PB92147453 \1 I 1111 1\ 111111 I \II \ 1\111 11111\ NOAA Technical Memorandum NMFS-F/NEC-79 Contaminants in Sediment and Fish Tissue from Estuarine and Coastal Sites of the Northeastern United States: Data Summary for the Baseline Phase of the National Status and Trends Program Benthic Surveillance Project, 1984-1986 u.s. DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration National Marine Fisheries Service Northeast Fisheries Center Woods Hole, Massachusetts December 1990 REPRODUCED BY u.S. DEPARTMENT OF COMMERCE NATIONAL TECHNICAL INFORMATION SERVICE SPRINGFIELD, VA 22161
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PB92147453 \1 I 1111 1\ 111111 I \II \ 1\111 11111\
NOAA Technical Memorandum NMFS-F/NEC-79
Contaminants in
Sediment and Fish Tissue
from Estuarine and Coastal Sites
of the Northeastern United States:
Data Summary for the Baseline Phase of the
National Status and Trends Program
Benthic Surveillance Project, 1984-1986
u.s. DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration
National Marine Fisheries Service Northeast Fisheries Center
Woods Hole, Massachusetts
December 1990
REPRODUCED BY u.S. DEPARTMENT OF COMMERCE
NATIONAL TECHNICAL INFORMATION SERVICE SPRINGFIELD, VA 22161
Recent issues in this series
48. Indexed Bibliography of the Bay Scallop (Argopecten irradians). By Barbara D. Sabo (Gibson) and Edwin W. Rhodes. May 1987. iii + 85p. NTIS Access. No. PB87-231411/AS.
49. Northeast Fisheries Center Framework for Inshore Research. By Research Planning & Coordination Staff, Northeast Fisheries Center. July 1987. vi + 44p., 2 figs., 2 tables. NTIS Access. No. PB87-232286/AS.
50. Status of the Fishery Resources Off the Northeastern United States for 1987. By Conservation & Utilization Division, Northeast Fisheries Center. October 1987. iii + 132 p., 48 figs., 50 tables. NTIS Access. No. PB88-148549.
51. An Annotated List of the FIshes of Massachusetts Bay. By BruceB. Collette and Karsten E. Hartel. February 1988. x + 70 p., 1 fig., 1 table. NTIS Access. No. PB88-179247/AS.
52. An Evaluation of the Bottom Trawl Survey Program of the Northeast Fisheries Center. By Survey Working Group, Northeast Fisheries Center. March 1988. ix + 83 p., 33 figs., 13 tables. NTIS Access No. PB88-201983/AS.
53. Contaminants in Hudson-Raritan Estuary Water and Influence of Cold Storage upon Its Chemical Composition. By Anthony Calabrese, Lawrence 1. Buckley, and 1. Christopher Powell. May 1988. vii + 37 p., 10 figs., 11 tables. NTIS Access. No. PB88-225628/AS.
54. Epizootic Ulcerative Syndromes in CoastalfEstuarine Fish. By Carl 1. Sindennann. June 1988. v + 37 p., 8 figs., 1 table. NTIS Access. No. PB89-110803/AS.
55. A Plan for Study: Response of the Habitat and Biota of the Inner New York Bight to Abatement of Sewage Sludge Dumping. By Envirorunental Processes Division, Northeast Fisheries Center. June 1988. iii + 34 p., 5 figs., 3 tables, 4 app. NTIS Access. No. PB89-100903/AS.
56. Characterization of the Middle AtlanticWater Management Unit of the Northeast Regional Action Plan. By Anthony L. Pacheco, ed. July 1988. v + 322 p., 136 figs., 21 tables. NTIS Access. No. PB89-145262/AS.
57. An Analysis and Evaluation of Ichthyoplankton Survey Data from the Northeast Continental Shelf Ecosystem. By Wallace G. Smith, ed. August 1988. xiii + 132 p., 53 figs., 12 tables, 1 app. NTIS Access. No. PB89-122501/AS.
58. An Indexed Bibliography of Northeast Fisheries Center Publications and Reports for 1987. By Jon A. Gibson. August 1988. iii + 20 p. NTIS Access. No. PB89-113013/AS.
59. SUll"Veys of Breeding Penguins and Other Seabirds in the South Shetland Islands, Antarctica, J anuaryFebruary 1987. ByW. David Shuford and Larry B. Spear. September 1988. vii + 27 p., 14 figs., 1 table. NTIS Access. No. PB89-141311/AS.
60. Survey of Antarctic Fur Seals in the South Shetland Islands, Antarctica, during the 1986-1987 Austral Summer. By John L. Bengtson, Lisa M. Fenn, Tero 1. Harkonen, Everett G. Schaner, and Brent S. Stewart. September 1988. vii + 8 p., 1 fig., 3 tables. NTIS Access. No. PB89-141303/AS.
61. Fish as Sentinels of Environmental Health. By Robert A. Murchelano. September 1988. iii + 16 p., 4 figs. NTIS Access. No. PB89-139737/AS.
62. The Effects of Density Dependent Population Mechanisms on Assessment Advice for the Northwest Atlantic Mackerel Stock. By W. 1. Overholtz, SA Murawski, W.L. Michaels, and L.M. Dery. October 1988. v + 49 p., 7 figs.,
!"_ 20 tables. NTIS Access. No. PB89-151948/AS.
63. Status of the Fishery Resources Off the Northeastern United States for 1988. By Conservation and Utilization Division. October 1988. iii + 135 p", 51 figs., 52 tables. NTIS Access. No. PB89-130819/AS.
(continued on inside back cover)
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TABLE OF CONTENTS
Executive Summary .................................................................................................................................................... ix Introduction .................................................................................................................................................................. 1 Methods ........................................................................................................................................................................ 1 Data Presentation ......................................................................................................................................................... 1 Acknowledgements ...................................................................................................................................................... 2 References Cited .......................................................................................................................................................... 2 Site Summary Figures .................................................................................................................................................. 6 Analyte Summary Figures .......................................................................................................................................... 44 Analytical Data Tables ............................................................................................................................................... 72
LIST OF FIGURES
Figure 1. Sites sampled in the northeastern United States during 1984-86 as part of the National Status and Trends Program's Benthic Surveillance Project ........................................................ X
Figure 2a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Machias Bay ................................... 6
Figure 2b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Machias Bay .................................. 7
Figure 3a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Frenclunans Bay ............................ 8
Figure 3b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Frenclunans Bay ............................ 9
Figure 4a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Penobscot Bay .............................. 10
Figure 4b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Penobscot Bay ............................. 11
Figure 5a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Casco Bay ..................................... 12
Figure 5b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Casco Bay .................................... 13
Figure 6a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for the Merrimack River mouth area ................................................................................................................... 14
Figure 6b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs,liver pesticides, liver PCBs) for the Merrimack River mouth area ........................................................................................................ 15
Figure 7a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Salem Harbor ................................ 16
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Figure 7b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Salem Harbor ............................... 17
Figure 8a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Boston Harbor ............................... 18
Figure 8b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Boston Harbor ............................. 19
Figure 9a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PAHs, sediment texture, liver metals) for Quincy Bay .............................................................. 20
Figure 9b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Quincy Bay .................................. 21
Figure lOa. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Buzzards Bay .............................. 22
Figure lOb. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Buzzards Bay ............................. 23
Figure lla. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Narragansett Bay ......................... 24
Figure lIb. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Narragansett Bay ........................ 25
Figure 12a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for eastern Long Island Sound ................................................................................................................ 26
Figure 12b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for eastern Long Island Sound ..................................................................................................................... 27
Figure 13a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for western Long Island Sound .................................................................................................................... 28
Figure 13b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for western Long Island Sound .................................................................................................................... 29
Figure 14a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Raritan Bay ................................. 30
Figure 14b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Raritan Bay ................................ 31
Figure 15a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Great Bay r .................................... 32
Figure 15b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Great Bay ................................... 33
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Figure 16a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Delaware Bay .............................. 34
Figure 16b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Delaware Bay ............................ 35
Figure 17a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Upper Chesapeake Bay ............... 36
Figure 17b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Upper Chesapeake Bay .............. 37
Figure 18. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, sediment texture, sediment pesticides, sediment PCBs) for Baltimore Harbor ...................................... 38
Figure 19. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, sediment texture, sediment pesticides, sediment PCBs) for Mid Chesapeake Bay ................................ 39
Figure 20a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Lower Chesapeake Bay .............. 40
Figure 20b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Lower Chesapeake Bay ............. 41
Figure 21a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for the Elizabeth River ...................... 42
Figure 21b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for the Elizabeth River .................... 43
Figure 22a. Concentrations of hydrocarbons (naphthalene, 2-methylnaphthalene, l-methylnaphthalene, biphenyl, 2,6-dimethylnaphthalene, acenaphthene) in sediments from all sites .................................... 44
Figure 22b. Concentrations of hydrocarbons (fluorene, phenanthrene, anthracene, I-methylphenanthrene, fluoranthene, pyrene) in sediments from all sites .......................................................................... : ........ 45
Figure 22c. Concentrations of hydrocarbons (benzo[a]anthracene, chrysene, benzo[e]pyrene, benzo[a]pyrene, perylene, dibenzo[a,h]anthracene) in sediments from all sites .................................... 46
Figure 22d. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p' -DOE) in sediments from all sites .................................................................... 47
Figure 22e. Concentrations of hydrocarbOns (a-chlordane, trans-nonachlor, dieldrin, p,p'-DDE, o,p'-DDD, p,p' -DOD) in sediments from all sites ................................................................................................... 48
Figure 22f. Concentrations of hydrocarbons (o,p' -DDT, p,p' -DDT, mirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in sediments from all sites .................................................... 49
Figure 22g. Concentrations of hydrocarbons (pentachlorobiphenyls, hexachlorobiphenyls, heptachloro-biphenyls, octachlorobiphenyls, nonachlorobiphenyls) in sediments from all sites .............................. 50
Figure 23a. Concentrations of metals (silver, cadmium, chromium, copper, nickel, lead) in sediments from all sites ......... : ............................................................................................................ 51
Figure 23b. Concentrations of metals (zinc, thallium, manganese, arsenic, mercury ~ selenium) in sediments from all sites ...................................................................................................................... 52
Page vi
Figure 23c. Concentrations of metals (antimony, tin, silicon, iron, aluminum) in sediments from all sites ...................................................................................................................... 53
Figure 24. Concentrations of total organic carbon and silt-clay in sediments from all sites ..................................... 54
Figure 25a. Concentrations of hydrocarbons (naphthalene, 2-methylnaphthalene, I-methylnaphthalene, biphenyl, 2,6-dimethylnaphthalene, acenaphthene) in stomach contents collected from all sites .............................................................................................................. 55
Figure 25b. Concentrations of hydrocarbons (fluorene, phenanthrene, anthracene, I-methylphenanthrene, fluoranthene, pyrene) in stomach contents collected from all sites .................. 56
Figure 25c. Concentrations of hydrocarbons (benzo[a]anthracene, chrysene, benzo[e]pyrene, benzo[a]pyrene, perylene, dibenzo[a,h]anthracene) in stomach contents collected from all sites .............................................................................................................. 57
Figure 25d. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p'-DDE) in stomach contents collected from all sites ............................. 58
Figure 25e. Concentrations of hydrocarbons (a-chlordane, trans-nonachlor, dieldrin, p,p'-DDE, o,p' -DOD, p,p' -DOD) in stomach contents collected from all sites ...................................................... 59
Figure 25f. Concentrations of hydrocarbons (o,p' -DDT, p,p' -DDT, mirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in stomach contents collected from all sites ......................... 60
Figure 25g. Concentrations of hydrocarbons (pentachlorobiphenyls, hexachlorobiphenyls, heptachlorobiphenyls, octachlorobiphenyls, nonachlorobiphenyls) in stomach contents collected from all sites .............................................................................................................. 61
Figure 26a. Concentrations of metals (silver, cadmium, chromium, copper, nickel, lead) in stomach contents collected from all sites ............................................................................................... 62
Figure 26b. Concentrations of metals (zinc, iron, manganese, arsenic, mercury, selenium) in stomach contents collected from all sites ............................................................................................... 63
Figure 26c. Concentrations of metals (tin) in stomach contents collected from all sites ........................................... 64
Figure 27a. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p'-DDE) in livers collected from all sites ........................................................... 65
Figure 27b. Concentrations of hydrocarbons (a-chlordane, trans-nonachlor, dieldrin, p,p' -DOE, o,P' -DOD, p,p' -DOD) in livers collected from all sites ......................................................................... 66
Figure 27c. Concentrations of hydrocarbons (o,p' -DDT, p,p' -DDT, rnirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in livers collected from all sites ............................................ 67
Figure 27d. Concentrations of hydrocarbons (pentachlorobiphenyls, hexachlorobiphenyls, heptachlorobiphenyls, octachlorobiphenyls, nonachlorobiphenyls) in livers collected from all sites ............................................................................................................................ 68
Figure 28a. Concentrations of metals (silver, cadmium, chromium, copper, nickel, lead) in livers collected from all sites .................................................................................................................. 69
Figure 28b. Concentrations of metals (zinc, iron, manganese, arsenic, mercury, selenium) in livers collected from all sites .................................................................................................................. 70
Figure 28c. Concentrations of metals (tin) in livers collected from all sites .............................................................. 71
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LIST OF TABLES
Table 1. Northeast sampling locations and sample types collected from 1984 through 1986 ................................. 3
Table 2. Variables measured, sample matrices, and key to analyte codes used in Site Summary section ............... 5
Table 6e. Concentrations of hydrocarbons (pentachlorobiphenyl, hexachlorobiphenyl, heptachlorobiphenyl, octachlorobiphenyl, nonachlorobiphenyl) in stomach contents (ppb dry weight) ............................... 108
Table 7. Concentrations of metals in stomach contents (ppm dry weight) ......................................................... 109
Table 8a. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p' -DDE, a-chlordane, trans-nonachlor) in fish liver (ppb dry weight) .............. 110
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Table 8b. Concentrations of hydrocarbons (dieldrin, p,p' -DOE, o,p' -DOD, p,p' -DOD, o,p' -DDT, p,p'-DDT, mirex, dichlorobiphenyl) in fish liver (ppb dry weight) .................................................... 114
Table 8c. Concentrations of hydrocarbons (trichlorobiphenyl, tetrachlorobiphenyl, pentachlorobiphenyl, hexachlorobiphenyl,heptachlorobiphenyl,octachlorobiphenyl,nonachlorobiphenyl) in fish liver (ppb dry weight) ............................................................................................................ 117
Table 9a. Concentrations of metals (silver, cadmimn, chromimn, copper, nickel, lead, zinc, iron) in fish liver (ppm dry weight) ........................................................................................................... 121
Table 9b. Concentrations of metals (manganese, thallimn, arsenic, mercury, selenimn, tin, antimony) in fish liver (ppm dry weight) ........................................................................................................... 130
Page ix
EXECUTIVE SUMMARY
~'\ Between 1984 and 1986, the baseline phase of the National Status and Trends Program was conducted at approximately
SO estuarine and coastal sites around the nation. Numerous histopathological observations of fish tissues and measurements of concentrations of chemical contaminants in sediments and fish tissues were made to quantify the status of United States coastal habitats with respect to environmental contamination. One of the products of this effort is a large data set containing information on concentrations of contaminants that possibly may threaten the health of the nation' s coastal ecosystems. This body of data is useful to environmental scientists and managers. The purpose of this document is to make the chemical contaminant data available to the environmental community. Data sununaries are presented in both graphical and tabular form. <"_ ..
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76' 74" 72' 70'
NATIONAL ST A TUS AND TRENDS
PROGRAM
achias Bay(MB) renchmans Bay(FB)
.. .' Penobscot Bay(PB)_ l}.~r Casco Bay(CB) ¥
Benthic Surveillance Project
Merrimack River Mouth(MR)
Salem Harbor(SH) Boston Harbor(BH}
~"---~OUinCY BayCOBl
~ Buzzards Bay(BB} , Narragansett Bay(NB}
Eastern Long Island Sound(EL} Western Long Island Sound(WL}
Raritan Bay(RB}
Great Bay(GB} Baltimore Harbor( BA}
Delaware Bay(DB}
Upper Chesapeake B~y(CU}
Mid Chesapeake Bay(CM}
. Lower Chesapeake Bay(CL)
Elizabeth Rlver(ER)
..
42
66'
Figure 1. Sites sampled in the northeastern United States during 1984-86 as part of the National Status and Trends Program's Benthic Surveillance Project. Site codes in parentheses.
INTRODUCTION
The National Status and Trends (NS&T) Program is an ongoing federal program initiated in 1984 to establish and maintain an information base needed to quantify the status of, and temporal and spatial trends in, concentrations of selected chemical contaminants, as well as indicators of potential biological effects, in the nation's coastal and estuarine ecosystems (National Ocean Service 1989). A nationally uniform set of measurement techniques is used to obtain comprehensive, high quality data on environmental quality. A rigorous quality assurance program is an integral part of the NS&T Program.
One of the NS&T Program's major components is the Benthic Surveillance Project, the objectives of which include quantifying baseline levels of selected chemical compounds at approximately 50 sites in estuarine and coastal areas around the nation, and detecting trends in habitat contamination by monitoring levels of selected chemicals in sediments and fish tissues.
During 1984-86, personnel of the Northeast Fisheries Center (NEFC) participated in the baseline phase of the Benthic Surveillance Project, collecting and analyzing samples of sediments and fish tissues from 20 sites throughout the northeastern region.
The purpose of this document is to make available the large body of chemical data resulting from NEFC participation in the baseline phase of the NS&T Benthic Surveillance Project.
METHODS
Twenty sites were sampled in the northeastern region (Figure 1). A list of station locations, samples collected, and site codes used in the figures in the Analyte Summary section is given in Table 1. A list of variables measured, the matrices in which they were measured, and analyte codes used in the figures in the Site Summary section is given in Table 2.
Sites were selected to encompass a range of environmental conditions. Field methods and sample collection protocols are detailed in a report by Shigenaka and Lauenstein (1988).
AU sediment and tissue samples were collected and stored individually. Depending on the matrix, however, samples were analyzed either individually or as composites. Sediments for both hydrocarbon and metal analyses were composites of the 0-3 cm layer of surface sediment from each of three bottom samples at each of 3-5 stations in each site; one composite per station was analyzed. Thirty specimens of each targeted fish species were collected at each site. Stomach content samples for both hydrocarbon and metal analyses were composites of 10 individual specimens; one composite per site was analyzed. Liver samples for hydrocarbon analyses were composites of 10 individual
Page 1
specimens; three composites per site were analyzed. Liver samples for metal analyses were not composited; 10 individual specimens per site were analyzed.
Methods used for analyses of hydrocarbons in tissues and sediments are described by MacLeod et al. (1985) and Krahn et al. (1988). Hydrocarbon analyses were performed under the direction of D. Gadbois of the National Marine Fisheries Service (NMFS) Gloucester (Massachusetts) laboratory.
Methods used for analyses of metals in tissues were developed at the NMFS Beaufort (North Carolina) Laboratory under the direction of P. Hanson, based on a procedure described by Okamoto and Fuwa (1984). Methods used for analyses of metals in sediments were developed at the NMFS Sandy Hook (New Jersey) Laboratory under the direction of V. Zdanowicz, based on a procedure described by Bernas (1968). Metal analyses were performed under the direction of V. Zdanowicz of the Sandy Hook Laboratory.
Sediment grain size determinations employed a modification of a U.S. Environmental Protection Agency procedure (Plumb 1981). Total organic carbon (TOC) determinations were performed using the method described by Hedges and Stem (1984). Grain size and TOC analyses were performed under the direction of P. Hanson of the Beaufort Laboratory.
DATA PRESENTATION
Data presented in the figures in the Site Summary and Analyte Summary sections are mean values for each analyte for each site over the 1984-86 period. When calculating means, "less than" values were used as best estimates of the actual concentrations. Since "less than" values estimate maximum concentrations, a positive bias is introduced into the calculated means.
The Site Summary section is a graphical summary of data from each site, presenting distributions of analytes in each sample matrix (Figures 2-21). Due to the wide range of concentrations observed, data are presented on a common log scale.
The Analyte Summary section is a graphical summary of data for each analyte by sample matrix, showing distributions of analytes at all sites (Figures 22-28).
No fish specimens were obtained at the Mid Chesapeake (CM) or Baltimore Harbor (BA) sites; therefore, no data appear at those sites in figures of hydrocarbons or metals in stomach contents and livers. In addition, metals were not measured in stomach contents in samples collected in 1986 (see Table 1); consequently, no data appear at the Quincy Bay (QB) or Elizabeth Ri ver (ER) sites in figures of metals in stomach contents. Also, stations sampled at the Casco Bay (CB) site in 1984 were located at the mouth of the bay rather than the interior, so those data were not included in the means shown in the figures. Finally, 1984 tissue data from the Lower Chesapeake (CL) site were not included in any figures, as a different species was collected in 1985 and
Page 2
1986. . Analytical data are presented in the Analytical Data
section (Tables 3-9).
ACKNOWLEDGEMENTS
The authors thank E. Leimburg and P. Fournier for producing the graphics, R Murchelano for suggestions on presentation format, and R. Reid, F. Steimle, A. Draxler, and 1. E. O'Reilly for critical review.
The following NOAA personnel made completion of this project possible through their dedication and their participation in field work, laboratory analyses or project administration: Gloucester Laboratory--C. Auld, P. Chen, B. Dockum, A. Humason, L. Karohl, A. Khan, and R Tremblay; Oxford Laboratory--1. Evans, S. Everline, S. McLaughlin, S. Maclean, R Murchelano, M. Newman, A. Rosenfield, and D. Spitzer; Sandy Hook Laboratory--K. Fedosh, T. Finneran, R Kothe, S. Leftwich, K McNulty, J. Pearce, 1. Vitaliano, S. Wilk, and 1. Ziskowski; and the officers and crews of the research vessels Albatross IV Ferrell, Gloria Michelle, and Kyma. '
!REFERENCES CITED
Bernas, B. 1968. A new method for decomposition and comprehensive analysis of silicates by atomic absorption spectrometry. Anal. Chem. 40(11): 1682-1686.
Hedges, 1.1., and 1.H. Stern. 1984. Carbon and nitrogen
determination of carbonate-containing solids. Limnol . Oceanogr. 29: 657-663.
Krahn M.M., L.K Moore, RG. Bogar, C.A. Wigren, S-L Chan, andD.W. Brown. 1988. A rapid HPLC method for isolating organic contaminants from tissue and sediment extracts. J. Chromatogr. 437: 161-175.
MacLeod, W.D., Jr., D.W. Brown, A.S. Friedman, D.G. Burrows, o. Maynes, R. Pearce, c.A. Wigren, andRG. Bogar. 1985. Standard analytical procedures of the NOAA National Analytical Facility, 1985-1986: extractable toxic organic compounds. 2nd ed. NOAA [Nat. Ocean. Atmos. Admin.] Tech. Mem. NMFS [Nat. Mar. Fish. Serv.] FjNWC-92. 121 pp.
National Ocean Service. 1989. Report to the Congress on ocean pollution, monitoring and research: October 1987 through September 1988. Available from National Oceanic and Atmospheric Administration, National Ocean Pollution Program Office, Rockville, MD 20852. 68pp.
Okamoto, K, and K Fuwa. 1984. Low-contamination digestion bomb method using a teflon double vessel for biological materials. Anal. Chem. 56: 1758-1760.
Plumb, R.H. 1981. Procedures for handling and chemical analysis of sediment and water samples. Tech. Rep. EPA/CE-81-1. Available from U.S. Army Corps of Engineers, Waterways Experiment Station, P.O. Box· 631, Vicksburg, MS 39180. 478 pp.
Shigenaka, G., and G.G. Lauenstein. 1988. National Status and Trends Program for Marine Environmental Quality: Benthic Surveillance and Mussel Watch Projects sampling protocols. NOAA [Nat. Ocean. Atmos. Admin.] Tech. Mem. NOS [Nat. Ocean Serv.] OMA 40. 18 pp.
Page 3
Table 1. Northeast sampling locations and sample types collected from 1984 through 1986. Site codes in parentheses.
Station N.Lat. W.Long. 1984 1985 1986 Station N.Lat. W.Long. 1984 1985 1986
Machias Bay (MB) Boston Harbor (BB)
MB1 44°38.0' 67°20.1' S S S,LS BH1 42°20.9' 70°58.0' S,WF S,WF MB2 44°38.2' 67°19.1' S,LS BH2 42°19.8' 70°58.2' S S S MB3 44°40.7' 67°20.8' S S BH3 42°19.7' 71°00.1' S S S MB4 44°38.8' 67°20.7' S S BH4 42°20.7' 70°58.9' S
BHS 42°20.5' 71°00.2' S Frenchmans Bay (FB) BH6 42°19.7' 70°57.8' WF
FBI 44°26.8' 68°13.3' S S Quincy Bay (QB) FB2 44°26.5' 68°10.4' S S FB3 44°23.0' 68°09.9' S,LS S QB1 42°17.5' 70°59.2' S,WF FB4 44°19.0' 68°08.1' S QB2 42°17.2' 70°58.0' S
QB3 42°18.4' 70°58.4' S Penobscot Bay (PB)
Buzzards Bay (BB) PB1 44°24.4' 68°53.3' S S PB2 44°19.2' 68°52.0' S BB1 41°36.6' 70°45.2' S S S,WF PB3 44°12.7' 69°00.7' S S BB2 41 °33.3' 70°41.4' S S PB4 44°10.0' 68°46.6' S S BB3 41 °32.5' 70°47.8' S S S PB5 44°07.7' 68°58.4' S LS BB4 41 °33.4' 70°52.6' S S S PB6 44°09.4' 69°02.8' LS BB7 41°35.1' 70°40.8' WF
BB8 41°29.2' 70"70°3' WF Casco Bay (CB) BB80 41 °29.5' 70°53.9' S S S
CB1 43°47.1' 70°03.4' S S Narragansett Bay (NB) CB2 43°43.9' 70°09.0' S S CB3 43°42.8' 70°05.9' S NBI 41°39.5' 71 °19.3' S,WF S S CB4 43°40.6' 70°12.8' S S NB2 41°38.1' 71°23.3' S S S,WF CB5 43°39.6' 70°09.1' S S,LS LS NB3 41 °33.5' 71°23.7' S S S CB12 43°40.0' 69°49.1' WF NB4 41"32.6' 71°19.6' S,WF S,WF S CB14 43°38.0' 69°49.3' S CB15 43°41.0' 69°56.7' S Eastern Long Island Sound (EL)
Merrimack River (MR) EU1 41°14.1' 72°10.6' S S S ELI2 41 °15.5' 72°15.1' S S S
MR1 42°50.9' 70°47.7' S ELI3 41°10.1' 72°19.3' S S S MR2 42°48.5' 70°47.5' S S ELI4 41°13.9' 72°13.4' WF MR3 42°43.3' 70°44.0' S S,WF ELlS 41°07.9' 72°31.9' S MR4 42°45.0' 70°42.0' WF ELI6 41 °08.5' 72°24.2' WF WF
Salem Harbor (SB) Western Long Island Sound (WL)
SH1 42°31.0' 70°52.4' S S S WLIl 41°00.7' 73°22.1' S S SH2 42°31.5' 70°51.6' S S S WLI2 40°55.9' 73°35.6' S S S SH3 42°32.3' 70°51.0' S S S WLI3 40°55.1' 73°41.0' S SH4 42°31.3' 70°52.0' WF S WLI4 40°52.8' 73°44.8' S S SHS 42°32.2' 70°49.6' WF WF WLI6 40°57.2' 73°31.2' WF WF WF
Station N.LAt. W. Long. 1984 1985 1986 Station N.Lat. W.Long. 1984 1985 1986
RAritan Bay (RB) Upper ChesApeAke BAY (CU)
RBI 40°27.2' 74°00.8' S S S CUll 38°51.6' 76°26.0' S S RB2 40°29.5' 74°10.2' S S S CU22 38°55.7' 76°25.0' S S RB3 40°29.0' 74°05.1' S S S CU33 39°01.4' 76°22.4' S S RB4 40°32.1' 74°02.9' S S CU44 39°05.8' 76°20.0' S S RB5 40°35.6' 74°01.1' S S CUS5 39°12.2' 76°16.6' S S RB7 40°29.2' 74°04.4' WF WF CU4 38°57.7' 76°26.0' SP SP
GreAt BAY (GB) Mid ChesApeAke BAY (CM)
GBI 39°31.7' 74°21.7' S S CMl 37°47.3' 76°10.7' S S GB2 39°31.6' 74°23.5' S S CM2 37°52.2' 76°07.8' S S GB3 39°30.7' 74°23.7' S S CM3 37°58.5' 76°11.1' S S GB4 39°32.7' 74°24.3' S CM4 38°05.1' 76°13.1' S S GB5 39°31.1' 74°22.1' WF GB30 39°26.1' 74°24.2' WF Lower ChesapeAke BAY (CL)
DelaWAre Bay (DB) CLl 37°09.1' 76°10.6' S S S CL2 37°14.3' 76°04.2' S S S
DBI 39°03.9' 75°13.3' S S S CL3 37°19.0' 76°11.1' S S S DB2 39°19.6' 75°23.0' S CL4 37°11.1' 76°11.9' SP DB4 39°04.2' 75°13.4' WPF WPF WPF CL6 37°10.1' 76°14.7' CR SP DB9 38°57.6' 75°04.5' S DB 11 38°50.9' 75°04.5' S ElizAbeth River (ER) DB15 38°52.8' 75°10.3' S S DB16 38°55.1' 75°02.0' S S ERI 36°52.8' 76°20.3' S
ER2 36°50.33' 76°15.1' S Baltimore Harbor (BA) ER3 36°48.6' 76°17.35' S
ER6 36°51.4' 76°20.4' CR BAHI 39°13.6' 76°33.0' S BAHZ 39°14.7' 76°33.8' S BAH3 39°15.5' 76°34.7' S
Table 2. Variables measured, sample matrices, and key to analyte codes used in Site Summary section
Ace C N P Z T M A H S S S G 0 R U IBN L N S G E 8 N
STOMACH METALS
P P 10000.0 M
o R Y
W G T
P P
1000.0 +---------j<,M------
100.0 +---!)OO-----£>OO-tioo-e.~---
1000.0
Ace C N P Z F M A H S S G 0 R U IBN ENS G E N
UVEA METALS
M 100.0 +------~-m------
o R y 10.0 +----ISM--~-fl.M:------
W G T 1.0 +=,------~-_tWI*94*94i'n'1__f'i&!_-~-
O.l..u..o.L>J...J.AAI. .......... u.AJ....I..:...o..L..L. ............. '-AJ.J.4 ............. ..............,......,...'U"O":"L..L.:..o.L Ace C N P Z F M A H S 5 G 0 R U I 8 N ENS G E N
Figure 7a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals. stomach PAHs. stomach metals, sediment texture, liver metals) for Salem Harbor.
SEDIMENT PESTlCDES
100.0
P P B D 10.0 R Y
W G T
A A A A A A A A A A A A A A A 233 3 3 3 3 3 3 334 444 9 0 1 2 3 4 5 6 7 890 1 2 3
STOMACH PESTlCl)fS
p P B
100.0
D 10.0 R Y
W G T
A A A A A A A A A A A A A A A 233 333 3 333 3 4 4 4 4 9 0 1 2 3 4 5 678 9 0 123
UVal PESTICIDES
1000.0
P p B 100.0 +-------..-.-rf'.l\i\-f.i'ii\-l'i"i+---;;;;;;;----
o R y 10.0 -+=-----m~~~~~*_-
W G T 1.0 -1M-M------I.'X'5I----JIixl\I-M-l<'I6I-I1I~'I-M-&'\HiSi'\HI'ii'\I_
A A A A A A A A A A A A A A A 2 3 3 3 333 333 3 4 444 9 0 1 234 5 6 7 890 '1 2 3
p P B
D R
Page 17
SEDlJfNT PCBs
Y 1O+-~~r&~~~~YMMH~~-
W G T
p P B
A A A A A A A A 4 4 4 4 4 455 4 5 6 7 8 9 0 1
STOMACH PCBs
D 100 +-------I'R:.&+-l'~~)!\/f------R Y
W G T
p P B
D R
1000
A A A A A 4 4 4 4 4 4 5 678
A A A 455 9 0 '1
LIVER PCBs
Y 100 +------lr"l/'iI't4-l.w.riHi'li~~8-----
W G T
A A A 444 456
A A A A A 44455 78901
Figure 7b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs,liver pesticides, liver PCBs) for Salem Harbor.
M 100.0 +----\i'iN-R'i'il------l19iH1'i'\I--'o/'i/<r-----
o R y 10.0 +---&OO-~)OO-t)'M+w---------w~;r__--_&OO_
W G T 1.0 -1N\IIH'NI-~I'li9H~i'iII-l'I"l'r------I'r'i'I-I'i"o'!_rr._r___f'.i".i+_1\i91_
Ace C N P Z T M A H S S S G 0 R U IBN L N S G E B N
STOMACH METALS
100000.0
P p 10000.0 +-------------!'iM-----
M
o R Y
W G T
P P
1000.0 +----------liM-----
100.0 +--~=--~~~M_---
1000.0
Ace C N P Z F M A H S S G 0 R U I 8 N ENS G E N
UVEA METALS
M 100.0 +-------.....".~-----
o R y 10.0 +----M'\---N\o!!--I\M------
W G T 1.0 --I!"iI91----I'<>9I--+\l9I--f9'*-f9'*-I99!--I99!--!';>94--
Ace C N P Z F M A H S S G 0 R U IBN ENS G E N
Figure Sa. Concentrations of analytes within sample matrices (sediment PAHs. sediment metals. stomach PAHs, stomach metals, sediment texture, liver metals) for Boston Harbor.
SEDItvENT PESTlCDES
P P B
100.0
o 10.0 R Y
W G T
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 334 444 9 0 123 4 567 890 1 2 3
STOMACH PESTlClJES
P P B
100.0
o 10.0 R Y
W G T
A A A A A A A A A A A A A A A 2 3 3 333 3 333 3 4 4 4 4 9 0 1 234 5 6 7 8 9 0 123
UVEA PESTICIDES
p P B
D R Y
W G T
1000
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 444 901 234 567 890 1 2 3
p P B
o R y
W G T
P P B
D R Y
W G T
p
Page 19
SEDM:NT PCBs
noo~----~~~------------
10000.0
A A 4 4 4 5
A A 4 4 6 7
A 4 8
A A A A A 4 4 444 4 5 678
A 4 9
A 5 o
A 5 1
STOMACH PCBs
A A A 4 5 5 9 0 1
lIVER PCBs
P B 1000.0 +-----~~~_JM.:;~;.oot_-----
o R Y
W G T
A A A A A A 4 4 4 4 4 4 4 5 6 7 8 9
A A 5 5 o 1
Figure 8b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Boston Harbor.
Page 20
SEDIMENT PAHs
P P B
D R
1000
Y ~~~------~~~~~~~---
W G T
A A A A A A A A A A A A A A A A A A 1 1 1 1 1 111 1 222 2 2 2 222 1 2 345 678 9 0 1 2 3 456 7 8
STOMACH PAHs
1000
P P B
D R Y
W G T
A A A A A A A A A A A A A A A A A A 111111111222222222 12345 6 7 8 9 0 1 2 345 678
~TEXTlft
I.
o R y
W G T
100
~+-------~~HM~----
A L
F E
s c
S I
o c
P P M
D R Y
W G T.
P P M
D R Y
W G T
SEDu..ENT METALS
1000.0
~.o
10.0
1.0
0.1 A C C C N P Z T M A H S S S G D R U I 8 N L N S G E 8 N
Metals in stomach contents
not measured in
1986 specimens
UVEA METALS
10000.0
'K)()O.O
100.0
10.0
to
0.1 A C C C N P Z F M A H S S G D R U I B N E N S G E N
Figure 9a. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, stomach P AHs, sediment texture, liver metals) for Quincy Bay.
SED~NT PESTJCI)ES
p P B
m.o
o 10.0 R Y
W 1.0 +-----~_f,{,.lf_~Mf..!~/!_Mo1I_f,{,.lf_Mi1_ G T
A A A A A A A A A A A A A A A 2 3 3 333 3 333 3 4 444 9 0 1 234 567 890 1 2 3
STOMACH PESTICIDES
p P B
m.o
o 10.0 R V
W G T
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 444 9 0 1 234 567 890 1 2 3
LIVER PESTICIDES
p P
1000.0
B 1OO.0+-----~~~----
o R y 10.0 -!M----v"I~_w;Ii*WH~w___~I_m-
W G T 1.0 -l&'\I-M-----.;:><~I_M_~Wl6:~rM1~~)I_M
A A A A A A A A A A A A A A A 2 3 333 333 3 3 3 4 4 4 4 9 0 1 2 3 4 5 6 7 8 9 0 123
p P B
D R Y
W G T
p P B
Page 21
SEDtENT PCBs
m+------~~~r------
1000
A A 4 4 4 5
A A A 444 678
A A A 455 901
STOMACH PCBs
o 'K)() ~rM__/I~~>M_t~~~~t__-
R Y
W G T
p P B
'0000
A A 4 4 4 5
A A A A A A 4 4 4 4 5 5 6 7 890 1
LIVER PCBs
o 1XlO +_--------t.~__Moe<M__o;~---R Y
W ~+-~~~~~~~~~~-G T
A A A 444 456
A A 4 4 7 8
A 4 9
A 5 o
A 5 1
Figure 9b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Quincy Bay.
Page 22
SEDIMENT PAHs
P P
1000.0
B 100.0 +-------,.,.o-M+::==--n7';------
o R y 10.0 -\K4-1*\-,.=l'i?l----»I-I~>W;>4~~~'i4=;_
Figure 12a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for eastern Long Island Sound.
SEDLVENT PESllOOES
tOO P P B
o R y 0.10 +--------;:;o:;------j~=--
W G T
0.01 ~~~~~~~w..:.L~~""'_'A~ .......... A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3
STOMACH PESTJCI)ES
P P B
100.0
o 10.0 R Y
W G T
A A A A A A A A A A A A A A A 233 3 3 3 333 3 3 4 4 4 4 9 0 1 234 5 6 7 890 1 2 3
UVEA PESTICIDES
1000.0
P p B 100.0 +------------f',l<,:\------
D R Y 10.0 +------004~~)4000il_W1_W'tl1*_-
W G T 1.0 ~-1¥lI-____i!~~--&'lI-_I!\o!\H!'.!IH!'.!\I-W'>HMI~~W
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3
10.0 p P B
D R
Page 27
SIDIvlENT PCBs
Y tO~Mr------~~~----------
W G T
p P B
1000
A 4 4
A 4 5
A 4 6
A 4 7
A 4 8
A 4 9
A 5 o
A 5 1
STOMACH PCBs
D ~+-------~~~~--------R Y
W 1O~WH~~~~~~~M-----G T
P P B
1000
A A A 4 4 4 456
A A A A 444 5 7 8 9 0
A 5 1
UVEA PCBs
o 100 +------~:6H~~~~j__----R Y
W n+-~~~~HW~~~~MM~~ G T
A A A A A 4 4 444 4 5 678
A A A 455 901
Figure 12b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomachPCBs, liver pesticides, liver PCBs) for eastern Long Island Sound.
Page 28
SEDIMENT PAHs
P P B
D R
"k)()()
Y ~+---------~~~~~~~~
W G T
A A A A A A A A A A A A A A A A A A 111111111222222222 12345 6 7 8 901 2 345 6 7 8
D R Y 10.0 +----M\'}l:iM-l~~OO------M+------V'i'ii"
W G T 1.0 -Il'*I-=-lSt9I-l'i'i'H99H'i9H5\'X1------!S:'~<'I_--__=_w
10000.0
P
Ace C N P Z T M A H S S S G D R U IBN L N S G E B N
STOMACH METALS
P 1000.0 +------------~9*_------M
D R Y
W G T
P
100.0 +------"""'rI'ii'5Ij~f_______----
10000.0
Ace C N P Z F M A H S S G D R U IBN ENS G E N
UVEA METALS
P 1000.0 +---------------1"i"O't------M
~ 100.0 +---------f~M-----
Y
W G T
10.0 +----tm--~~~~~--
Ace C N P Z F M A H S S G D R U IBN ENS G E N
Figure 13a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for western Long Island Sound.
A A A A A A A A A A A A A A A 2 3 3 3 333 3 3 3 3 4 4 4 4 9 0 1 2 345 678 9 a 1 2 3
STOMACH PESTJCI)ES
p P B
100.0
o "Xl.O R Y
W G T
A A A A A A A A A A A A A A A 2 3 3 333 3 3 3 3 344 4 4 9 a 1 2 3 4 5 6 7 8 9 a 123
LIVER PESTICIDES
p P
1000.0
B 100.0 +-----------.._---/'i'Jlf------
o R y to.O -I-------".,,...---~I_bMbM-!~~~rW""""'"
W G T 1.0 -lII%I~-~h=-~~~~~~~
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 444 9 a 1 2 3 4 5 6 7 890 1 2 3
P P B
o R
Page 29
SEDtJ.ENT PCBs
y ~+-~~~~oooo~~~~----
W G T
P P B
o R
A 4 4
A 4 5
A 4 6
A 4 7
A 4 8
A 4 9
A 5 o
A 5 1
STOMACH PCBs
y no +-------/;9;)9Q....l;:>;>Q9;~;.;:q.....j~I__--
w G T
P P B
o R y
W G T
A A 4 4 4 5
A A 4 4 6 7
A A 4 4 8 9
A 5 o
A 5 1
LIVER PCBs
DOO+-----~~~------
A A A A 4 4 4 4 4 5 6 7
A A A A 4 4 5 5 890 1
Figure 13b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for western Long Island Sound.
Page 30
S8JIMENT IP AHs
p P B
o R
1000
y ~~~~----~~~~~~~~
W G T
A A A A A A A A A A A A A A A A A A 1 1 1 1 1 1 1 1 1 2 222 2 2 222 123 4 5 678 9 0 1 2 3 4 5 6 7 8
STOMACH PAHs
P P B
o R
1000
y ~+-~--~--~~~~~~~*-
W G T
A A A A A A A A A A A A A A A A A A 111 1 1 1 1 1 1 222 2 2 222 2 1 2 3 4 5 678 9 0 1 2 3 456 7 8
SEDIMENT TEXTLR:
'I.
D R Y
W G T
100
~+-------~~~~----
A L
F E
s c
S I
o c
p P
1000.0
S8JIMENT METALS
M 100.0 +----m-m--4i~W___1'i>;j_-------
D R Y 10.0 -l----W-m.1;,M.l!~M__R>?t_Ni~----_llM
W G T 1.0 -mH9Q\~OOi~~~-I'<'>!I-l9lx-m'h:o:-r1'i'l?!-l'i9f
10000.0
p
Ace C N P Z T M A H S S S G 0 R U I 8 N L N S G E B N
Figure 14a. Concentrations of analytes within sample matrices (sediment PARs, sediment metals, stomach PARs, stomach metals, sediment texture, liver metals) for Raritan Bay.
SBlLVENT PESTlCDES
m.o P P B D 10.0 R Y
W G T
~1~~~~~~~~~~~~~
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 1 2 3 4 5 6 7 890 1 2 3
STOMACH PESTlCl)ES
P P
1000.0
B 100.0 -I----------1~____fiI'~--
D R Y 10.0 +-----~iM_~~~____flt4__
W G T 1.0 -IlIQ';I-II99-~~<4___lIS:'SfM_M-Im_Ii~~iI_M_M_
0.1 JJ6.1$J..J2Q!J..J.lQ;LJ.!S;l!:I..ruJ..J.lSl5J..J.!QlLll~~~IISJSJ...I.!=~ A AA A A A A A A A A A A A A 2 333 333 333 3 444 4 9 0 1 234 567 8 9 0 123
UVEA PESTICIDES
P P B
1000
D 100 R Y
W G T
A A A A A A A A A A A A A A A 2 3 3 3 3 333 3 3 344 4 4 9 0 1 2 3 4 567 890 1 2 3
P P B
1000
Page 31
SEIJt.fNT PCBs
o 100 ~----;o=-IQQQ~~~j-----R Y
W 1O~~~~~~~H*~~~= G T
P P B
o R
1000
A A 4 4 4 5
A 4 6
A A 4 4 7 8
A A 4 5 9 0
A 5 1
STOMACH PCBs
y 1OO+-~~~~~~~~w-----
W G T
P P B
o R y
W G T
10000
A A A A 4 4 4 4 4 5 6 7
A A A A 4 4 5 5 890 1
UVEA PCBs
1000 +----....rvvr-1VV'O'"vr-==-----
A A. A A 4 4 4 4 4 567
A A 4 4 8 9
A A 5 5 o 1
Figure 14b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomach PCBs, liver pesticides, liver PCBs) for Raritan Bay.
Page 32
S8JIMENT PAHs
1000.0
P P B '00.0 +---------;e+.o:..-=-----
o R y 10.0 -1I"rl1i91==-----AA-l'i'H'iI'l-M-~i'l_M.Jl'.lH'~1___
W G T 1.0 -fOO-IW1i''~OO_____wI-001~:H*oo*E;tOO_oo1i~1OO
A AA A A A A A A A A A A A A A A A 111111111222222222 123 456 789 0 1 2 3 4 5 6 7 8
Figure 15a. Concentrations of analytes within sample matrices (sediment PAHs, sediment metals, stomach PAHs, stomach metals, sediment texture, liver metals) for Great Bay.
SEDM:NT PEST1CDES
p P B
o R
10.0
y to+-----~--------~~M-----
W G T
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 123 4 5 6 789 0 123
STOMACH PESTlOOES
p P B
100.0
o 10.0 R Y
W G T
A A A A A A A A A A A A A A A 233 333 3 3 3 3 3 4 444 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3
UVEA PESTlCIDES
p P
m.o
B 100.0 +-----------=----Ir,;t,;\----f,l\,l---
o R y 10.0 +-----__ --Mlt-004l~OO-OO4*'lI-OO4-~..,
W ~ W~~~_w~~~~ww~~~
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 444 9 0 123 4 567 890 123
p P B
o R
Page 33
SEDl.£NT PCBs
y t)+-----':««I--t«*-':««f--Wi:o.?t-----
W G T
p P B
o R Y
W G T
p P B
D R
A A A 444 456
A A A A A 4 4 4 5 5 7 8 9 0 1
STMCH PCBs
1OO+------~~h=~---
A A 4 4 4 5
A A A A A 4 4 445 6 7 890
A 5 1
UVEA PCBs
Y 1)(} +-------W9i'll-.ltWj~I9i4-{l'i:9l"1_-----
W G T
A A 4 4 4 5
A A A 444 678
A A A 455 901
Figure iSb. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides, stomachPCBs, liver pesticides, liver PCBs) for Great Bay.
Page 34
SEDIMENT PAHs
P P
1000.0
B 100.0 +-------------M.j--------
D R Y
W G T
0.1 ~t:JC1J::>ana.=..t::Li..I:::.::!.OC1l~:u::.a.=.:u::.a..t::aL=lllCl A A A A A A A A A A A A A A A A A A 1 1 111 1 1 1 1 222 2 2 2 2 2 2 1 234 5 6 7 890 1 234 567 8
STOMACH PAHs
P P B
1000
D 100 R Y
W G T
A A A A A A A A A A A A A A A A A A 111111111222222222 1 2 3 4 5 6 7 8 9 0 123 4 5 6 7 8
A A A A A A A A .A A A A A A A 2 3 3 333 333 334 444 9 0 1 2 3 456 7 8 9 0 123
SEDIMENT TEXTIllE
'I.
o R y
W G T
100
1O-t------'Ie>E)OO€!--'Ie>E)OO€!--
A L
F E
s c
S I
o c
P P 8
D R Y
W G T
P P
1000.0
A A A A 4 4 4 4 4 5 6 7
SEDf.ENT PCBs
A A 4 4 8 9
A 5 o
A 5 1
SEDLVENT METALS
M 100.0 +---m-m----li9'lH/'it'JI-----J.."'X'ir-----
D R Y 10.0 +---f)OO+El4-t)OO-BoOO-I~~oo-f)OO_-~>4f)OO_
W G T
Ace C N P Z T M A H S S S G D R U IBN L N S G E B N
No fish specimens obtained
Figure 18. Concentrations of analytes within sample matrices (sediment P AHs, sediment metals, sediment texture, sediment pesticides, sediment PCBs) for Baltimore Harbor.
SEDtJENT P AHs
1000.0
P P B m.o o R y 10.0
W G T 1.0
0.1
~ ~~
8]B:8
I ~~ ~~ ~~ ~~ ~~ ~ ~~ ~~
~ ~~ ~ ~ ~ ~ ~~ ~~ ~ :X ~
~ ~~ ~~ X»Si g A A A A A A A A A A A A A A A A A A 1 1 1 1 1 1 1 1 1 2 2 2 2 2 2 2 2 2 1 234 567 890 1 234 5 678
SEDtJENT PEST1CDES
to p p B
o R y
W G T
0.1-"""" ...................... ""'"-' ............. """-"'.........". .......... ""-""' ......... '-"""".....,..."""""'-'....,... A A A A A A A A A A A A A A A 2 333 3 333 3 3 344 4 4 90123 456 7 8 9 0 1 2 3
SErnVBfT TEXT~
'I.
o R y
W G T
100
1O+------l!'leI~~M---
A L
F E
s c
S I
o c
p P B
0 R Y
W G T
P P M
o R Y
W G T
Page 39
SEDtvENT PCBs
10.0
to
0.1 A A A A A A A A 4 4 4 4 4 4 5 5 4 5 6 7 8 9 0 1
A A A A A A A A A A A A A A A A A A 1 1 1 1 1 1 1 1 1 2 2 222 2 2 2 2 1 2 3 4 5 6 789 0 1 234 5 678
SEDIMENT TEXTlllE
'/.
o A y
W G T
100
A L
F E
s c
S I
o c
P P M
D R Y
W G T
P P M
D R Y
W G T
SEDtJENT METALS
1000.0
100.0
10.0
1.0
0.1 Ace C N P Z T M A H 5 S 5 G D R U I B N L N S G E B N
Metals in stomach contents
not measured in
1986 specimens
UVEA METALS
1000.0
100.0
10.0
1.0
0.1 A C C C N P Z F ~ A H S S G D R U I B N E N S G E N
Figure 21a. Concentrations of analytes within sample matrices (sediment PAlls. sediment metals, stomach PAlls, stomach metals, sediment texture, liver metals) for the Elizabeth River.
SEDM:NT PESTICIlES
10.0
P P B
o R y to+---------~~~~~~~OO--
W G T
0.1 ~..I.II.lo.I.~~~.IW4I11.1Al\l..lAl>.L.Io!.loj..l.ll.lo.l..IAtoj,J..:..:.w.~"'" A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3
STOMACH PESTICIDES
P p B
100.0
o 10.0 R Y
W G T
A A A A A A A A A A A A A A A 2 3 333 3 3 3 3 3 3 4 444 9 0 1 234 567 890 1 2 3
lJVER PESTICIDES
1000.0
P P B 100.0 +----------mf-rn:r---
o R y
W G T
A A A A A A A A A A A A A A A 2 3 3 3 3 3 3 3 3 3 3 4 4 4 4 9 0 1 234 567 8 9 0 123
p P B
o R
100
Page 43
SEDtJENT PCBs
y 1O+-~~~~~~~HMMrWW~--
W G T
p P B
1000
o 100 R Y
W G T
p P B
o R y
W G T
A 4 4
A 4 5
A 4 6
A 4 7
A 4 8
A A A A A 4 4 444 4 5 6 7 8
A A A A A 4 4 444 4 5 678
A 4 9
A 5 o
A 5 1
STOMACH PCBs
A A 4 5 9 0
A 5 1
UVER PCBs
A A 4 5 9 0
A 5 1
Figure 21 b. Concentrations of analytes within sample matrices (sediment pesticides, sediment PCBs, stomach pesticides. stomach PCBs, liver pesticides, liver PCBs) for the Elizabeth River.
Page 44
NAPHlHALEN:
P P
1400
B 1050 +_--------l*1r-----
D R Y 700+--~~----_Mr_---
W G T ~~-~~----~~---
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
1 - METHYL.NAPHTHALEt£
P p
1400
B 1050 +_--------l*1r-----
D R Y 700+---------Mr_---
W G T ~+--------~r-------
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
2, 6 - I».£THYl.NAPHTHALEt.£
P P B
1500
D 1000
R Y
~ ~+---------OOr_--T
ECCCBDGRWENBOBSMCPFM RLMUABBBL LBBBHHRBBBB
P P B
3300
o 2200 R Y
2 - METHYLNAPHTHAJB.E
W ~+-_______ ~ ___ __ G T
P p B
300
D 200 R Y
o~--~~~~--~~~------
ECCCBDGRWENBOBSMCPFM RLMUABB8LL888HHR888B
~ 100 +_------;;>(I-----------J;><;);------
T
P P B
120
D 80 A Y
ECCCBDGRWENBQBSMCPFM R LMUABB8 L L 8BBHHR8888
ACENAPHn£NE
~.~~--1~~~--~~---T
ECCCBDGRWENBOBSMCPFM RLMUABB8LLB88HHR8888
Figure 22a. Concentrations of hydrocarbons (naphthalene, 2-methylnaphthalene, I-methylnaphthalene, biphenyl, 2,6-dimethylnaphthalene, acenaphthene) in sediments from all sites.
FLlJOR&£
300
P P B o 200 R Y
~ 100 -lM---=i:~------fjEot---T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
ANnmCENE
900
p P B o 600 R Y
~ 300 -lOO---4;~--OO-----OO---T
ECCCBOGRWENBQBSMCPFM RLMUABBBLLBBBHHRBBBB
FLUORANTHENE
1500
p P B o 1000 R Y
~ ~~-~~-OO~-~ffiffi~---T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P
Page 45
B 750 +----~~-----M-----
o R Y ~~--~~------~~-----
W G T 250 -1i<*---~>4--~ft€+-----*~<'t------
p P B
4500
03000
R Y
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~ ~OOr---------OOr--T
P P
- B
1800
o 1200 R Y
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
PYRENE
~ ~~-~r--Mmr-~~~--T
E C C C B'O G R WEN B Q B S M C P F M RLMUABBBLLBBBHHRBBBB
Figure 22b. Concentrations of hydrocarbons (fluorene, phenanthrene, anthracene, I-methylphenanthrene, fluoranthene, pyrene) in sediments from all sites.
Page 46
BENZO [aJ ANTliRAce£
P P B
750
0500
R Y
~ 250 -lM---!;~~<lOO--~~--T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
BENZO [e] PYRENE
P P B
1200
o 800 R Y
W 400~--~~~*=--~~~---G T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
PERYLENE
P P B
600
o 400 R Y
~ 200 -;OO---oo100---~---------T
ECCCBOGRWENBOBSMCPFM R L M U AS B B L L B B B H H R B B B B
P p
1400
~YSENE
B ~50~-~r----------
o R Y 700 -iM-----!~----~'-':l-------
W G T ~~-~~~~r---~~~-----
P P B
1200
o 800 R Y
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
BENZO [aJ PYRENE
~ 400~-~~~~--~~-----T
P P
280
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
DIBENZO [a, h1 ANTliRACENE
B 2ID~-----------------
D R Y ~O~--~~----------
W G T 70~-~~~~~-~~~---
ECCCBDGRWENBOBSMCPFM RLMUABBB L L BBBHHRBBBB
Figure 22c. Concentrations of hydrocarbons (benzo[a]anthracene, chrysene, benzo[e]pyrene, benzo[a]pyrene, perylene, dibenzo[a,h]anthracene) in sediments from all sites.
P P B 6+---~~-------------------
o R y 4+---~~-------------------
W G T 2+---~~~~------~~-----
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
I-£PTACHLOR
P P B
t5
o to R y
~ 0.5 +------OO---------i'~L---OO--l'ie-oooooo T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
I-£PTACHLOR EPOXDE
p P
1.00
B 0.75 +---~oo----------
o R y 0.50 +-------ll?l---------
W G T 025~~~~~-~=-~*-~~-
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
3.3
022
R Y
Page 47
~ 1.1+-------~OO-~---«~---T
p P B
4.5
o 3.0
R Y
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B ~
ALDRN
~ ~+-------~~~~--~~~OOT
p P
40
B 30
o R y2Q
W G T 10
o
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
0, p' - DOE
.rr> ~~~
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 22d. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p'-DDE) in sediments from all sites.
Page 48
alpha - Clt.ORDAt£
p P B
6
o 4 R Y
~2+---~~~~--~~~------T
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
DIELDRIN
p P B
3
02
R Y
~ 1r----1*--1*--1*-~~------T
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
0, p' - ODD
P P B
9
o 6 R Y
~3~--~~~~----~~~----T
o~==~==~==~==~==~==~=
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
P P
4
trans - NONACH..OR
B 3 r---~<2tOO----te-(t-----------i~t-OO--------
o R y 2 +-----I".i'l-M--1".i't--------'l'i'HYfM--------
W G T 1~--~~~#*-*~*»~------
P P B
12
o 8 R Y
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
p, p' - OOE
W 4 -lOO----1*-----£~----~~----G T
P P
36
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
p, p' - DOD
B 27r---------------~(t-----------
o R y ~+-----------------1".~------
W G T 9+---~~~~----~~------
o~=-~==~~~===ww=~~=-
ECCCBDGRWENBOBSMC'FM R L M U A B B B L L B B B H H R B B B B
Figure 22e. Concentrations of hydrocarbons (a-chlordane, trans-nonachlor, dieldrin,p,p' -DOE, o,p' -DDD,p,p' -DOD) in sediments from all sites.
0, p' - OOT
5
P P 4+-------~------~---------B
o 3+---~~~~----~--------R Y
W 2 G
T 1~--~~~~----~~~-----
tJJREX
P P B
3
o 2 R Y
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~ 1+---------~~--~~------T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
TRlCK.OROBA£NYl.S
P P
400
B 300+---------------~~------
o R y ~+---------------~~------
W G T »o+---------------~~------
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
3
o 2 R Y
Page 49
p, p' - DDT
~ 1-lM---~~---£~--M-£i~--T
p P
20
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
DICH..OROBfI-ENYLS
B ~+--------------w~---------
o R y ~+--~~~~-~------
W G T 5+--~*-~*-~~~~-~*-
P P B
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
TETRACH.OROBPI-ENYLS
2700
01800 R Y
~ ~+---------------~-------T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 22f. Concentrations of hydrocarbons (o,p' -DDT, P,P' -DDT, mirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in sediments from all sites.
Page 50
PelT ACtt.OROBIPHENYLS
2400
P P B 1800
D R Y 1200
W G T 600
o IrV"I ,R>l~ .~ ,ml'Q'l 1M
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
I-EPTACH.OOOBFt£NYLS
P P B
120
8O+------1>9'!-------""*"".,-----D R Y
W40+------100----100---~oo-eoOl;__--G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
NONACH.OR081P1-ENYLS
"Kl
P P 8 B
D 6 R Y
W 4 G T 2
o
~
~I ~
~ ~ ~ILrV"I """"" iX,=
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
P P B
600
D400 R Y
taACH.OROBPH:NYLS
~ ~+---------~»-------T
P P
40
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
OCT ACH.OROBP1-ENYLS
B 30 +-------100----00-------------I9oEt------
D R Y 20 +--------1<9l---m--------=~il'l------
W G T "Kl~--~~--~--~~~*-----
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
Figure 22g. Concentrations of~ydrocarbons (pentachlorobiphenyIs, hexachlorobiphenyIs, heptachlorobiphenyIs, octachlorobiphenyIs, nonachlorobiphenyIs) in sediments from all sites.
SILVER 6
P P M o 4 R Y
~2+---~~~OO-----~OO-------T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
CIilCMJM
P P M
1800
01200 R Y
~ ~+-----------------~-----T
f«)(a,
75
P P M
050
R Y
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~ 25r---~~~~~~~~~~~ T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P M
6
o 4 R Y
Page 51
~ 2 +---~*I-~OO-------=h€t-----T
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
COPPER
280
P P M ~r---~~------------------
o R y WO+---~*-~~----~~------
W G T 70+*--~*-~~~~~~------
P P M
180
0120 R Y
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
LEAD
W60-IM----="")6------IO~---t3&--M-&EI-OO------G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 23a. Concentrations of metals (silver, cadmium, chromium, copper, nickel, lead) in sediments from all sites.
Page 52
ZINC
660
P P M o 440
R Y
~ ~O~--~f~~~----~~-----T
ECCCBDGRWENBOBSMCPFM ALMUABBBLLBBBHHRBBBB
MANGANESE
1800
P P M
D1200 R Y
W ~~--~~--~w-----~~---G T
o~==~u==ww==a~u=~~~~
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
MERrow 2.4
P P M 18
D R Y 12
W G T 0.6
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
p. P
100
THAWI.J.A
M 0.75 +-'----IJoa------~l-OOli~----
D R Y 0.50 -lM---I'i'H':oIl------t'x'!I-f'x't--Mt'x'H'X'l-Ntf'-'1---oo-t'.>Mx'j--
W G T 025~~~~~~=»~~~~~~
P P
32
ECCCBDGRWENBOBSMCPFM RLMUABBB L L BBBHHABBBB
ARSENIC
M 24+---~*-~=----------------
o R y ~+---~~~~---------------
W G T 8~~MM*=~~~~00#~~~~
P P M
18
D 12 R Y
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
S8..EN1UM
~ 0.6 4----MJ:)4-----t:;~----~I1OO----T
ECCCBDGRWENBOeSMCPFM R L M U A B B B L L B B B H H R B B B B
Figure 23b. Concentrations of metals (zinc, thallium, manganese, arsenic, mercury, selenium) in sediments from all sites.
ANTIMONY
P P
52
M 39~--~~-------------------
D R Y 26+---~~-------------------
W G T O+---~~-------------------
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
SlUCON
40
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
ALlMNllM
9
'/.
D 6+---~~~~~--4*~~~~R Y
W ~ 3~~~~~~~~~~~~~M
ECCCBDGRWENBOBSMCPFM RLMUABBBLlBBBHHRBBBB
P P M
75
D 50 R Y
Page 53
~~+---~~------~~------T
6
"I.
ECCCBDGRWENBOBSMCPFM RLMUABBBLlBBBHHRBBBB
IRON
o 4+---~~~~----~----~~R Y
W ~ 2~~~~~~~~~~~~~
ECCCBDGRWENBOBSMCPFM RLMUABBBllBBBHHRBBBB
Figure 23c. Concentrations of metals (antimony, tin, silicon, iron, ahuninum) in sediments from all sites.
Page 54
TOTAl ORGANC CARBON 5.0 -
'/.
o R Y
W G T
~5~--~~~~~--~~~Nm~-
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H RoB B B B
'/.
o R Y
W G T
100
SLT-CLAY
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
Figure 24. Concentrations of total organic carbon and silt-clay in sediments from all sites.
NAPliTHALaE
P P
800
B ~+-------------~~---------
o R Y400+-------------u<::rM-l'i'l-------
W G T ~+-----------~~#*---------
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
1 - METHYLNAPHTHALENE
P P B
450
0300
R Y
W ~+_--~------~~~»-------_ G T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
2, 6 - DtJETHYl.NAPHTHALEtE
400
P P B300
o R Y200
W G T 100
o
~ ~ ~
1~f9\ .~ ,~~ .rn
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P p-B
300
o 200 R Y
Page 55
2 - METHYLNAPHTH~
W 100 +-----------OO---*"i~--G T
150
P P B
0100
R Y
ECCCBOGRWENBOBSMCPFM R L MU A B B B L L B B B H H R B B B B
W 50 +------------------w-oo---------G T
P P B
75
o 50 R Y
ECCCBOGRWENBOBSMCPFM RLMUABBB L LBBBHHRBBBB
ACENAPHTI-ENE
~ ~+------~~~~----T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 25a. Concentrations of hydrocarbons (naphthalene, 2-methylnaphthalene, I-methylnaphthalene, biphenyl, 2,6-dimethylnaphthalene, acenaphthene) in stomach contents collected from all sites.
Page 56
FLlJOREft:
400
P P B300
o R Y200
W G T XlO
P P B
o
0600
R Y
.~. 1'71 ,~P'7l ~
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~300+-----.oo----~I------T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
FLUORANTI-EfE
P P B
0 R Y
W G T
2000
1500
1000
500
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
2400
01600 R Y
~ 800 +-I*l--=-------OO'OO------&EI----
T
P P
320
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
B 240 +-l*---=------~;l;-----
o R y ~~~~--=---~~----
W G T 80 +--1~--m--___I~4__-___I~----
P P B
1500
o 1000 R Y
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
PYREt£
~ ~+----~~~-~~----T
o~------~~~u=~~~~---
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 25b. Concentrations of hydrocarbons (fluorene, phenanthrene, anthracene, I-methylphenanthrene, fluoranthene, pyrene) in stomach contents collected from all sites.
BENZO [a] ANTHRAce£
P P
2400
B ~+---~-------------------
o R y ~+---~-------------------
W G T ~~*-~----------~-------
o~=-~~~~==w=~~~==~
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
BENZO Ie] PYRENE
P P
500
B 375 ~-----------f:oG-----~O!-------
o R y 250 +-------~<'I---------IS)4-------
W G T ~5~------~~----~~------
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
PERYLEtI:
P P
1400
B l)5O +---------------~~--
o R y 700 +----------------1'\1'1-----
W G T ~+---~---------~~---
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
750
0500
R Y
Page 57
CHWse£
~ 250 +----~}----"---oo----T
P P B
660
o 440 R Y
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
BENZO [a] PYReE
~ ~O+----~~--~---T
100
P P B 75
o R y 50
W G T 25
o
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
DlBENZO [&, h1 ANTHRAcaE
ri"U"i"l .I""a l~~ I,..,.,~~,..,.,~~
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 25c. Concentrations of hydrocarbons (benzo[a] anthracene , chrysene, benzo[e]pyrene, benzo[a]pyrene, perylene, dibenzo[a,h]anthracene) in stomach contents collected from all sites.
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
HEPTACH..OR
P P
32
B ~4+-~-------------
D R Y t6~~--~---------
W G T 0.8 -l=-&M-~----+:~----+:)t-----4i)t-----=r.,.-*4
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
HEPT ACI-LOIR EPO)(I)E
P P B
6
D 4 R Y
~ 2 +-M---M----1:'>efOO-------1M--------l*i
T
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
. 6
P p B D 4 R Y
~ 2 +-I~-=------I!~-OO-----OO-----t;;illM1WT
P
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
ALDRIN
P 8+------#~----------------B
D 6+---~~---------~ R Y W 4+-----~~---------------G
T 2+----W~*--~----,~
P P B
75
D 5.0
R Y
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
0, p' - ODE
~ ~5 -JM-----------------------
T
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
Figure 25d. Concentrations of hydrocarbons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p' -DDE) in stomach contents collected from all sites.
q,ha - CH.ORDAJ£
P P
32
B 24+-------~~~--~~-------
o R y ~+-------~~r---~~-------
W G T 8+---~--~~~--~~~-----
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
01El..D~
P P B
0 R Y
W G T
27
18
9
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
0, p' - DOD
P P B
30
020 R Y
~ 10+-------~~~--~~r-----T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
45
o 30 R Y
Page 59
trans - NONACHLOR
~ 5+-------~~~--~~r_----T
140
P
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRB88B
Po p' - DOE
P B1)5+----~I----!;>4--------------
o R y 70+------R~~-------------
W G T ~+-----~~~--~~~-----
140
P
ECCC80GRWEN80BSMCPFM R L M U A B B B L L B B B H H R B B B B
Po p' - 000
P B1)5+----------E>e---------------
o R y 70+-------~~--------------
W G T ~+-------~*-----~~-----
ECCCBDGRWENBOBSMCPFM RLMUAB8BLLB8BHHRBBBB
Figure 25e. Concentrations of hydrocarbons (a-chlordane, trans-nonachlor, dieldrin, p,p'-DDE, o,p'-DDD, p,p'-DDD) in stomach contents collected from all sites.
Page 60
0, p' - OOT
p P
16
B 12+--------------1~----------
D R Y 8+--------------4~~~------
W G T 4+---------~--~*=~*-------
MlREX
p P B
6
D 4 R Y
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
~ 2~------~~~----~------T
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
TRlCK.OA08IPt£NYlS
P P B
180
D120 R Y
W 60 -ffi€I---------OO--------I'>a.MOOi>Jt;f------G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
p P B
15
D 10 R Y
p, p' - DDT
W 5~--------~------~------~ G T
P P B
600
D 400
R Y
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
DJCli.OROBIPHENYLS
~ 200 +----------------11*\------T
P P
500
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
TETRActl.OROBI'I-ENYLS
B 375+------~~---~~-----
D R Y 250+------~~--~~~------
W G T ~5+-------~~~~~~~-----
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 25f. Concentrations ofhydrocaroons (o,p' -DDT, p,p' -DDT, mirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in stomach contents collected from all sites.
PENT ACtlOROBPHENYLS
p P B
600
0400 R Y
~ ~+-------~~--~~r------T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
I-EPTACli.OROBPt£NYLS
p P B
1200
o BOO R Y
~ ~O+-----------------~~---T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
NONACli.OROBIPI-ENYLS
P P B
15
o 10 R Y
W 5~--------~~~~~M------G T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
660
o 440 R Y
Page 61
HEXACK.OROBI'I-ENYLS
~ ~O+-------~~--~~~r---T
P p
40
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
OCT ACK.OROBR£NYlS
B ~+---------~----------------
o R y ~~------~~--------------
W G T ~~------~~~~*-~*-------
ECCCBOGRWENBQBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 25g. Concentrations of hydrocarbons (pentachlorobiphenyls, hexachlorobiphenyls, heptachlorobiphenyls, octachlorobiphenyls, nonachlorobiphenyls) in stomach contents collected from all sites.
Page 62
SILVER
P P M
3
o 2 R Y
~ 1+-------~~r_----~r_----= T
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
CHROMIUM
P P
160
M 1~+---------------~~------
o R Y80+----------------i'X'H'X'l-------
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~CKa
18
P P M
o 12 R Y
W 6 G T
o
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~ ~
~H~ ~ ~ ~~~ ~ ~~ ~~~~
~ ~~
~~~~~ >X ~~
~~~~ ;x ;x~
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
P P
2.0
M t5 +-----------------~a-w------
o R y to -t---------------------t'J6ffl----=--
W G T 0.5 +------t<3+-----~*+__+e+~~~***-
P P M
90
060
R Y
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
COPPER
~ 30 +------OO----OOr---l2~----~-Effle:----T
P P M
75
050
R Y
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
LEAD
~ 25+-------~~~~~~----T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 26a. Concentrations of metals (silver, cadmiwn, chromium. copper, nickel, lead) in stomach contents collected from all sites.
ZN)
240
P P M
o 160 R Y
~ 80 T
o
1'5<':
~ ~ ~
~ ~ Q<:
~ ~~ ~ Xz ~ ~~ ~ ~ ~ ~ ~ ~i z ~ ~ ~ ~ ~ ~
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MANGANESE
1500
P P M o 1000 R Y
~ ~+---~--~~=-----~~---T
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
~ClJly
tOO
P P M 0.75 +------------------00--------
o R y 0.50 +---------f':i:'i---------f':..Ij-,....--------
W G T 025~----~~~----~~------
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Page 63
IRON
24000
P P M
016000
R Y
W 8000 +---t>Q---,OO-----=-----S€fOO-~S>GWfOO----G T
P P M
60
o 40 R Y
o~~~~w=~~~~~~~
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
ARSEtfC
~ ~+-----------~~---------T
P P M
6
o 4 R Y
~2 T
o
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R ~ B B B
S8..EN1lJv1
)1'j
~ ~~ ~2
~H-:
~~ ~~ ~ !X
~ ~~ ~ ~~ ~~ ~
I~ ~ ~~ ~~~ ~ !X~x ;X
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 26b. Concentrations of metals (zinc, iron, manganese, arsenic, mercury. selenium) in stomach contents collected from all sites.
Page 64
P P M
15
o 10+----------------*~------R Y
~ 5 +---------------~tM_-----T
ECCC8DGRWEN808SMCPFM RLMUA888Ll888HHR8B8B
Figure 26c. Concentrations of metals (tin) in stomach contents collected from all sites.
I-EXACK.OROBENZm:
12
P p B
8 o R y
~ 4 T
o
~ ~ ~~ ~~8! ~ ~
~~ ~
~I~ ~~
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Figure 27a. Concentrations ofhydrocaroons (hexachlorobenzene, lindane, heptachlor, aldrin, heptachlor epoxide, o,p'-DDE) in livers collected from all sites.
Page 66
alpha - C/i.ORDAf'£
P P B
300
D 200
R Y
~ 100 +----------'~'h",._--T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
DIELDRIN
P P B
D R Y
240
~+---------~~---
W80+__--------l~l-OO----G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
0, p' - DOD
P P
40
B 30 -t--------------le>(t-----
o R y 20 +__-----1''i'l------I''ii'l-----
W G T ~+---~-~~~~OO#*-~~-
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
P P B
450
0300
R Y
trans - NONACHLOR
~15O+----------l~l----T
P P B
750
0500
R Y
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Po p' - OOE
~ 250 +-----OO-00J9~---l~l-OO-------e€l--T
180
P P B
0120
R Y
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Po p' - 000
~60-ffi€l---i*j-------e€Ii*H:~------I9oe-oo----T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 27b. Concentrations of hydrocarbons (a-chlordane, trans-nonachlor, dieldrin,p,p' -DDE, o,p' -DDD,p,p' -DDD) in livers collected from all sites.
o. p' - DDT
25
P p 20 B
o 15 R Y
W 10 G T 5
o
w:lEX
12
P P B o 8 R Y
~ 4 T
o
~ ~I ~ ~ ~ ~~
~~ ~ ~~ ~~ ~~
~~ ~~ ~~ X !XiX IX
~;I ~ ~~ ~ ~~ ~~
~ ~~ IX ~~ ~~ ;.; PH~ ~~ iX~ x~
ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
~~
~ ~ ~~ ~iX
~ ~ ~~ ~ ~~
~~ ~iX[8 ~~ ~ ~~ ~ ~~ ~~~ ~~
~ ~~ ~ ~l6~ iX~ ~ iX~ x ECCCBOGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
TRlCH.OROBA£NYLS
P P B
0 R Y
W G T
270
180
90
o~n-~~~wn~~~ww~~~
ECCCBOGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
P P B
60
040 R Y
Page 67
p. p' - DDT
~ 20 -t------1*t-----1:~---oo-t;~1*HO~---OO T
50
P
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
DICtt.OROBAENYLS
P 40+-----------~~ B
o ~+------------------M~R Y W20+-------~r--~~~
G T 10+---~~--~~~~~~
1250
P
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
TETRACH.OR~YLS
P mO-t-------~r-----~------B
D 750+-------~~----~------R Y W ~O-t-----~~~~~~------G
T 250+-----~~~~~~~-----
O~~~~~~~~~~~~=
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 27c. Concentrations of hydrocarbons (o,p' -DDT, p,p' -DDT, mirex, dichlorobiphenyls, trichlorobiphenyls, tetrachlorobiphenyls) in livers collected from all sites.
Page 68
PENT ACH..OAOBPHENYLS
P P B
2700
D1800 R Y
W ~+_------~~--~~~----__ G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
I-EPTACli.OROBfl~
P P B
1500
D 1000 R Y
W ~+-______ ~~~=-~~~~ ___ G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
NONACli.OROBPI-£NYLS
P P B
60
D40 R Y
~ ~+---~~~~~~==~~~----T
ECCCBDGRWENBOBSMCPFM R L M U A B B B L L B B B H H R B B B B
P P B
3000
D 2000 R Y
HEXACli.OROBU't-ENYlS
~ 1000 +--------=--OO------I»~SI-------T
P P B
D R Y
240
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
OCTACli.OROBPHENYlS
~O+---------------~---------
W 80 +--------oo-J:~I----l:){t-__ooJ::~IOO-J:*---G T
ECCCBDGRWENBOBSMCPFM RLMUABBBLLBBBHHRBBBB
Figure 27d. Concentrations ofhyd.rocarbons (pentachlorobiphenyls. hexachlorobiphenyls. heptachlorobiphenyls. octachlorobiphenyls. nonachlorobiphenyls) in livers collected from all sites.