.2X10-’ 

9.2x1o-8 

8.5~10-~ 

8.1x10-s 

5. lxlo-g 

4.9x1o-8 

4.7x1o-8 

4.7x10-* 

4.4x10‘s 

3.8x1o-8 

2.4~16~ 

22x10-* 

1.9x10-* 

-_ 

__ 

_- 

-_ 

Black Drum TX - Freeport - Brazes R. 

Spotted Seatrout LA - Moss Lake - Calcasieu R. 

Brown Trout NY - Rochester - Lake Ontario 

Chinook Salmon NY - Olcott - Lake Ontario 

A tl. Croaker TX - Morgan Point - Houston Ship Channel 

Channel Cattish/Lm Bass TN - Memphis - Mississippi R. 

Channel Catfish PA - Torresdale - Delaware R. 

Lake Trout IL - Waukegan - Lake Michigan 

Lm Bass NY - N. Tonawanda - Niagara R. 

White Perch MD - Baltimore - Baltimore Harbor 

Brown Bullhead DE - Tybouts Comer - Red Lion Creek 

Freshwater Drum LA - Union - Mississippi R. 

Sm Bass MI - Riwr Rouge - Rouge R. 

Catfish OR - Owyhee - Owyhee R. 

White Bass OK - Kaw Reserwiir 

Flathead Catfish CA - Calipatria -Alamo R. 

White Bass WV - Wintield - Kanawha R. 

Channel Catfish/Carp IL - Geneva - Fox R. 

Northern Pike NY - Olcott - Eighteen Mile Creek 

Sm Bass WV - New Martinstille - Ohio R. 

Lm Bass GA - Austell - Chattahoochee R. 

Lm Bass AL - Mobile - Cold Creek 

Walleye PA - E aston - Lehigh R 

Carp IL - Quincy - Mississippi R. 

Sm Bass NY - Oswego - Oswego Harbor 

Sm Bass NY - Porter - Niagara R. Delta 

Squaw&h CA - Salinas - Blanco Drain 

Sm Bass VA - Brookneal - Roanoke R. 

Brown Trout PA - Paoli - Little Valley Creek 

Bigmouth Buffalo LA - Baton Rouge - Mississippi R. 

Lm Bass NY - Lewiston - Niagara R. 

Sauger KY - Catlettsburg - Big Sandy R. 

Walleye MI - Escanaba - Escanaba R. 

Bass MI - Saugatuck - Kalamazoo R. 

Lm Bass TN - Hardin Co. - Tennessee R. 

White Bass TX - Lufkin - Lake Sam Raybum 

L ongear Sunfish VA - Cartersville - James R. 

Lm Bass ME - Lewiston - Androscoggin R. 

Bluegill IA - Hamburg - Nishnabotna R. 

Lm Bass MO - Lexington - Missouri R. 

l Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-33 
Table D-10 Hexachlorobenzeae(coat) 

Episode Cone (a&g) Estimated Risk Specks Locatba 

3048 ND 

3069 ND 

3070 ND 

3080 ND 

3083 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

30% ND 

3104+/2212 ND 

3105 ND 

3 106v2608 ND 

3108 ND 

3110 ND 

3112 ND 

3115 ND 

3125 ND 

3141 ND 

3146 ND 

3148 ND 

3172 ND 

3183 ND 

3182 ND 

3184/2133+ ND 

3188 ND 

3216 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3258 ND 

3259 ND 

3266 ND 

3267 ND 

3290 ND 

3298 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

me 

-- 

-- 

_- 

-_ 

-- 

-_ 

-- 

-- 

_- 

-- 

-- 

-- 

-_ 

-- 

-- 

-- 

-- 

_- 

-- 

-- 

-- 

_- 

-- 

_- 

_- 

-- 

-_ 

-- 

-- 

-- 

-- 

_- 

-- 

-- 

_- 

_- 

-_ 

-- 

-_ 

-- 

__ 

-_ 

White Bass MO - West Alton - Mississippi R. 

Trout TX - Corpus Christi - Inner Harbor 

Sheepshead TX - Port Arthur - Neches R. (tidal) 

Lm Bass LA - Monroe - Ouachita R. 

Lm Bass LA - Oak Ridge - Bayou Bonne Idee 

Bluegill LA - Deridder - Anacoco Bayou 

White Crappie OK - Muskogee - Webbers Falls 

White Crappie OK - Pyrer Creek - Fort Gibson Reserwir 

Warmouth LA -Hedge - Dugdemona R. 

Lm Bass TX - Diboll - Neches R. 

Brown Bullhead PA - Eddystone - Delaware R. 

Lm Bass&m Bass PA - Philadelphia - Schuylkill R. 

Lm Bass OK - Fort Cobb - Fort Cobb Reservoir 

Walleye WI - U. Pentenwell Flow - Wisconsin R. 

Walleye WI - Merrill - Wisconsin R. 

Carp WI -Hudson - St. CroixR. 

Walleye MN - Little Falls - Mississippi R. 

Catfish IL - East St. Louis - Mississippi R&r below Sauget 

White Bass MN - Red Wing - Mississippi R. 

Northern Pike WI - Milwaukee - Milwaukee R. 

Walleye WI - Rothschild - Wisconsin. R. 

Walleye MI - Muskegon - Muskegon Lake 

Lm Bass AL/GA-- State Line - Coosa R. 

Lm Bass GA - Early County - Spring Creek 

Rock Bass KY - Russellville - Mud R. 

Blue Catfish/W. Crappie MS-Redwood - Yazoo R. 

Lm Bass TN - Nickajack Reservoir 

Squawfish OR - St, Helens - Columbia R. 

Squawfish OR - Wauna - Columbia R. 

White Sturgeon OR - Dailes - Columbia R. 

Sm Bass WA - Richland - Yakima R. 

Brook Trout ID - Coeur d’Alene - Coeur d*Alene R. 

Lm Bass ID - Parma - Boise R. 

spot VA - Norfolk - S. Br. Elizabeth R. 

Lm Bass NY - Fort Miller - Hudson R. 

Black Crappie AZ - Gila Bend - Gila R. 

Rainbow Trout CA - Anderson - Sacramento R. 

Redear Sunfish CA - Stockton - Port of Stockton 

Lm Bass NY - Buffalo - Buffalo R. 

Sm Bass NY - Newton Falls - Oswegatchie R. 

Northern Pike NY - Dexter - Black R&r Delta 

Sm Bass NY - Massena - Raquette R. 

Sm Bass NY - Massena - Grass R. 

Northern Pike NY - Rouses Pt. - Richelieu R. 

* Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-34 
Table D-10 Hesacbbrobenzem(cont) 

Episode Cone. (a&$ Estimated Risk Specks Lmat bn 

3312 ND __ 

3313 ND -- 

3336 ND __ 

3346 ND __ 

3348 ND -- 

3350 ND __ 

3354 ND -- 

3355 ND __ 

3376 ND -- 

3377 ND __ 

3403 ND -- 

3409+/2709 ND __ 

3414 ND __ 

3415 ND __ 

3419 ND __ 

3420 ND __ 

3421 ND __ 

3422 ND -_ 

3426 ND -- 

3427 ND _- 

3428 ND __ 

3429 ND __ 

Sm Bass WV -Wheeling -Ohio R. 

Sm Bass WV - Bedington - Opequon Creek 

Spotted Seatrout GA - St. Marys - North R. (mouth) 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA - Franklin - Chattahoochee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill - Hudson R. 

Channel Catfish&m Bass PA - Pittston - Susquehanna R. 

Channel Catfish/Sm Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grove - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Riwxdale - Blackwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

l Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-35 
D-IO-36 
Table D-10 (cant) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Trifluralin 

(Consumption Rate 6.5 g/day) 

Epbode Coat (ng/gl Estlmatcd Risk Species Locatba 

3282 116 

3212 64.8 

3115 33.1 

3114 20 

3444 13.4 

3048 1.64 

2228 ND 

2328 ND 

2329 ND 

2356 ND 

2410 ND 

3036/2 190* ND 

304#2199* ND 

3063 ND 

3065 ND 

3066 ND 

3068 ND 

3069 ND 

3070 ND 

3079 ND 

3080 ND 

3081 ND 

3083 ND 

3085 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

3094 ND 

30% ND 

3097 ND 

3100 ND 

3101 ND 

3104/2212* ND 

3105 ND 

3106*/2608 ND 

3108 ND 

3110 ND 

3112 ND 

8.3~10-~ 

4.6~10’~ 

2.4x10-’ 

1.4xlo-8 

9.6x10-’ 

1.2x1o-g 

-_ 

-- 

_- 

__ 

-_ 

_- 

_- 

-- 

-- 

-- 

-_ 

-- 

-- 

-- 

-- 

me 

-- 

mm 

-- 

w- 

-- 

-- 

_- 

-- 

-- 

_- 

_- 

__ 

-- 

-_ 

-_ 

_- 

-- 

-_ 

FIathead Catfish 

Cattish 

Catfish 

Carp 

Channel Catfish 

White Bass 

Longear Sunfish 

Chinook Salmon 

Brown Trout 

Lm Bass 

Sm Bass 

Bluegill 

Lm Bass 

Spotted Scatrout 

Bigmouth Buffalo 

Freshwater Drum 

A tl. Croaker 

Trout 

Sheepshead 

White Bass 

Lm Bass 

White Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

White Crappie 

Warmoutb 

Lm Bass 

Channel Catfish 

Brown Bullhead 

Brown Bullhead 

White Perch 

Brown Trout 

Sm Bass/‘Lm Bass 

Lm Bass 

Walleye 

Walleye 

Carp 

Walleye 

CA - Calipatria - Alamo R. 

OR - Owyhee - Owyhee R. 

IL - East St. Louis - Mississippi Riwzr below Sauget 

IL - Quincy - Mississippi R. 

TN - Memphis - Mississippi R. 

MO - West Alton - Mississippi R. 

VA - Carterswlle - James R. 

NY - Olcott - Lake Ontario 

NY - Rochester - Lake Ontario 

ME - Lewiston - Androscoggin R. 

MI - Riwzr Rouge -Rouge R. 

IA - Hamburg - Nishnabotna R. 

MO - Lexington - Missouri R. 

LA -Moss Lake - Calcasieu R. 

LA - Baton Rouge -Mississippi R. 

LA - Union - Mississippi R. 

TX - Morgan Point -Houston Ship Channel 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

OK - Kaw Resermir 

LA - Monroe - Ouachita R. 

TX - Lu&in - Lake Sam Raybum 

LA - Oak Ridge - Bayou Bonne Idee 

TX - Freeport - Brazes R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Reservoir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Torresdale - Delaware R. 

PA - Eddystone - Delaware R. 

DE - Tybouts Comer - Red Lion Creek 

MD - Baltimore - Baltimore Harbor 

PA - Paoli - Linle Valley Creek 

PA - Philadelphia - Schuylkill R. 

OK - Fort Cobb - Fort Cobb Resermir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

WI - Hudson - St. CroixR. 

MN - Little Falls - Mississippi R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-37 
Table D-10 Tr!Nnlin(cont) 

EplSOdt Cont. (a@& Eutimated Rlak Specks Location 

3113 ND 

3117 ND 

3118 ND 

3120 ND 

3125 ND 

3141 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

318412133* ND 

3188 ND 

3193 ND 

3216 ND 

3218 N-D 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3258 ND 

3253 ND 

3266 ND 

3267 ND 

3288 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3310 ND 

3311 ND 

3312 ND 

3313 ND 

3314 ND 

3336 ND 

-- 

-- 

ma 

__ 

-_ 

__ 

_- 

__ 

_- 

_- 

__ 

me 

mm 

-_ 

-- 

_- 

-_ 

-- 

-- 

_- 

-- 

_- 

-- 

-_ 

-- 

_- 

mm 

-- 

mm 

_- 

_- 

em 

-- 

-- 

-- 

-- 

-- 

__ 

_- 

-_ 

me 

_- 

__ 

-- 

Channel Catfish/Carp 

Lake Trout 

Walleye 

Bass 

White Bass 

Northern Pike 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sauger 

Blue Catfish/W. Crappie 

Lm Bass 

Sm Bass 

Squawtish 

Squaw-fish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

spot 

Lm Bass 

Black Crappie 

Rainbow Trout 

Squawflsh 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Walleye 

Sm Bass 

Sm Bass 

Sm Bass 

White Bass 

Spotted Seatrout 

IL - Geneva - Fox R. 

IL - Waukegan - Lake Michigan 

MI - Escanaba - Escanaba R. 

MI - Saugatuck - Kalamazoo R. 

MN - Red Wing - Mississippi R. 

WI - Milwaukee - Milwaukee R. 

WI - Rothschild - Wisconsin R. 

MI - Muskegon - Muskegon Lake 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Russellville - Mud R. 

KY - Catlettsburg - Big Sandy R. 

MS -Redwood - Yazco R. 

TN - Nickajack Reservoir 

VA - Brookneal - Roanoke R. 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

VA -Norfolk - S. Br. Elizabeth R. 

NY - Fort Miller -Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Salinas - Blanco Drain 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter - Niagara R. Delta 

NY - Olcott - Eighteen Mile Creek 

NY - Lewiston - Niagara R. 

NY -Newton Falls - Oswegatchie R. 

NY - Dexter - Black Rim Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

PA - Easton -Lehigh R. 

WV -New Martinsville - Ohio R. 

WV -Wheeling - Ohio R. 

WV - Bedington - Opequon Creek 

WV - Winfleld - Kanawha R. 

GA - St. Marys -North R. (mouth) 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-38 
Table D-10 Trlfhwalla(eont) 

Eplrode Cone (a&) Ehmated Rl#k Speckr Lncatlon 

3346 

3348 

3350 

3354 

3355 

3375 

3376 

3377 

3401 

3403 

3409+/2709 

3412 

3414 

3415 

3419 

3420 

342 1 

3422 

3426 

3427 

3428 

3429 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - AusteE - Chattahoochee R. 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA - Franklin - Chattahoochee R. 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill - Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel Catfish/Sm Bass PA - Pittston - Susquehanna R. 

Channel Cattish&n Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grow - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Rixrdale - BIackwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-M-39 
D-1040 
Table D-10 (cant) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Heptacblor 

(Consumption Rate 6.5 g/day) 

Eplrode Cont. @g/g) E4rmated Risk Specks LocatIon 

3310 

2228 

2328 

2329 

2356 

2410 

3036/2190+ 

3046/2 199+ 

3048 

3063 

3065 

3069 

3070 

3079 

3080 

3081 

3083 

3085 

3088 

3089 

3090 

3092 

3093 

3094 

3096 

3100 

3101 

3104/2212+ 

3105 

31@5+/2608 

3108 

3110 

3112 

3113 

3114 

3115 

3117 

0.28 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

ND 

Walleye PA - Easton -Lehigh R. 

Longear Sunfish VA - Cartersville -James R. 

Chinook Salmon NY - Olcott -Lake Ontario 

Brown Trout NY - Rochester - Lake Ontario 

Lm Bass ME - Lewiston - Androscoggin R. 

Sm Bass MI - Riwzr Rouge - Rouge R. 

Bluegill IA - Hamburg - Nishnabotna R. 

Lm Bass MO - Letigton - Missouri R. 

White Bass MO - West Alton - Mississippi R. 

Spotted Seatrout LA -Moss Lake - Calcasieu R. 

Bigmouth Buffalo LA - Baton Rouge - Mississippi R. 

Freshwater Drum LA - Union - Mississippi R. 

Atl. Croaker TX - Morgan Point - Houston Ship Channel 

Trout TX - Corpus Christi - Inner Harbor 

Sheepshead TX - Port Arthur - Neches R. (tidal) 

White Bass OK - Kaw Resermir 

Lm Bass LA - Monroe - Ouachita R. 

White Bass TX -L&kin - Lake Sam Raybum 

Lm Bass LA - Oak Ridge - 3ayou Bonne Idee 

Black Drum TX - Freeport - Brazes R. 

Bluegill LA - Deridder - Anacoco Bayou 

White Crappie OK - Muskogce - Webbers Falls 

White Crappie OK - Pyrer Creek - Fort Gibson Reserwir 

Warmouth LA - Hodge - Dugdemona R. 

Lm Bass TX - Diboll - Neches R. 

Channel Cattish PA - Torresdale - Delaware R. 

Brown Bullhead PA - Eddystone - Delaware R. 

Brown Bullhead DE - Tybouts Comer - Red Lion Creek 

White Perch MD - Baltimore - Baltimore Harbor 

Brown Trout PA - Paoli - Little Valley Creek 

Sm Bass/Lm Bass PA - Philadelphia - Schuylkiil R. 

Lm Bass OK - Fort Cobb - Fort Cobb Remir 

Walleye WI - U. Pentenwell Flow - Wisconsin R. 

Walleye WI - Merrill - Wisconsin R. 

Carp WI -Hudson - St. CroixR. 

Walleye MN - Little Falls - Mississippi R. 

Carp/Channel Catfish IL - Geneva - Fox R. 

Carp IL - Quincy - Mississippi R. 

Catfish IL - East St, Louis - Mississippi Riwr below Sauget 

Lake Trout IL - Waukegan - Lake Michigan 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations, 

Species listed is for the sample used. 

D-10-11 
Table D-10 Heptachlor (coat) 

Eplrodc Cone. (II&) Ehtlmated Risk Specks Location 

3118 ND 

3120 ND 

3125 ND 

3141 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

318412133+ ND 

3188 ND 

3212 ND 

3216 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3258 ND 

3259 ND 

3266 ND 

3207 ND 

3282 ND 

3288 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3311 ND 

3312 ND 

3313 ND 

3314 ND 

3315 ND 

3336 ND 

3346 ND 

-- 

_- 

-- 

__ 

__ 

-- 

-- 

__ 

_- 

-- 

-- 

-- 

-- 

__ 

-_ 

-- 

-- 

-- 

-- 

-- 

-- 

_- 

-- 

-- 

-- 

-- 

-- 

_- 

-- 

-_ 

-- 

__ 

-_ 

-- 

__ 

_- 

__ 

-- 

-- 

__ 

-- 

-- 

-v 

_- 

Walleye 

Bass 

White Bass 

Northern Pike 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sau ger 

Blue Catfish/W. Crappie 

Lm Bass 

Catfish 

Squawfish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

Spot 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Catfish 

Squawfish 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Sm Bass 

White Bass 

Lm Bass 

Spotted Seatrout 

Lm Bass 

MI - Escanaba - Escanaba R. 

MI - Saugatuck - Kalamazoo R. 

MN - Red Wing - Mississippi R. 

WI - Milwaukee - Milwaukee R. 

WI - Rothschild - Wisconsin R. 

MI - Muskegon - Muskegon Lake 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Russelltille - Mud R. 

KY - Catlettsburg - Big Sandy R. 

MS - Redwood - Yazoo R. 

TN - Nickajack Reser\roir 

OR - Owyhee - Owyhee R. 

OR - St Helens - CoIumbia R. 

OR - Wauna - Columbia R. 

OR - DalIes - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

VA - Norfolk - S. Br. Elizabeth R. 

NY - Fort Miller -Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanco Drain 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter - Niagara R. Delta 

NY - Olcott - Eighteen Mile Creek 

NY - Lewiston - Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black Riwx Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

WV - New Martinsville - Ohio R. 

WV -Wheeling - Ohio R. 

WV - Bedington - Opequon Creek 

WV - Winfield - Kanawha R. 

PA - Lebanon - Union Canal 

GA - St. Marys - North R. (mouth) 

NC - Plymouth - Roanoke R. 

I Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 
Table D-10 Heptmblor(cont) 

Episode Cone (II@ Eatlmated RJnk Spccbr L.ocatkn 

3348 ND -- 

3350 ND -_ 

3354 ND -- 

3355 ND -- 

3375 ND me 

3376 ND -_ 

3377 ND -- 

3401 ND -- 

3403 ND -- 

3409+f2709 ND -- 

3412 ND -- 

3414 ND me 

3415 ND _- 

3419 ND -- 

3420 ND -- 

3421 ND -- 

3422 ND _- 

3426 ND -- 

3427 ND -- 

3428 ND -- 

3429 ND -- 

3444 ND -- 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - Austell - Chattahoochee R. 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA - Franklin - Chattahoochee R. 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill - Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel Catfish&m 3ass PA - Pittston - Susquehanna R. 

Channel Catish/Sm Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grove - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Riwrdale - Blackwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

Channel Catfb&‘Lm Bass TN - Memphis - Mississippi R. 

* Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-43 

Table D-10 (cant) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Dicofol 

(Consumption Rate 6.5 g/day) 

Eplrode COIN. (ng@ Eatlmated Rink Specks Location 

3117 14.9 

3288 11.8 

3212 11.6 

3094 10.4 

3282 5.13 

2328 3.88 

3444 2.83 

2329 2.82 

3252 1.58 

3141 1.51 

3377 1.25 

3184/2133+ 0.79 

3375 0.78 

3083 0.76 

3080 0.7 

3046!2199+ 0.66 

3376 0.46 

2228 ND 

2356 ND 

2410 ND 

3036/2190* ND 

3048 ND 

3063 ND 

3065 ND 

3066 ND 

3068 ND 

3069 ND 

3070 ND 

3079 ND 

3081 ND 

3085 ND 

3086 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

30% ND 

3097 ND 

3100 ND 

6.1~10“ 

48x10-’ 

4.7x10-’ 

42x10-’ 

2.1x10-’ 

1.6x10-’ 

1.2x10-’ 

1.2x10-’ 

6.5x10-* 

6.2~10-~ 

5.1x1 o-8 

3.2x1o-8 

3.2x10-* 

3.1x10-* 

2.9x10-* 

2.7x10-s 

1 .9x1o-8 

_- 

Lake Trout 

Squawfish 

C atflsh 

Channel Catfish 

Flathead Cattish 

Chinook Salmon 

Channel Catfish 

Brown Trout 

Lm Bass 

Northern Pike 

Lm Bass 

Blue Catfish 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Longear Sunfish 

Lm Bass 

Sm Bass 

Bluegill 

White Bass 

Spotted Seatrout 

Bigmouth Buffalo 

Freshwater Drum 

Atl. Croaker 

Trout 

Sheepshead 

White Bass 

White Bass 

Black Drum 

Red Drum 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

Lm Bass 

Brown Bullhead 

Brown Bullhead 

White Perch 

IL - Waukegan - Lake Michigan 

CA - Salinas - Blanco Drain 

OR - Owyhee - Owyhee R. 

PA - Torresdale - Delaware R. 

CA - Calipatria -Alamo R. 

NY - Olcott - Lake Ontario 

TN - Memphis - Mississippi R. 

NY - Rochester - Lake Ontario 

ID - Parma - Boise R. 

WI - Milwaukee - Milwaukee R. 

GA - Franklin - Chattahoochee R. 

MS-Redwood - Yazoo R. 

GA - Austell - Chattahoochee R. 

LA - Oak Ridge - Bayou Bonne Idee 

LA - Monroe - Ouachita R. 

MO - Lexington - Missouri R. 

GA - Whitesburg - Chattahoochee R. 

VA - Cartersville - James R. 

ME - Lewiston - Androscoggin R. 

MI - Riwx Rouge - Rouge R. 

IA -Hamburg - Nishnabotna R. 

MO - West Alton - Mississippi R. 

LA -Moss Lake - Calcasieu R. 

LA - Baton Rouge - Mississippi R. 

LA - Union - Mississippi R. 

TX - Morgan Point - Houston Ship Channel 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

OK - Kaw Reserwir 

TX - Lutkin - Lake Sam Raybum 

TX - Freeport - Brazos R. 

LA - Sulfur - Bayou D Tnde 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Reserwir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Eddystone - Delaware R. 

DE - Tybouts Comer - Red Lion Creek 

MD - Baltimore - Baltimore Harbor 

* Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-15 
Table D-10 Dkmfol (coat) 

Eplrode Cone (I&) Estimated Risk Speckr Lm8tloa 

3101 ND 

3104/2212+ ND 

3105 ND 

3106*/2608 ND 

3108 ND 

3110 ND 

3112 ND 

3113 ND 

3114 ND 

311s ND 

3118 ND 

3120 ND 

3125 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

3188 ND 

3193 ND 

3216 ND 

3218 ND 

3219 ND 

323 1 ND 

3249 ND 

3258 ND 

3259 ND 

3266 ND 

3267 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3310 ND 

3311 ND 

3312 ND 

Brown Trout 

Sm Bass/Lm Bass 

Lm Bass 

Walleye 

Walleye 

Carp 

Walleye 

Carp/Channel Catfish 

Carp 

Catfish 

Walleye 

Bass 

White Bass 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sauger 

Lm Bass 

Sm Bass 

Squawfish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

spot 

Lm Bass 

Black Crappie 

Rainbow Trout 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Walleye 

Sm Bass 

Sm Bass 

PA - Paoli - Little Valley Creek 

PA - Philadelphia - SchuyIkill R. 

OK - Fort Cobb - Fort Cobb Resenoir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

WI - Hudson - St. Croix R. 

MN - Little Falls - Mississippi R. 

IL - Geneva - Fox R. 

IL - Quincy - Mississippi R. 

IL - East St. Louis - Mississippi Riwr below Sauget 

MI - Escanaba - Escanaba R. 

MI - Saugatuck - Kalamazoo RI 

MN - Red Wing - Mississippi R. 

WI - Rothschild - Wisconsin R. 

MI - Muskegon - Muskegon Lake 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - RusselIville - Mud R. 

KY - Catlettsburg - Big Sandy R. 

TN - Nickajack Resemir 

VA - Brookneal - Roanoke R. 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d*Alene - Coeur d’Alene R. 

VA - Norfolk - S. Br. Elizabeth R. 

NY - Fort Miller - Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter -Niagara R. Delta 

NY - Lewiston - Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black R&r Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

PA - Easton - Lehigh R. 

WV -New Martinsville - Ohio R. 

WV -Wheeling - Ohio R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-46 
TabIe D-10 Dkofol (coat) 

Ephode Coat (a&) Estimated Rlrk Specks LocatIon 

3313 ND -_ 

3314 ND __ 

3336 ND _- 

3346 ND em 

3348 ND _- 

3350 ND -_ 

3354 ND _- 

335.5 ND -- 

3401 ND __ 

3403 ND __ 

34#+/2709 ND -- 

3412 ND -- 

3414 ND -- 

3415 ND __ 

3419 ND -_ 

3420 ND __ 

3421 ND -- 

3422 ND __ 

3426 ND __ 

3427 ND _- 

3428 ND __ 

3429 ND -- 

Sm Bass WV - Bedington - Opequon Creek 

White Bass WV - Winfield - Kanawha R. 

Spotted Seatrout GA - St. Marys - North R. (mouth) 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill - Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel Catfish&m Bass PA - Pittston - Susquehanna R. 

Channel Cattish/Sm Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA - Erie - Lake Erie 

Green Sunfish PA - Spring Grow - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - Riwxdale - Blackwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ -Newark - Passaic R. 

Weakfish NJ - Salem -Delaware R. 

+ Asterisk indicates epi&e number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

Table D-10 (cant) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Hexachlorobutadiene 

(Consumption Rate 6.5 g/day) 

Episode Coat (II%& Estimated Risk Speeles Location 

3063 88.31 

3115 10.5 

3085 3.53 

3068 0.81 

3081 0.27 

2228 ND 

2328 ND 

2329 ND 

2356 ND 

2410 ND 

3036/2 190+ ND 

3046/2199+ ND 

3048 ND 

3065 ND 

3066 ND 

3069 ND 

3070 ND 

3079 ND 

3080 ND 

3083 ND 

3088 ND 

3089 ND 

3090 ND 

3092 ND 

3093 ND 

3094 ND 

3095 ND 

3096 ND 

3097 ND 

3100 ND 

3101 ND 

3104/2212+ ND 

3105 ND 

3106+/2608 ND 

3108 ND 

3110 ND 

3112 ND 

3113 ND 

3114 ND 

3117 ND 

6.4~10” 

7.6~10’~ 

2.6~10.~ 

5.9x1o-g 

2.ox1o-9 

-- 

-- 

-- 

w- 

-_ 

me 

me 

_- 

-- 

-- 

-- 

-- 

-w 

_- 

_- 

-_ 

_- 

-- 

-- 

-- 

-- 

mm 

_- 

w- 

-_ 

mm 

mm 

me 

ma 

-- 

-- 

-- 

mm 

-- 

-w 

Spotted Seatrout 

Catfish 

Black Drum 

Atl. Croaker 

White Bass 

Longear Sunfish 

Chinook Salmon 

Brown Trout 

Lm Bass 

Sm Bass 

Bluegill 

Lm Bass 

White Bass 

Bigmouth Buffalo 

Freshwater Drum 

Trout 

Sheepshead 

White Bass 

Lm Bass 

Lm Bass 

Bluegill 

White Crappie 

White Crappie 

Warmouth 

Lm Bass 

Channel Cattish 

Brown Bullhead 

Brown Bullhead 

Brown Bullhead 

White Perch 

Brown Trout 

Sm Bass/Lm Bass 

Lm Bass 

Walleye 

Walleye 

Carp 

Walleye 

Carp/Channel Catfish 

Carp 

Lake Trout 

LA -Moss Lake - Calcasieu R. 

IL - East St. Louis - Mississippi R&r below Sauget 

TX - Freeport - Brazos R. 

TX - Morgan Point - Houston Ship Channel 

TX - Lufkin - Lake Sam Rayburn 

VA - Cartersville - James R. 

NY - Olcott - Lake Ontario 

NY - Rochester - Lake Ontario 

ME - Lewiston - Androscoggin R. 

MI - Riwr Rouge - Rouge R. 

IA - Hamburg - Nishnabotna R. 

MO - Lexington -Missouri R. 

MO - West Alton - Mississippi R. 

LA - Baton Rouge - Mississippi R. 

LA - Union -Mississippi R. 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

OK - Kaw Reservoir 

LA -Monroe - Ouachita R. 

LA - Oak Ridge - Bayou Bonne Idee 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

OK - Pyrer Creek - Fort Gibson Reservoir 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

PA - Torresdale - Delaware R. 

PA - Schuyllcill Jet. - Delaware R. 

PA - Eddystone - Delaware R. 

DE - Tybouts Corner - Red Lion Creek 

MD - Baltimore - Baltimore Harbor 

PA - Paoli - Little Valley Creek 

PA - Philadelphia - Schuylkill R. 

OK - Fort Cobb - Fort Cobb Reser\loir 

WI - U. Pentenwell Flow - Wisconsin R. 

WI - Merrill - Wisconsin R. 

WI - Hudson - St. Croix R. 

MN - Little Falls - Mississippi R. 

IL - Geneva - Fox R. 

IL - Quincy - Mississippi R. 

IL - Waukegan - Lake Michigan 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 
Table D-10 Hexachbrobutadkne (coat) 

Episode Coat (n&) Estimated Risk Speckr Locatbn 

3118 ND 

3120 ND 

3125 ND 

3141 ND 

3146 ND 

3148 ND 

3168 ND 

3172 ND 

3180 ND 

3182 ND 

3183 ND 

3184/2133+ ND 

3188 ND 

3 193 ND 

3212 ND 

3216 ND 

3218 ND 

3219 ND 

3231 ND 

3249 ND 

3252 ND 

3258 ND 

3259 ND 

32% ND 

3267 ND 

3282 ND 

3288 ND 

3290 ND 

3298 ND 

3299 ND 

3300 ND 

3301 ND 

3302 ND 

3303 ND 

3304 ND 

3305 ND 

3306 ND 

3308 ND 

3310 ND 

3311 ND 

3312 ND 

3313 ND 

3314 ND 

3336 ND 

-- 

-- 

-_ 

-- 

-- 

-_ 

-_ 

mm 

me 

-- 

-_ 

-- 

-0 

-- 

-_ 

-- 

-- 

-- 

-_ 

-- 

-- 

-- 

_- 

-_ 

-_ 

-- 

-- 

-- 

-_ 

-- 

__ 

mm 

_- 

me 

-- 

mm 

-- 

_- 

-- 

-- 

-a 

-- 

-- 

_- 

Walleye 

Bass 

White Bass 

Northern Pike 

Walleye 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sauger 

Blue Catfish/W. Crappie 

Lm Bass 

Sm Bass 

Catfish 

Squawfish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

spot 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Catfish 

Squawfish 

Redear Sunfish 

Lm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Walleye 

Sm Bass 

Sm Bass 

Sm Bass 

White Bass 

Spotted Seatrout 

MI - Escanaba - Escanaba R. 

MI - Saugatuck - Kalamazoo R. 

MN - Red Wing - Mississippi R. 

WI - Milwaukee - Milwaukee R. 

WI -Rothschild - Wisconsin R. 

MI - Muskegon -Muskegon Lake 

AL - Mobile - Cold Creek 

AL/GA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Russelltille - Mud R. 

KY - Catlettsburg - Big Sandy R. 

MS -Redwood - Yazoo R. 

TN - Nickajack Reservoir 

VA - Brookneal - Roanoke R. 

OR - Owyhee - Owyhee R. 

OR - St. Helens -Columbia R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d’Alene - Coeur d’Aleoe R. 

ID - Parma - Boise R. 

VA - Norfolk - 8 Br. Elizabeth R. 

NY - Fort Miller - Hudson R. 

Ai! - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanco Drain 

CA - Stockton - Port of Stockton 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter - Niagara R. Delta 

NY - Olcott - Eighteen Mile Creek 

NY - Lewiston -Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black Riwx Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

PA - Easton - Lehigh R. 

WV - New Martinsville -Ohio R. 

WV - Wheeling - Ohio R. 

WV - Bedington - Opequon Creek 

WV - Winfield - Kanawha R. 

GA - St. Marys - North R. (mouth) 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-50 
Table D-10 Heucbbrobutadkne (cant) 

Episode Cont. (n&J Estimated Risk Specks Location 

3346 ND __ 

3348 ND __ 

3350 ND -- 

3354 ND __ 

3355 ND _- 

3375 ND -- 

3376 ND -_ 

3377 ND _- 

3401 ND __ 

3403 ND _- 

3409+/2709 ND -- 

3412 ND -_ 

3414 ND -_ 

3415 ND -- 

3419 ND -- 

3420 ND _- 

3421 ND -- 

3422 ND __ 

3426 ND __ 

3427 ND -- 

3428 ND _- 

3429 ND _- 

3444 ND -- 

Lm Bass NC - Plymouth - Roanoke R. 

White Perch SC - Georgetown - Sampit R. 

Lm Bass TN - Calhoun - Hiwassee R. 

Lm Bass CA - Stockton - New Mormon Slough 

Lm Bass CA - Stockton - Old Mormon Slough 

Lm Bass GA - Austell - Chattahoochee R. 

Lm Bass GA - Whitesburg - Chattahoochee R. 

Lm Bass GA - Franklin - Chattahoochee R. 

Lm Bass TN - Hardin Co. - Tennessee R. 

Lm Bass TN - Kingsport - S. Fork Holston R. 

Lm Bass NY - Peekskill -Hudson R. 

Sm Bass NY - Oswego - Oswego Harbor 

Channel CatfishISm Bass PA - Pittston - Susquehanna R. 

Channel Catfish&m Bass PA - Ransom - N. Br. Susquehanna R. 

Freshwater Drum PA -Erie - Lake Erie 

Green Sunfish PA - Spring Grove - Codorus Creek 

White Perch VA - Covington - Jackson R. 

Lm Bass VA - RiErdale - Blackwater R. 

Bluefish NJ - Carteret - Arthur Kill R. 

Bluefish NJ - Elizabeth - Newark Bay 

Bluefish NJ - Newark - Passaic R. 

Weakfish NJ - Salem - Delaware R. 

Channel Catfish/Lm Bess TN - Memphis - Mississippi R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-lo-51 
D-JO-52 
Table D -10 (cant) 

Estimated Cancer Risks from Ingestion of Fish Contaminated with Peotachloroanisole 

(Consumption Rate 6.5 g/day) 

Eplsodt Coat. (IQ/& Estimated Rirk Specie8 l.oeatlon 

3444 48.6 7.2x1o-8 

3375 14.45 2. 1x1o-8 

3420 10.54 1.6x10-* 

3094 8.95 1.3x1o-8 

3141 7.79 1.2x10-* 

3113 5.7 8.5x10-’ 

3115 5.68 8.4~10‘~ 

3376 3.09 4.6~10.~ 

3414 2.99 4.4x1 o-g 

3146 2.93 4.4x1 o-g 

3415 2.53 3.8xlo-g 

3258 2.2 3.3xlo-g 

30% 2.15 3.2x1o-g 

3377 1.82 2.7~10” 

3184/2133* 1.7 2.5x10-’ 

3312 1.59 2.4~10-~ 

3090 1.33 2.ox1o-9 

3301 1.28 1 .9x1o-9 

3079 1.27 1.!9x10-g 

3114 1.27 l.9X1O-9 

3125 1.26 1.9x1o-9 

3310 1.08 1.6~10-~ 

3048 O.% 1.4x1o-g 

3193 0.91 1 .4x1o-9 

3 106+/2608 0.9 1.3x1o-p 

3066 0.87 1.3x1o‘g 

3100 0.8 1.2x1o-g 

3314 0.78 1.2x1o-9 

3422 0.77 1. 1x1o-g 

3068 0.73 l.1x1o’g 

2328 0.7 1 .O%lo-g 

3104/2212+ 0.59 8.8~10-‘~ 

3065 0.5 7.4x10-to 

3097 0.45 6.7x10-” 

3081 0.38 5.7x1BL0 

3311 0.37 5.5x10-m 

3403 0.36 5.3x1o-‘o 

3108 0.33 4.9x1o-‘o 

342 1 0.33 4.9x1o-1o 

3290 0.31 4.6~10-‘~ 

Channel Catfish/Lm Bass 

Lm Bass 

Green Sunfish 

Channel Catfish 

Northern Pike 

Channel Catfish/Carp 

Catfish 

Lm Bass 

Channel Catfish 

Walleye 

Channel Catfish 

spot 

Brown Bullhead 

Lm Bass 

Blue Catfish 

Sm Bass 

White Crappie 

Northern Pike 

White Bass 

Carp 

White Bass 

Walleye 

White Bass 

Sm Bass 

Walleye 

Freshwater Drum 

White Perch 

White Bass 

Lm Bass 

Atl. Croaker 

Chinook Salmon 

Sm Bass 

Bigmouth Buffalo 

Brown Bullhead 

White Bass 

Sm Bass 

Lm Bass 

Walleye 

White Perch 

Redear Sunfish 

TN -Memphis - Mississippi R. 

GA - Austell - Chattahoochee R. 

PA - Spring Grow - Codorus Creek 

PA - Torresdale - Delaware R. 

WI - Milwaukee - Milwaukee R. 

IL - Geneva - Fox R. 

IL - East St. Louis - Mississippi Riwx below Sauget 

GA - Whitesburg - Chattahoochee R. 

PA - Pittston - Susquehanna R. 

WI - Rothschild - Wisconsin R. 

PA - Ransom - N. Br. Susquehanna R. 

VA -Norfolk - S. Br. Elizabeth R. 

PA - Eddystone - Delaware R. 

GA - Franklin - Chattahoochee R. 

MS - Redwood - Yazoo R. 

WV - Wheeling - Ohio R. 

OK - Pyrer Creek - Fort Gibson Reserwnr 

NY - Olcott - Eighteen Mile Creek 

OK - Kaw Reservoir 

IL - Quincy - Mississippi R. 

MN - Red Wing - Mississippi R. 

PA - Easton - Lehigh R. 

MO - West Alton - Mississippi R. 

VA - Brookneal - Roanoke R. 

WI - U. Pentenwell Flow - Wisconsin R. 

LA - Union - Mississippi R. 

MD - Baltimore - Baltimore Harbor 

WV - Winfleld - Kanawha R. 

VA - Rivzrdale - Blackwater R. 

TX - Morgan Point - Houston Ship Channel 

NY - Olcott - Lake Ontario 

PA - Philadelphia - Schuylkill R. 

LA - Baton Rouge - Mississippi R. 

DE - Tybouts Corner -Red Lion Creek 

TX - Lufkin - Lake Sam Raybum 

WV - New Martinsville - Ohio R. 

TN - Kingsport - S. Fork HoIston R. 

WI - Merrill - Wisconsin R. 

VA - Covington - Jackson R. 

CA - Stockton - Port of Stockton 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-53 
Table D-10 Pentachloroan&ole(cont) 

Episode Cone. (a&) Estimated Risk Spech Locatloa 

3348 0.28 4.2x1o-‘o 

3101 0.27 4.0x10-‘” 

3118 0.19 2.8x10-‘” 

3426 0.16 2.4x10-” 

2228 ND -- 

2329 ND -- 

2356 ND -- 

2410 ND _- 

3036i2 190” ND -- 

3046/2 199” ND -- 

3063 ND -- 

3069 ND -- 

3070 ND -- 

3080 ND -- 

3083 ND _- 

3085 ND -- 

3088 ND -- 

3089 ND -- 

3092 ND -- 

3093 ND -- 

3105 ND -- 

3110 ND -- 

3112 ND -- 

3117 ND -- 

3120 ND _- 

3148 ND -- 

3168 ND -- 

3172 ND -- 

3180 ND -- 

3182 ND -- 

3183 ND -- 

3188 ND -- 

3212 ND -- 

3216 ND -- 

3218 ND -- 

3219 ND -- 

323 1 ND -_ 

3249 ND -_ 

3252 ND _- 

3259 ND -- 

3266 ND -- 

3267 ND -- 

3282 ND -- 

3288 ND -a 

White Perch 

Brown Trout 

Walleye 

Bluefish 

Longear Sunfish 

Brown Trout 

Lm Bass 

Sm Bass 

Bluegill 

Lm Bass 

Spotted Seatrout 

Trout 

Sheepshead 

Lm Bass 

Lm Bass 

Black Drum 

Bluegill 

White Crappie 

Warmouth 

Lm Bass 

Lm Bass 

Carp 

Walleye 

Lake Trout 

Bass 

Walleye 

Lm Bass 

Lm Bass 

Lm Bass 

Rock Bass 

Sauger 

Lm Bass 

Catfish 

Squaw-fish 

Squawfish 

White Sturgeon 

Sm Bass 

Brook Trout 

Lm Bass 

Lm Bass 

Black Crappie 

Rainbow Trout 

Flathead Catfish 

Squawftsh 

SC -Georgetown - Sampit R. 

PA - Paoli - Little Valley Creek 

MI - Escanaba - Escanaba R. 

NJ - Carteret - Arthur Kill R. 

VA - Cartersville - James R. 

NY - Rochester - Lake Ontario 

ME - Lewiston - Androscoggin R. 

MI - River Rouge - Rouge R. 

IA - Hamburg - Nishnabotna R. 

MO - Lexington - Missouri R. 

LA - Moss Lake - Calcasieu R. 

TX - Corpus Christi - Inner Harbor 

TX - Port Arthur - Neches R. (tidal) 

LA - Monroe - Ouachita R. 

LA - Oak Ridge - Bayou Bonne ldee 

TX - Freeport - Brazos R. 

LA - Deridder - Anacoco Bayou 

OK - Muskogee - Webbers Falls 

LA - Hodge - Dugdemona R. 

TX - Diboll - Neches R. 

OK -Fort Cobb - Fort Cobb Reservoir 

WI -Hudson - St. CroixR. 

MN - Little Falls - Mississippi R. 

IL - Waukegan - Lake Michigan 

MI - Saugatuck - Kalamazoo R. 

MI - Muskegon - Muskegon Lake 

AL -Mobile - Cold Creek 

ALIGA - State Line - Coosa R. 

GA - Early County - Spring Creek 

KY - Russellville -Mud R. 

KY - Catlettsburg - Big Sandy R. 

TN - Nickajack Reservoir 

OR - Owyhee - Owyhee R. 

OR - St. Helens - Columbia R. 

OR - Wauna - Columbia R. 

OR - Dalles - Columbia R. 

WA - Richland - Yakima R. 

ID - Coeur d*Alene - Coeur d’Alene R. 

ID - Parma - Boise R. 

NY - Fort Miller -Hudson R. 

AZ - Gila Bend - Gila R. 

CA - Anderson - Sacramento R. 

CA - Calipatria - Alamo R. 

CA - Salinas - Blanc0 Drain 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-10-54 
Table D-10 Pentacbbroanbolt(coat) 

Epbode Coat (ngf’g) Estimated Rhk species hcrtba 

3298 ND -- 

3299 ND -- 

3300 ND _- 

3302 ND -- 

3303 ND -- 

3304 ND _- 

3305 ND -- 

3305 ND -- 

3308 ND -_ 

3313 ND __ 

3336 ND -- 

3346 ND __ 

3350 ND -- 

3354 ND __ 

3355 ND _- 

3401 ND __ 

3409*/2709 ND -- 

3412 ND _- 

3419 ND __ 

3427 ND __ 

3428 ND __ 

3429 ND -- 

Lm Bass 

Lm Bass 

Sm Bass 

Lm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Sm Bass 

Northern Pike 

Sm Bass 

Spotted Seatrout 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Lm Bass 

Sm Bass 

Freshwater Drum 

Bluefish 

Bluefish 

Weakfish 

NY - Buffalo - Buffalo R. 

NY - N. Tonawanda - Niagara R. 

NY - Porter - Niagara R. Delta 

NY - Lewiston - Niagara R. 

NY - Newton Falls - Oswegatchie R. 

NY - Dexter - Black Riwx Delta 

NY - Massena - Raquette R. 

NY - Massena - Grass R. 

NY - Rouses Pt. - Richelieu R. 

WV - Bedington - Opequon Creek 

GA - St. Marys - North R. (mouth) 

NC - Plymouth - Roanoke R. 

TN - Calhoun - Hiwassee R. 

CA - Stockton - New Mormon Slough 

CA - Stockton - Old Mormon Slough 

TN - Hardin Co. - Tennessee R. 

NY - Peekskill - Hudson R. 

NY - Oswego - Oswego Harbor 

PA - Erie - Lake Erie 

NJ - Elizabeth - Newark Bay 

NJ - Newark - Passaic R. 

NJ - Salem - Delaware R. 

+ Asterisk indicates episode number associated with sample actually used for the risk calculations. 

Species listed is for the sample used. 

D-IO-SS 
D-10-56 
+bEPA 

United States 

Environmental Protection Agency 

(WH-551) 

Washington, DC 20460 

Official Business 

Penalty tor Private Use 

$300 

*1992* 

THEYEAROF