United States
Environmental Protection
Agency
Office of Water
Criteria & Standards Division
Washington, D.C.
July, 1985
NATIONAL PERSPECTIVE
ON
SEDIMENT QUALITY
REGIONAL AREAS
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NATIONAL PERSPECTIVE ON
SEDIMENT QUALITY
H. Suzanne Bolton
Ronald J. Breteler
Bruce W. Vigon
Judith A. Scan Ion
Sandra L. Clark
May 10, 1985
Prepared for:
Environmental Protection Agency
Criteria and Standards Division
Office of Water Regulations and Standards
Washington, D.C. 20460
Submitted by:
BATTELLE
Washington Environmental Program Office
2030 M Street, N.W.
Washington, D.C. 20036
EPA Contract No.68-01-6986
Battelle Project No.G-8834-0100
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TABLE OF CONTENTS
Page
1.0 OVERVIEW OF SEDIMENT CRITERIA DEVELOPMENT 1.1
1.1 INTRODUCTION ' 1.1
1.2 RESPONSIBILITY OF CRITERIA AND STANDARDS DIVISION
TO DEVELOP CRITERIA IN SUPPORT OF THE CLEAN WATER
ACT (CWA) 1.1
1.3 STATUS OF SEDIMENT CRITERIA DEVELOPMENT 1.2
1.3.1 Background Approach 1.3
1.3.2 Water Quality Criteria Approach 1.3
1.3.3 Sediment-Water Equilibrium Partitioning Approach. . . . 1.4
1.3.4 Sediment-Biota Equilibrium Partitioning Approach. . . . 1.4
1.3.5 Bioassay Approach 1.5
1.4 GENERAL OVERVIEW APPROACH 1.5
2.0 INVENTORY SCOPE AND METHODOLOGY 2.1
2.1 CONTAMINANT CATEGORIZATION AND DERIVATION
OF THRESHOLD VALUES 2.1
2.2 METHODS FOR DATA ACCESSION AND PRESENTATION 2.8
2.2.1 Freshwater Data Base 2.9
2.2.1.1 STORET Chemical Data 2.9
2.2.1.2 Ancillary Chemical and Biological Data .... 2.11
2.2.2 Marine/Estuarine Data Base 2.11
2.2.2.1 STORET Chemical Data 2.13
2.2.2.2 Data Identification 2.13
3.0 RESULTS AND DISCUSSION-FRESHWATER 3.1
3.1 METALS 3.1
3.2 POLYNUCLEAR AROMATIC HYDROCARBONS (PAHs) 3.12
3.3 PHTHALATE ESTERS 3.19
3.4 PESTICIDES 3.23
3.5 CHLORINATED HYDROCARBONS (EXCEPT PESTICIDES) 3.23
3.6 MONOAROMATIC HYDROCARBONS 3.33
3.7 MISCELLANEOUS 3.33
4.0 RESULTS AND DISCUSSION—MARINE/ESTUARINE 4.1
4.1 METALS AND ORGANIC CONTAMINANTS 4.2
4.2 NATIONAL PERSPECTIVE 4.3
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TABLE OF CONTENTS (Continued)
Page
5.0 GEOGRAPHIC DATA 5.1
5.1 OVERVIEW 5.1
5.2 FRESHWATER DATA 5.1
5.2.1 Metals 5.1
5.2.2 Pesticides 5.7
6.0 OBSERVATIONS AND CONCLUSIONS 6.1
6.1 FRESHWATER 6.1
6.2 MARINE/ESTUARINE WATERS 6.2
7.0 REFERENCES 7.1
APPENDIX
TABLE GENERATION AND INTERPRETATION A-l
n
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TABLE OF CONTENTS (Continued)
LIST OF TABLES
Page
Table 2.1. Toxicants Considered/
Threshold Contamination Concentrations 2.2
Table 3.1. Freshwater Data Summary—Metals 3.10
Table 3.2. Freshwater Data Summary—PAHa 3.18
Table 3.3. Freshwater Data Sum-nary—Phtha late Esters 3.22
Table 3.4. Freshwater Data Summary—Pesticides 3.30
Table 4.1. Coastal U.S. Regions Containing Single Pollutants
at Concentrations Exceeding Provisional Sediment
Threshold Values by More than Ten Fold 4.10
Table 4.2. Coastal U.S. Regions Containing Single Pollutants
at Concentrations Exceeding Provisional Sediment
Threshold Values by One- to Three-Foled 4.11
Table 4.3. Coastal U.S. Regions Containing Single Pollutants
at Concentrations Exceeding Provisional Sediment
Threshold Values by One- to Three-Fold 4.12
Table A-l. Freshwater Regions Containing Elevated Sediment
Levels of Copper. A-2
Table A-2. Freshwater Regions Containing Elevated Sediment
Levels of Lead A-5
Table A-3. Freshwater Regions Containing Elevated Sediment
Levels of Mercury A-9
Table A-4. Freshwater Regions Containing Elevated Sediment
Levels of Zinc A-ll
Table A-5. Freshwater Regions Containing Elevated Sediment
Levels f Nickel A-15
Table A-6. Freshwater Regions Containing Elevated Sediment
Levels of Arsenic A-19
Table A-7. Freshwater Regions Containing Elevated Sediment
Levels of Cadmium A-22
m
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TABLE OF CONTENTS (Continued)
Page
Table A-8. Freshwater Regions Containing Elevated Sediment
Levels of Acenaphthalene A-26
Table A-9. Freshwater Regions Containing Elevated Sediment
Levels of Anthracene A-30
Table A-10. Freshwater Regions Containing Elevated Sediment
Levels of Benzo(a)anthracene A-34
Table A-ll. Freshwater Regions Containing Elevated Sediment
Levels of Fluorene A-38
Table A-12. Freshwater Regions Containing Elevated Sediment
Levels of Phenanthrene A-42
Table A-13. Freshwater Regions Containing Elevated Sediment
Levels of Diethylphthalate A-46
Table A-14. Freshwater Regions Containing Elevated Sediment
Levels of Dimethylphthalate A-50
Table A-15. Freshwater Regions Containing Elevated Sediment
Levels of Aldrin A-54
Table A-16. Freshwater Regions Containing Elevated Sediment
Levels of Chlordane A-58
Table A-17. Freshwater Regions Containing Elevated Sediment
Levels of DDT A-62
Table A-18. Freshwater Regions Containing Elevated Sediment
Levels of Heptachlor A-66
Table A-19. Freshwater Regions Containing Elevated Sediment
Levels of Lindane A-70
Table A-20. Freshwater Regions Containing Elevated Sediment
Levels of Toxaphene A-73
Table A-21. Freshwater Regions Containing Elevated Sediment
Levels of PCB A-76
Table A-22. Freshwater Regions Containign Elevated Sediment
Levels of Cyanide A-81
iv
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TABLE OF CONTENTS (Continued)
Page
LIST OF FIGURES
Figure 2.1. Percentage Distribution of Individual
Chemicals Among Chemical Categories 2.5
Figure 2.2. Division of National Maps into Regional Areas 2.11
Figure 3.1. Cumulative Frequency Plot for Copper 3.2
Figure 3.2. Cumulative Frequency Plot for Lead 3.3
Figure 3.3. Cumulative Frequency Plot for Mercury 3.4
Figure 3.4. Cumulative Frequency Plot for Zinc 3.5
Figure 3.5. Cumulative Frequency Plot for Nickel 3.6
Figure 3.6. Cumulative Frequency Plot for Arsenic 3.7
Figure 3.7. Cumulative Frequency Plot for Cadmium 3.8
Figure 3.8. Cumulative Frequency Plot for Acenaphthalene 3.13
Figure 3.9. Cumulative Frequency Plot for Antnracene 3.14
Figure 3.10. Cumulative Frequency Plot for Benzo(a)Anthracene. 3.15
Figure 3.11. Cumulative Frequency Plot for Fluorene 3.16
Figure 3.12. Cumulative Frequency Plot for Phenanthrene 3.17
Figure 3.13. Cumulative Frequency Plot for Diethylphthalate 3.20
Figure 3.14. Cumulative Frequency Plot for Oiraethylphthalate 3.21
Figure 3.15. Cumulative Frequency Plot for Aldrin 3.24
Figure 3.16. Cumulative Frequency Plot for Chlordane 3.25
Figure 3.17. Cumulative Frequency Plot for DDT 3.26
Figure 3.18. Cumulative Frequency Plot for Heptachlor 3.27
Figure 3.19. Cumulative Frequency Plot for Lindane 3.28
Figure 3.20. Cumulative Frequency Plot for Toxaphene .......... 3.29
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TABLE OF CONTENTS (Continued)
Page
Figure 3.21. Cumulative Frequency Plot for PCB (Aroclor 1016) 3.32
Figure 3.22. Cumulative Frequency Plot for Cyanide 3.34
Figure 4.1. Aromatic and Polynuclear Aromatic Hydrocarbons 4.4
Figure 4.2. Pesticides and Other Chlorinated Hydrocarbons 4.5
Figure 4.3. Metals and Phthalates 4-8
Figure 5.1. National Map Classification Levels for Metals 5.2
Figure 5.2. Region I Calssification Levels for Metals 5.3
Figure 5.3. Regions II, III Classification Levels for Metals 5.4
Figure 5.4. Region V Classification Levels for Metals 5.5
Figure 5.5. Region IV, VI Classification Levels for Metals 5.6
Figure 5.6. Region VII, VIII Classification Levels for Metals 5.8
Figure 5.7. Region X Classification Levels for Metals 5.9
Figure 5.8. Region IX Classification Levels for Metals 5.10
Figure 5.9. National Map Classification for Pesticides 5.11
Figure 5.10. Regions II, III Classification Levels for Pesticides. . . . 5.12
Figure 5.11. Region I Classification Levels for Pesticides 5.13
Figure 5.12. Region V Classification Levels for Pesticides 5.14
Figure 5.13. Regions IV, VI Classification Levels for Pesticides .... 5.15
Figure 5.14. Regtons VII, VIII Classification Levels for Pesticides. . . 5.16
Figure 5.15. Region X Classification Levels for Pesticides 5.18
Figure 5.16. Region IX Classification Levels for Pesticides 5.19
Figure 5.17. National Map Classification Levels for Phthalates,
Cyanide, PCB's, Total PAH's 5.20
Figure 5.18. Region I Classification Levels for Phthalates,
Cyanide, PCB's, Total PAH's *-*L
Figure 5.19. Regions II, III Classification Levels for Phthalates,
Cyanide, PCB's, Total PAH's 5-"
VI
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TABLE OF CONTENTS (Continued)
Page
Figure 5.20. Region V Classification Levels for Phthalates
Cyanide, PCB's, Total PAH's ........ . ....... 5>23
Figure 5.21. -yUsslflcon LeveU for mha,ates,
5.22.
for
••
Figure 5.23. Region X Classification Levels for Phthalates
Cai ' ' '
Cyanide, PCB's, Total PAH's
Figure 5.24. Region IX Classification Levels for Phthalates
Cyanide, PCB's, Total PAH's ......... .' ...... 5<27
vii
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1.0 OVERVIEW OF SEDIMENT CRITERIA DEVELOPMENT
1.1 INTRODUCTION
The purpose of this document is to provide an overview of the quality of
freshwater and marine/estuarine sediments on a national basis and to provide
assistance in focusing sediment criteria development efforts. It was
originally developed for use by participants in an EPA-sponsored Sediment
Criteria Development Workshop held on November 28-30, 1984. The primary
sources of data for this overview were the EPA Storage and Retrieval (STORET)
system computer file, the open literature and reports of limited availability
produced by state and federal agencies.
1.2 RESPONSIBILITY OF THE CRITERIA AND STANDARDS DIVISION
TO DEVELOP CRITERIA IN SUPPORT OF THE CLEAN WATER ACT (CWA)
The Criteria and Standards Division (CSO) of the Environmental Protection
Agency (EPA) develops and revises criteria, regulations, standards and
guidelines in support of the mandates of the CWA. The CSD has published water
quality criteria for 65 priority pollutants and pollutant categories. These
criteria are based on an assessment of water column pollutant concentration
which, if not exceeded, will protect designated uses of a water body and
95 percent of the aquatic life from adverse effect. The EPA recognizes,
however that, while ambient water quality criteria are an important component
in assuring the health of an aquatic environment, contaminated sediments may
be responsible for significant adverse effects on certain aquatic organisms in
the presence of acceptable ambient water quality criteria.
EPA has authority1 to pursue the development of sediment criteria in
streams, lakes, and other "waters of the United States" under sections 104 and
304(a)(l) and (2) of the CWA as follows:
(1) Section 104 authorizes the Administrator to establish national
programs for the prevention, reduction and elimination of pollution
by conducting and promoting "the coordination and acceleration of
lEPA Memorandum, Catherine A. Winer to David K. Sabock, October 25, 1984.
1.1
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research, investigations, experiments, training, demonstrations,
surveys, and studies relating to the causes, effects, and extent,
prevention, reduction, and elimination of pollution" and by
publishing relevant information. Section 104(n)(l) specifically
provides for the study of the effects of pollution, including
sedimentation, in estuaries on aquatic life.
(2) Section 304(a)(l) directs the Administrator to develop and publish
criteria for water quality accurately reflecting the latest
scientific knowledge "on the kind and extent of all identifiable
effects on health and welfare including, but not limited to,
plankton, fish, shellfish, wildlife, plant life, shorelines,
beaches, aesthetics, and recreation which may be expected from the
presence of pollutants in any body of water, including groundwater
...on the concentration and dispersal of pollutants, or their
byproducts ...on the effects of pollutants on biological community
diversity, productivity and stability, including information of the
factors affecting ...rates of organic and inorganic sedimentation
for varying types of receiving waters."
(3) Section 304(a)(2) directs the Administrator to develop and publish
information on, among other things, "the factors necessary for the
protection and propagation of shellfish, fish, and wildlife for
classes and categories of receiving waters ..."
The Office of the General Counsel (OGC) sees no difficulty in
interpreting the phrase "pollutants in any body of water" to include
pollutants in the substrate bed of those waters, where the pollutants may
affect aquatic life. OGC recognizes a regulatory role in developing sediment
criteria where the Administrator finds that including sediment criteria is
necessary to meet the requirements of the Act to protect designated water
uses. The office contends, furthermore, that "to the extent that sediment
criteria could be developed which addressed the concerns of the section
404(b)(l) Guidelines (for discharge of dredged or fill material under the
Clean Water Act) or ocean dumping criteria (under the Marine Protection,
Research, and Sanctuaries Act), they would also be incorporated into those
regulations."
1.3 STATUS OF SEDIMENT CRITERIA DEVELOPMENT
Sediment criteria development has evolved under the auspices of several
institutions and regulatory agencies. The following section provides a summary
of those approaches which are under consideration by regulatory agencies or
1.2
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otherwise appear promising avenues to lead to formulation of defensible
criteria. Other approaches not specifically enumerated in this document were
introduced independently by workshop participants and received equal
consideration during the course of the workshop. A summary document of the
workshop proceedings has been prepared for the EPA (Battelle, Columbus
Laboratories, 1985). More detailed discussions of the following approaches
can be obtained from the "Background and Review Document on the Development of
Sediment Criteria," (JRB Associates, 1984a) distributed to workshop
participants on November 2, 1984.
1.3.1 Background Approach
The Background Approach establishes criteria on a relative basis.
Concentration of a chemical in sediments of a particular site is compared to
concentrations of the same chemical from reference sites where levels of the
chemical of concern in the sediments are deemed to be acceptable. In
determining suitable reference areas, consideration of assimilative capacity
based on toxicological data is implied. The difficulties inherent in
developing a technically and legally defensible method of selecting a
"suitable" reference area or determining an "acceptable" level place
limitations on the use of this approach. A modification of this approach has
been applied to a dredge site designation in EPA Region X.
1.3.2 Water Quality Criteria Approach
The Water Quality Criteria Approach has been developed by EPA Region VI.
The approach reTies upon existing Water Quality Criteria data to assess
acceptable levels of various chemicals in interstitial waters. Toxicological
data used to establish the Mater Quality Criteria, it should be noted, were
derived from sediment-free bioassays primarily with nektonic organisms. The
assumption, then, is made at the onset, that ingestion of or direct contact
with sediment does not increase the body burden of chemicals in benthic
1.3
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organisms above those obtainable strictly by absorption from surrounding
waters. The methods for obtaining and analyzing interstitial water are still
under development.
1.3.3 Sediment-Water Equilibrium Partitioning Approach
The Sediment-Water Equilibrium Partitioning Approach also relies upon the
toxicological data available from established Water Quality Criteria. The
approach is based on the assumption that the distribution of various chemicals
among different compartments in the sediment is controlled by a continuous
exchange among sediment, infauna, interstitial and overlying waters. The
constants relating these concentrations at equilibrium are referred to as
partition coefficients. Compound-specific partition coefficients are
determined and used to predict the distribution of the compound between
sediment and interstitial water. Because of the influence of organic carbon
in the sediment on the distribution of many chemicals among phases, partition
coefficients often are expressed in terms of organic carbon content of the
sediment. Uncertainties about the effects of site-specific variations in
physical/chemical factors on trace metal and organic chemical distributions
among phases complicate quantification of these chemical distributions for use
in defensible sediment criteria.
1.3.4 Sediment-Biota Equilibrium Partitioning Approach
Sediment quality criteria developed by the Sediment-Biota Equilibrium
Partitioning approach establish a concentration of a chemical in the sediment
below which benthic organisms would be unable to attain body burden of the
chemical in excess of a permissible limit. Extensive body burden-effect data
are necessary to establish permissible limits and both water-biota and biota-
sediment partitioning processes must be quantified. The EPA/ERL Narragansett
and the Corps of Engineers have advocated this approach for the assessment of
hydrophobic or neutral organic compounds. The Food and Drug Administration
has set action level limits for several pollutant chemicals in the edible
tissues of commercial fisheries species.
1.4
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1.3.5 Bioassay Approach
The Bioassay Approach establishes criteria based on dose-response
relationships developed by exposing organisms to sediments containing known
concentrations of chemicals and measuring biological parameters including
mortality, sublethal effects and bioconcentration. This approach has the
capacity to assess overall sources and rates of chemical uptake by organisms
and has been used as a component of the assessment process for both coastal
dredge and fill permits, ocean dumping permits, and for National Pollution
Discharge Elimination System (NPDES) permits for offshore oil and gas drilling
discharges.
1.4 GENERAL OVERVIEW APPROACH
This survey is, by the necessities of time and resource limitations, not
intended as an exhaustive review of existing data sets. However, the text does
provide an overview of the national sediment quality status and does
highlight, to some extent, the weaknesses and strengths of the data and
criteria used to characterize the quality of sediments. Both this document and
the workshop summary document identify the need for and direction of a more
extensive literature review.
Due to the differences in data quality and data availability for
sediments in both freshwater and marine/estuarine sites, information has been
presented in formats that best fit each data set. The STORET system provided
extensive freshwater sediment chemistry data but little correlating data on
biological effects. The marine data were less readily abundant and chiefly
resulted from an arduous search of the available literature rather than of
computer files. This latter search supplied more perspective on
biota/sediment interactions and effects.
To standardize the inventory of the literature/computer searches, a
tentative chemical concentration ranking system was established. Where
available, numerical criteria specified by EPA or other federal entities were
1.5
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used to establish a threshold level of the chemical in sediment. In the
absence of established sediment quality criteria, preliminary threshold
concentrations were used to assess the data. The derivation, shortcomings,
and advantages of the use of these preliminary threshold concentrations are
dnscussed in appropriate sections of this document, summarized in one section,
Numerical ranges which represent multiples of the appropriate threshold
concentration were arbitrarily designated as follows:
• Level 1-sediment concentrations less than the threshold value
• Level 2—1 to 3 times the threshold value
t Level 3—3 to 10 times the threshold value
• Level 4--greater than 10 times the threshold value.
1.6
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2.0 INVENTORY SCOPE AND METHODOLOGY
The purpose of this effort was to compile a national inventory of both
marine and freshwater data that indicate the concentration of various
chemicals in the sediment. A total of 48 chemical contaminants were initially
identified by the EPA Office of Water Regulations and Standards (OWRS) and
Battelle. These 48 chemicals represented seven categories of major pollutant
chemical classes. Existing data sources were then evaluated and used to
provide a broad-based geographic perspective on the level of these chemicals
in sediments throughout the United States.
2.1 CONTAMINANT CATEGORIZATION AND DERIVATION OF THRESHOLD VALUES
The chemicals shown in Table 2.1 represent a diverse group of naturally
occurring and anthropogenic materials indicative of compounds that have been
of increasing environmental concern. This listing is not intended to be
exhaustive, but rather is illustrative of the types of chemical data available
for sediments. The percent distribution of the seven contaminant categories
is summarized in Figure 2.1.
The seven chemical categories identified in this document are:
• polynuclear aromatic hydrocarbons
• pesticides
• chlorinated hydrocarbons
• mononuclear aromatic hydrocarbons
• phthalate esters
0 metals
• miscellaneous
Table 2.1 also lists the threshold concentrations used to judge
differences in the levels of various chemicals in sediments. The majority of
these values was calculated using the methodology of the Sediment-Water
2.1
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TABLE 2.1. TOXICANTS CONSIDERED/THRESHOLD CONTAMINATION CONCENTRATIONS(a)
(DENOTED ON A DRY WEIGHT BASIS)
(I) Polynuclear Aromatic Hydrocarbons (PAH)
mg/kg
benzo(a)pyrene 1800
naphthalene 42
phenanthrene 56
chrysene 460
pyrene , 198
fluorene 28
acenaphthene 66
anthracene 44
benzo(a)anthracene 220
acenaphthalene 24
indeno(l,2,3-CD)pyrene 24,000
benzo(k)fluoranthene 5,000
(II) Pesticides
lindane
ODD
DDE
aldrin
Isophorone
DDT
chlordane(b)
toxaphene(b)
heptachlor
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(Ill) Chlorinated Hydrocarbons (Except Pesticides)
hexachloroethane
hexachlorobu tadi ene
tetrachloroethylene
trichloroethylene
dichlorobenzene
methyl chloride
methylene chloride
PCBs(c)
mg/kq
14.4
1.28
1.8
6.4
2.8
1.92
2
0.28
(IV) Monoaromatic Hydrocarbons
toluene
benzene
ethyl benzene
nitrobenzene
dinitrotoluene
mg/kg
10
1.36
5.6
6.6
0.88
(V) Phthalates
butylbenzyl phthalate
di-N-butylphthalate
diethylphthalate
dimethylphthalate
nig/kg
220
2,000
1.28
1.96
2.3
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(VI) Metals
arsenic
cadmium
copper
lead
mercury(d)
zinc
chromium(e)
nickel(e)
mq/kq
33
31
136
132
0.8
760
25
20
(VII) Miscellaneous
cyanide(d)
mq/kq
0.1
(a)
(b)
(c)
(d)
(e)
Threshold concentrations are those determined by EPA/OWRS unless
otherwise stated; criteria for organic contaminants are calculated on the
basis of 4 percent organic carbon content of sediment.
U.S. Geological Survey, sediment alert levels.
Based on criterion for hexachlorobiphenyl.
The value of 0.8 was not corrected for organic carbon. Correction of
this value would have resulted in a mercury concentration of 0.03, which
is considerably lower than the concentration of this metal in most
sediments.
EPA Region V guidelines
contaminated sediments.
for designating contaminated versus non-
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Phthalates (8.5%) Cyanide (2.1%)
Monoaromatic Hydrocarbons
(10.6%)
ro
ui
Metals (17.0%)
Chlorinated Hydrocarbons (17.0%)
Polyaromatic Hydrocarbons
(25.5%)
Pesticides (19.1%)
FIGURE 2.1. PERCENTAGE DISTRIBUTION OF INDIVIDUAL CHEMICALS AMONG CHEMICAL CATEGORIES
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Equilibrium Partitioning Approach (Section 1.3.3 of this report) discussed in
"Background and Review Document on the Development of Sediment Criteria" (JRB
Associates, 1984a) and/or they were derived from the EPA document "Development
and testing of the sediment-water equilibrium partitioning approach," (JRB
Associates, 1984b). It is not the purpose of this overview to judge the
adequacy of this approach for setting target concentrations vis-a-vis other
alternatives but rather to assume that the values are useful and to apply them
to the assessment of the ambient chemical measurements as described in
Section 2.2.1.
In this approach, the assumption is made that the distribution of a
chemical between the organic carbon phase of the sediment and the soluble phase
in interstitial water in equilibrium with the solid phase is described by the
organic carbon-water partition coefficient (Koc) for the chemical. If the
water quality criterion value for the chemical is taken to be the maximum
acceptable concentration of the chemical in solution in the interstitial water,
then the threshold concentration of the chemical in the bulk sediment is
calculated based on the sediment organic carbon-normalized Koc for the
chemical.
The methodology for derivation of criteria using this approach is
presented in the aforementioned document and was discussed during the
workshop. The advantages and disadvantages of this methodology are listed
below to permit the reader to form specific judgments regarding relevancy to
biological thresholds.
Advantages
• The large toxicological data base incorporated in the EPA water
quality criteria is directly utilized for sediment quality criteria.
Sediment quality criteria can be readily developed for those compounds
for which EPA water quality criteria are available and for those
compounds which are assigned water quality criteria in the future.
• "First-cut" criteria are available that can then be verified by future
field and laboratory studies.
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Disadvantages
t No sediment criteria can be established for those compounds for which
EPA water quality criteria have not been developed.
• The approach does not account for any increase in contaminant burden
which may result from ingestion of or direct body contact with
contaminated sediments above that which is attained simply by
absorption from the interstitial/overlying water.
• The assumption of contaminant equilibrium between sediment and
interstitial water, inherent in the approach, may not always hold in
natural systems (Prahl and Carpenter, 1983).
• Criteria developed for trace metals have a very high associated
uncertainty, making their regulatory application difficult.
• The method does not consider the effect of interstitial water
dissolved organic carbon on partitioning and bioavailability of highly
hydrophobic chemicals.
This approach does, however, allow a numerical "threshold" to be
established against which available monitoring data can be compared. The non-
judgmental use of this approach allows the distribution of the data set into
percentiles "above" and "below" the threshold even though one might question
the significance of the results relative to the observed integrity or lack of
integrity of biological communities.
Threshold values derived from the sediment-water partitioning approach
are based on the organic carbon content of the particular sediment. These
values were adjusted to a whole sediment basis on the assumption that an
average sediment contains 4 percent total organic carbon. Furthermore, the
values are compared to the monitoring data on a dry weight equivalent basis.
For several chemicals, where both acute and chronic water quality criterion
values are available, the chronic values were selected for this exercise. The
chemicals for which chronic values have been used are noted in the text.
The 4 percent value for average TOC is high for many freshwater and
certainly most marine/estuarine sediments. A more typical value may be in the
1-2 percent range. If 2 percent TOC had been chosen for calculation of TOC-
normalized sediment threshold concentrations for chemicals, the values in
2.7
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Table 2.1 would have been half those listed. More sites would have been
identified with sediment chemical concentrations above the threshold values.
However, a greater source of uncertainty in generating sediment threshold
values using this method is the wide variation in published K0c values for
each chemical. Koc values calculated for the same chemical by different
investigators and/or under different physical/chemical parameter regimes may
differ by several orders of magnitude. For instance, the threshold value for
zinc originally was calculated as 19,000 + 38,000 mg/kg, based on the
uncertainty of the Koc value for zinc. Because, TOC-based sediment
normalization theory has been more completely validated for non-polar organic
compounds than for heavy metals and polar organics, threshold values for non-
polar organics (chemical classes I-V in Table 2.1) probably are more reliable
than those for metals and cyanide.
Threshold values for six of the chemicals were not available from EPA
sediment criterion developmental documents. Values for three pesticides,
chlordane, toxaphene and heptachlor, were obtained from alert levels
established by the U.S. Geological Survey. The establishment of the values of
0.02 mg/kg for these constituents was based on a decision to examine in
greater detail 15-20 percent of the samples analyzed from heavily contaminated
areas (JRB Associates, 1984b). No toxicological implications were intended.
Freshwater threshold values for two metals, chromium and nickel, and for
cyanide were obtained from guidelines developed by EPA Region V. As in the
case of the Geological Survey alert levels, these concentrations were intended
for the classification of polluted sediments and are of limited applicability.
Additional test data are required in order to judge the significance of the
observed sediment contamination levels.
2.2 METHODS FOR DATA ACCESSION AND PRESENTATION
The methods used to evaluate the level of various chemicals in sediments
of freshwaters, marine waters and estuaries was consistent to the extent
2.8
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that the data search included the same chemicals and selected threshold
values. The exception to this was chromium for which only marine data were
available.
To compare the monitoring data, the concentrations were divided for
convenience into four subranges-designated as "Level 1" (less than the
threshold value), "Level 2 (1-3 times the threshold value), "Level 3" (3-10
times the threshold value), and "Level 4" (greater than 10 times the threshold
value).
Additional information was compiled, where available, to place this
information in perspective. Because of the differences in the amount of data
available and the capability to computer process only part of the data base,
the detailed methodologies for processing and interpreting the freshwater and
marine/estuarine data are described in separate sections.
2.2.1 Freshwater Data Base
A very large data base was available for evaluation of contamination of
sediments in streams, rivers, lakes and reservoirs. The EPA Storage and
Retrieval (STORET) System was the primary source of data for this effort. Of
the group of 48 chemicals identified initially, data on 22 were obtained from
the STORET system and over 255,000 data records were processed. No attempt
was made to judge the quality of these data or the accuracy and precision of
the analytical techniques used to obtain them. Additional descriptive
information on the site-specific biological implications of some parameters
was obtained from appropriate journals and reports.
2.2.1.1 STORET Chemical Data
To gain some appreciation of the distributions of sediment chemical
concentration data and to allow comparison of the various classification
levels of the measured ambient concentrations, a graphical plot of the decimal
2.9
-------
log of concentration versus cumulative frequency was prepared for each
chemical. For plotting purposes, data points recorded as zero In the data
base were assumed to represent values below the detection limit of the
analytical technique. The percentage of such values was determined for each
chemical in order to judge the proximity of the threshold concentration to the
analytical limits.
As described previously, the concentration range above the Level 1 value
was subdivided into several subranges. The statistical implications of setting
a criterion at any of these points were compared against the national STORET
data base. Most of the cumulative frequency plots contain between 5,000 and
20,000 data points for each chemical so the plots are described by smooth
curves.
To provide additional perspective on the distribution of various
chemicals in the nation's freshwater sediments, the median, 90th and 95th
percent!le concentrations were identified on the cumulative frequency plots.
The threshold concentration values can be readily compared to these percentile
points. A comparison of the data was also made against other proposed
sediment quality criteria. This comparison permits observations to be made
about the regulatory consequences of setting other threshold levels.
While the cumulative frequency plots provide a perspective of the
percentage of sample sites that exceed the threshold, these plots give no
indication of geographic distribution. National and regional maps have been
prepared to illustrate these distributions.
The geographic distribution of sites with elevated concentrations of
specific chemicals in sediments was evaluated by arranging the 200 highest
concentration measurements for each chemical from highest to lowest. In cases
where more than one analysis had been performed at a single site (as
determined from identical station numbers), the arithmetic mean concentration
was tabulated. When adjacent stations were reported that differed in location
by only a few seconds of latitude or longitude, these data were judged to
2.10
-------
represent the same site area. For a given site area, only the highest mean
concentration was used for the maps. Tabular summaries show all of the
individual sites comprising an area and are contained in the Appendix
(Tables A-l to A-22).
The mapped data are shown at two scales—national and regional. National
maps for each of three groups of chemicals were developed to provide an
overview of the distribution of high concentration sites around the country.
This scale map is also useful to examine areas having potential problems
because of the occurence of multiple chemicals. The national maps were
further subdivided into regional maps on the basis of EPA Regions
(Figure 2.2). The larger scale of these maps allows viewing the data for
specific sites at greater resolution. The data symbols were placed on the maps
at approximately the correct locations using longitude and latitude
coordinates. Where multiple chemicals are present at the same place, the
symbols were displaced slightly to improve the readability of the map.
2.2.1.2 Ancillary Chemical and Biological Data
To aid in the interpretation of the large amount of STORET data, the open
literature was examined for general and site specific investigations of
correlations between sediment pollutant burden and benthic community
structure. The large number of parameters, the lack of case study data for
many sites and chemicals, and the constraints of time precluded this activity
from being much more than illustrative of the scope of the potential problem.
This information is discussed after the presentation of the STORET data for
metals, PCBs, -and PAHs. No correlative data were found for the other
chemicals.
2.2.2 Marine/Estuarine Data Base
Concentrations of various chemicals in marine and estuarine sediments
were obtained from the published literature and from some literature with
limited distributions. An additional set of unreferenced data points was
derived from the STORET data file. All sediment concentration data were
2.11
-------
I
M
M
FIGURE 2.2. DIVISION OF NATIONAL MAP
INTO REGIONAL AREAS
-------
entered on an IBM personal computer, and the data set was sorted to facilitate
data presentation. While the data base presented in this report is not
complete or even exhaustive, it does present a preliminary national
perspective of the sediment quality status of marine and estuarine sites
Marine/estuarine data were placed on the national and regional maps in the
same manner as the fresh water data.
2.2.2.1 STORET Chemical Data
Marine/estuarine STORET data were limited to median concentrations of
various chemicals. No ranges of concentration were given and the data base
was insufficient to manipulate data in the manner described for the freshwater
data sets.
2.2.2.2 Data Identification
Due to time contraints, the literature search was limited to readily
available journal articles and publications in the open literature, and
included numerous reports from state and federal agencies.
Many additional data bases and sources of information were identified but
were not included in this report due to the lead time necessary to access
files. Notable among these data bases are: the Ocean Pollution Data and
Information Data Network (OPDIN), and the National Oceanographic Data Center
(NODC) Marine Toxic Substances and Pollutants Data File. Both systems were
established by the National Oceanic and Atmospheric Administration (NOAA) to
improve dissemination of data and information resulting from ocean pollution
programs conducted or sponsored by the U.S.federal government. NODC provides a
substantial quantity of data on toxic substances and pollutants in the marine
environment. These data sets are generally limited to a few specific sites,
i.e., Puget Sound, Gulf of Mexico, the New York Bight region, and Alaska. Both
systems have automated data retrieval systems. Another important source of
data for a more detailed review is an extensive computerized inventory of
long-term monitoring programs prepared by Battelle for NOAA's Ocean
2.13
-------
Assessments Division. This inventory includes marine pollution monitoring
programs conducted by private organizations, state, and federal agencies for
durations of at least two years. The inventory contains names and addresses,
including phone numbers, of cognizant individuals, who may be approached with
a request to submit published or unpublished reports which otherwise might be
unavailable or difficult to obtain.
2.14
-------
3.0 RESULTS AND DISCUSSION-FRESHWATER
The following sections are organized according to the chemical groups
identified in Table 2.1. Plots of cumulative frequency versus concentration in
sediments are presented for each chemical. Threshold, 3X and 10X threshold
concentrations as well as 50, 90, and 95 percent frequency concentrations are
included in each graph. To further aid in the comparison of chemicals to
their respective threshold values, a summary table is provided within each
section. Because the threshold values obtained via the sediment water
partitioning approach (JRB Associates, 1984a) are tentative, alternative
criteria are also shown and compared to the data. Additional comparative
commentary is included to place these values in perspective, but the extent of
this information is limited due to the nature of this study.
As described in Section 2, organic carbon based threshold values were
determined for each of the chemical contaminants via the sediment-water
partition coefficient approach outlined in the document, "Background and
Review Document on the Development of Sediment Criteria," and then converted
to a whole sediment basis on the assumption of a typical organic-carbon level
of 4 percent.
3.1 METALS
STORET data for metal concentrations in sediments were quite extensive.
With the exception of copper, the data base contained between 5,000 and 20,000
measurements for each metal. The copper data were restricted to wet weight
determinations-due to limitations in the STORET data transfer. The total
STORET data base size for dry weight copper measurements is comparable to that
for the other metals so that future evaluation of the STORET data base could
utilize a more extensive data set.
The log concentration in sediments versus cumulative frequency plots for
copper, lead, mercury, zinc, nickel, arsenic and cadmium are shown in Figures
3.1 to 3.7, respectively. These figures typically exhibit a sigmoid (S-)
3.1
-------
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LEGEND: A = 1 DBS. B = 2 DBS. ETC.
12 OBS HIDDEN
FIGURE 3.1 CUMULATIVE FREQUENCY PLOT FOR COPPER
-------
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FIGURE 3.2 CUMUWTIVE FREQUENCY PLOT FOR LEAD
-------
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FIGURE 3.3 CUMULATIVE FREQUENCY PLOT FOR MERCURY
-------
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10X THRESHOLD VALUE
3161
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CUMULATIVE FREQUENCY (IN PERCENT)
LIGEND: A = 1 UBS. B • 2 OBS. ETC
19820 OBS HIDDEN
FIGURE 3.4 CUMULATIVE FREQUENCY PLOT FOR ZINC
-------
GO
3161
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~ 315
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LEGEND. A - 1 OBS, B =- 2 OBS. ETC.
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FIGURE 3.5 CUMULATIVE FREQUENCY PLOT FOR NICKEL
-------
316
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-------
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FIGURE 3.7 CUMULATIVE FREQUENCY PLOT FOR CADMIUM
-------
shape on this type of plot. When transformed to a probability scale on the x-
axis, the plots are nearly straight lines indicating log-normally distributed
data. Table 3.1 provides a comparative summary of the data. The most striking
aspect of this summary is the large percentage of data in the Level 1 range
(less than threshold value). Irrespective of whether the preliminary
thresholds concentrations derived from chemical partitioning represent valid
and defensible biotic thresholds, the implication for a regulatory strategy
conditional upon these levels are that very few areas would be considered
sufficiently contaminated to require remedial action.
For each of the metals, a very small percentage of the data appears in
Level 4 (more than ten times threshold value). A review of the readily
available open literature, however, seems to indicate a need to carefully
examine the rationale for establishing these threshold levels. For example,
in a study of Portage Lake, environmental degradation was noted in an area
where sediment metals concentrations averaged 589 mg/kg (Malueg, 1984). Also
in the Little Grizzly Creek System in California, Malueg (1984) noted that
ephemeropterans (mayflies) and plecopterans (stoneflies) were rare or absent
from a location containing 2200 mg/kg of copper.
Bioconcentration may be another area of concern when evaluating the
threshold values. Leland et al. (1978) describes a rural stream located in
Illinois, which had low levels of cadmium and lead in the water but
substantially elevated levels in the sediments and organisms. Leland states
that "concentration factors increased in the order fish < sediment < aquatic
insects < snails." Schuytema (1984) reports that although sediment-sorbed
cadmium was observed to have little effect on Daphnia magna mortality, it may
have a pronounced effect on benthic organisms that ingest large quantities of
sediment relative to water intake.
For each of these metals, alternative threshold values have been
suggested by EPA Region V and the USGS. In the subsequent discussion, the more
conservative alternative threshold is the EPA value; the less conservative,
the USGS sediment alert levels. For copper, 25 mg/kg and 2000 mg/kg represent
the range of these other suggested threshold values. With a threshold value
3.9
-------
TABLE 3.1. FRESHWATER DATA SUMMARY-METALS
Cu
Pb
Hg*
Zn
Ni
w As
o Cd
Threshold
Concentration
(mg/kg)
136
132
0.8
760
20
33
31
Total Number
of Locations
300
32,024
24,989
23,382
15,690
16,275
20,297
Percent in
' Level 1
99.9
92.5
92
96
57
94
97.5
Percent in
Level 2
none
5.0
4.0
1.5
32
3.5
1.0
Percent in
Level 3
0.1
1.5
2.0
1.5
7.0
2.4
1.0
Percent in
Level 4
none
1.0
2.0
1.0
3.0
0.1
0.5
Median
Concentration
(mg/kg)
4.0
16
< 1.0
41
13
4.0
1.0
95th Percent! le
Concentration
(mg/kg)
32
199
1.0
379
99
39
12
Max imum
Concentration
(mg/kg)
493
19,000
40,000
50,800
6,000
6,200
8,230
*The mercury and values were not corrected for organic carbon content.
-------
of 2000 mg/kg, all the data would be classified as Level 1. A total of 8
percent of the STORET data appear in the Level 2 range with the lower
threshold of 25 mg/kg.
For lead, 40 mg/kg and 500 mg/kg are the suggested threshold range
endpoints. With a threshold level of 40 mg/kg, 21 percent of the data points
were distributed in Levels 2, 3, and 4. With a threshold value of 500 mg/kg,
1 percent of the data were so distributed.
The alternate criteria for mercury span the range between 1 mg/kg and 20
mg/kg. At 1 mg/kg, 6 percent of the data points were above this designated
threshold value. At 20 mg/kg, 2 percent of the sediments exceeded Level 1.
For zinc, 90 mg/kg and 5000 mg/kg were the limits of suggested threshold
values. At 90 mg/kg, 31 percent of the sediments would be designated as
greater than Level 1. At 5000 mg/kg, less than 0.01 percent of the data are
above level 1.
The only alternative concentration for nickel was 2,000 mg/kg. At 2000
mg/kg, less than 0.2 percent of the data would be classified in a level other
than Level 1.
For arsenic, 3 mg/kg and 200 mg/kg are two suggested threshold values.
At 3 mg/kg, 62 percent of the sediments would be classified in Levels 2, 3,
and 4. This percentage represents a significant number of sites and is
suggestive of a definite need to evaluate this alternative threshold. At 200
mg/kg, only 3 percent of the data would be distributed in the higher three
levels.
For cadmium, 6 mg/kg and 20 mg/kg were the two suggested threshold
values. At 6 mg/kg, 26 percent of the data would fall in levels greater than
one. At 20 mg/kg, 4 percent of the data would be classified in Levels 2, 3,
and 4.
3.11
-------
In general, for the metals examined, the vast majority of the data is
classified in Level 1. The data in the upper three levels are distributed
rather evenly with a slight increase in Level 2. Application of the lower
range of alternative criteria would result in greater numbers of sites
requiring regulatory scrutiny. As stated in Section 2.2, no freshwater STORET
data were acquired for chromium, although such measurements are available
within STORET.
3.2 POLYNUCLEAR AROMATIC HYDROCARBONS (PAHs)
STORET data for PAH concentration in sediments were judged to be adequate
for assessment in terms of number of data points. The data base for each PAH
typically consisted of approximately 400 measurements with the exception of
the benzo(a)anthracene data base which consisted of approximately 1,500
measurements. Although it is the most-frequently analyzed PAH in water and
sediments, benzo(a)pyrene is not here in the evaluation of freshwater
sediments due to difficulties in accessing the appropriate data for this
compound from STORET.
The log concentration versus cumulative frequency plots for
acenaphthalene, anthracene, benzo(a)anthracene, fluorene, and phenanthrene are
shown in Figures 3.8 to 3.12, respectively. The plots reflect the ubiquitous
nature of PAHs in that a comparatively low percentage was below detection. A
comparative summary of the data is provided in Table 3.2. The most striking
aspect of this summary is that the vast majority of the data is classified in
Level 1. The threshold values used to make this classification, however, must
be proven defensible and biologically relevant. Median concentrations, the
highest concentrations, and the concentrations below which 95 percent of the
data falls are "quite similar for all the PAHs shown in Table 3.2 with the
exception of benzo(a)anthracene which exhibits even lower values.
PAHs are of environmental concern due to the carcinogenic and/or
mutagenic properties of some of them. High incidences of tumors in carp and
goldfish of the Lake Erie tributaries have been correlated with high
concentrations of PAHs in sediment (Black et al.t 1980). In laboratory
studies, PAHs have induced tumors in fish as well as caused the production of
carcinogenic metabolites (Neff, 1979). A high incidence of tumors was observed
in Great Lakes fish that feed primarily on the bottom (Sonstegard, 1977).
3.12
-------
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7" 7!» 80 85 90
LEGEND- A = 1 UBS. B = 2 DBS. ETC
85 OBS HIDDEN
FIGURE 3.8 CUHJLATIVE FREQUENCY PLOT FOR ACENAPHTHALENE
-------
31.622
9.999
THRESHOLD VALUE ' A* mq/fcg
3.161
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FIGURE 3.9 CUMULATIVE FREQUENCY PLOT FOR ANTHRACENE
-------
1.994
0 999
0 500
0.250
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CUMULATIVE FREQUENCY (IN PERCENT)
"5 70 7b DO 85 »o"~"~»b
LEGEND- A = 1 DBS. B = 2 DBS. ETC.
1201 OBS HIDDEN
100
FIGURE 3.10 CUMULATIVE FREQUENCY PLOT FOR BENZOfA)ANTHRACENE
-------
I
31.622t
9.999
3.161
0.999
r
S
S
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THRESHOLD VALUE « 28 ng/ka
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CUMULATIVE FREQUENCY (IN PERCENT)
LEGEND. A = 1 OBS. B = 2 DBS. ETC.
88 OBS HIDDEN
FIGURE 3.11 CUMULATIVE FREQUENCY PLOT FOR FLUORENE
-------
THRESHOLD VALUE •• 56 mo/ko
100
CUMULATIVE FREQUENCY (IN PERCENT)
OBS-B •* OBS-ETC-
FIGURE 3.12 CUMULATIVE FREQUENCY PLOT FOR PHENANTHRENE
-------
TABLE 3.2. FRESHWATER DATA SUMMARY-POLYNUCLEAR AROMATIC HYDROCARBONS
00
acenaphthalene
anthracene
benzo( a) anthracene
fluorene
phenanthrene
Threshold
(•0/kg)
24
44
220
23
56
Median
Concentration
(mg/kg)
0.6
0.5
0.010
0.6
0.6
95th Percentile
Concentration
(mg/kg)
4.3
4.5
0.014
4.5
5.6
Highest
Concentration
(mg/kg)
5.0
17.0
0.650
6.3
6.4
-------
Bioaccumulation of PAHs within benthic organisms is also a major concern
when determining appropriate PAH levels, while some invertebrates have
inducible mixed function oxygenase systems capable of metabolizing PAHs,
others may lack the appropriate enzymes for b ^transformation. Oligochaete
worms, chironomids, and amphipods may contain concentrations of PAHs in their
tissues similar to those in the fine-grained organic rock sediment in which
they live. The amphipod, Pontoporia hoyi. in Lake Michigan, have
bioconcentration factors for PAH ranging from 10* to 1Q5 with respect to the
overlying water column (Eadie et al., 1982).
Alternative criteria were not readily available for PAHs. The only site
specific information obtained in this review referred to the Great Lakes
Region. Lake Superior had sediment concentrations that were ten times lower
than the lower Great Lakes. Lake Michigan had the highest sediment
concentrations. The available data correlate well with the hypothesis of
localized urban sources.
3.3 PHTHALATE ESTERS
The quantity of STORET data for for phthalate ester concentrations in
sediments was adequate. The data base for both esters consisted of
approximately 400 measurements.
The log concentration versus cumulative frequency plots for
diethylphthalate and dimethylphthalate are shown in Figures 3.13 and 3.14,
respectively. The shapes of the plots reflect the ubiquitous nature of
phthalate esters in the environment. There are few high concentration "hot
spots" that would be indicative of industrial point sources. Table 3.3
provides a summary of the data. The most notable aspect in the summary is the
lack of Level 4 range data.
The summary indicates that a significant number of sites are classified
as Level 3 for diethylphthalate. Dimethylphthalate, on the other hand,
contains a significant number of values in Level 2. In general, the data for
both phthalates are similar in terms of the shape of the respective
distributions.
-------
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FIGURE 3.13 CUMULATIVE FREQUENCY PLOT FOR DIETHYLPHTHALATE
-------
31 622«
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CUMULATIVE FREQUENCY (IN PERCENT)
OA
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LEGEND: A = 1 DBS. B ° 2 DBS. ETC
99 OBS HIDDEN
FIGURE 3.14 CUMULATIVE FREQUENCY PLOT FOR DIMETHYLPHTHALATE
-------
TABLE 3.3. FRESHWATER DATA SUMMARY--PHTHALATE ESTERS
chethylphthalate
dlinethylphthalate
Threshold
Concentration
(mg/kg}
1.28
1.96
Total Number
of Locations
368
347
Percent in
Level 1
64
65
Percent in
Level 2
20
34
Median
Percent in Percent in Concentration
Level 3 Level 4 (mg/kg)
16 none 0.40
1 none 0.50
95th Percent ile
Concentration
(ing/kg)
5.62
4.47
Highest
Concentration
(mg/kg }
5.80
5.00
•
SJ
ro
-------
Alternative criteria were not available. Site specific information
consisted mainly of studies in the middle and eastern United States where
major phthalate ester producers and consumers are located. Although
diethylphthalate and dimethylphthlate were not studied in these papers,
results for other phthalates were similar to those contained in Table 3.3.
3.4 PESTICIDES
STORET data for pesticide concentrations in sediments were relatively
extensive. The data base contained between 4,000 and 20,000 measurements for
each pesticide.
The log concentration versus cumulative frequency plots for aldrin,
chlordane, DOT, heptachlor, lindane and toxaphene are shown in Figures 3.15 to
3.20, respectively. The S-shaped plots transform into straight lines when the
x-axis is a probability scale; thus, the data are distributed in a log-normal
manner. Table 3.4 summarizes the pesticides data. In general, a very small
percentage of sites is in Level 4.
In reviewing the data, several aspects are worthy of note. The median
concentration is considerably less than the threshold value for all the
pesticides. Chlordane, DDT, and toxaphene are of greatest interest because of
the percent of observations in Level 2 column, the high values in the highest
concentration column and the 95 percent concentration column. An alternative
criterion of 0.02 mg/kg was proposed by the USGS for DDT. Using this
criterion, 96 percent of the data falls in Level 1. Lindane also has an
alternative criterion of 0.02 mg/kg which does not significantly change the
distribution. Alternative criteria were not found for the other pesticides.
3.5 CHLORINATED HYDROCARBONS (EXCEPT PESTICIDES)
The only chlorinated hydrocarbons excluding pesticides for which STORET
data could be obtained were the polychlorinated biphenyls (PCBs). PCB data
are contained in STORET in several isomer or trade-name groupings. The most
3.23
-------
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CUMULATIVE FREflUENCY (IN PERCENT)
LEGEND. A = 1 DBS. B = 2 DBS, ETC.
1937H OBS HIODFN
FIGURE 3.15 CUMULATIVE FREQUENCY PLOT FOR ALDRIN
-------
31 622 •
9.999
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LEGEND: A •= 1 DBS. B = 2 DBS. ETC.
11471 DBS HIDDEN
FIGURE 3.16 CUMULATIVE FREQUENCY PLOT FOR CHLORDANE
-------
31.622 •
9.999
3 161
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CUMULATIVE FREQUENCY (IN PERCENT)
LEGEND: A = 1 OK, 6 = 2 OK, ETC.
15661 OBS HIDDEN
FIGURE 3.17 CUMULATIVE FREQUENCY PLOT FOR DOT
-------
3.161
0.999
0.315
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93 100
CUMULATIVE FREQUENCY (IN PERCENT)
LEGEND: A = 1 DBS, B * 2 UBS. ETC.
12505 OBS HIDDEN
FIGURE 3.18 CUMULATIVE FREQUENCY PLOT FOR HEPTACHLOR
-------
1.994
0.999
0.500
0.250
^» O.lZb
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CUMULATIVE FREqUENCY (IH PERCENT)
eS TO 75 80 85 90 95 100
LEGEND A = 1 OBS. B * I OBS. ETC.
3762 OBS HIDDEN
FIGURE 3.19 CUMULATIVE FREQUENCY PLOT FOR LINDANE
-------
3 161
0.999
0.315
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CUMULATIVE FREQUENCY (IN PERCENT)
Ob 70 75 HO 85 90 95 100
LEGEND: A = 1 OBS. B • 2 OBS, ETC.
11678 OBS HIDDEN
FIGURE 3.20 CUMULATIVE FREQUENCY PLOT FOR TOXAPHENE
-------
TABLE 3.4. FRESHWATER DAFA SUMMARY-PESTICIDES
U)
aldrin
chlordane
DOT
heptachlor
lindane
toxaphene
Threshold
Concentration
(mg/kg)
0.021
0.020
0.006
0.020
0.0124
0.020
Total Number
of Locations
20,154
13,002
17,217
13,264
4,080
12,653
Percent in
Level 1
97
77
89
93
96
82
Percent in
Level 2
2
16
7
1
I
14
Percent in
Level 3
0.5
5
3
0.5
2
2
Median
Percent in Concentration
Level 4 (mg/kg)
0.5 0.0001
2 0.001
1 0.0004
0.5
1.0 0.0006
2
95th Percent ile
Concentration
(rag/kg)
0.003
0.097
0.015
0.006
0.012
0.044
Max imum
Concentration
{mg/kg)
1.97
11.9
15.0
1.97
1.19
19.5
-------
useful grouping for the present survey was by the Aroclor type. Due to the
large number of Aroclors commercially produced, only Aroclor 1016 (1221) data
were evaluated. This particular mixture contains a greater percentage of the
lower chlorinated analogs than do other Aroclor mixtures and is more water
soluble. The threshold criterion for Aroclor 1016 (1221) derived using
Pavlou's approach (JRB Associates, 1984a) would therefore be lower than for
PCBs as a group. To maintain consistency between the freshwater and marine
areas, a threshold value of 0.28 mg/kg, based on hexachlorobiphenyl, was
arbitrarily applied.
The STORET data base for Aroclor 1016 (1221) in sediments consists of 917
measurements. The log concentration-cumulative frequency plot is shown in
Figure 3.21. Approximately 18 percent of the data falls above Level 1. Seven
percent of the stations are classified as Level 2, 8 percent of the stations
are in the Level 3 range and 3 percent are in Level 4.
Once again, alternative EPA and USGS criteria for total PCBs have been
proposed. These criteria range from 0.02 mg/kg to 10 mg/kg using the USGS and
EPA criteria, respectively. At the lower end of this range, approximately 60
percent of the stations would have exceeded the Level 1 classification if this
criterion were employed. At the upper end, only a small number of
measurements (0.4 percent) would be classified as Level 2.
Considerable generic and site specific evidence has been accumulated
regarding the toxic environmental effects of PCBs (Nisbet, 1976). In situ or
Jin vivo studies that tested the effects of sediment-absorbed PCBs on biota
were not found/ Aquatic insects whose life stages include periods of time in
or on the sediments appear to be very sensitive to PCB exposure. In this
respect, it must be remembered that all of these toxicity data are based on
aqueous concentrations and, therefore, may not be indicative of the toxicity
of sediment-adsorbed PCB. However, sediment-adsorbed PCBs are available to
freshwater and marine benthic organisms (Neff, 1984) and therefore can be
expected to be toxic to them as well.
3.31
-------
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CUMULATIVE FREQUENCY (IN PERCENT)
LEGEND : A = 1 OBS. B « 2 DBS. ETC.
376 OBS HIDDEN
FIGURE 3.21 CUMULATIVE FREQUENCY PLOT FOR PCB
-------
This data gap highlights two implications for the application of a
chemical partitioning approach. One, if water quality criteria are to be used,
the criteria should be specifically based on assays which include benthic
organisms as one of the tested species. Two, solid phase bioassays should be
considered as a way to assess ingestive routes of exposure. If such bioassays
are economically or technically prohibitive, then it would seem reasonable
from a regulatory standpoint to apply a factor to account for the percentage
of uptake due to non-aqueous exposure.
3.6 MONOAROMATIC HYDROCARBONS
Insufficient STORET data were available to adequately analyze any
compounds in this chemical category.
3.7 MISCELLANEOUS
The only chemical not easily classified into one of the other six
categories was cyanide. Although usually thought of as a concern in the water
column due to solubility as free cyanide or soluble complexes, there is
nevertheless some tendency for cyanide to occur in some situations with
cations of lower solubility, thereby allowing for the possibility of sediment
accumulation.
The STORET data base consisted of 1,175 measurements of cyanide salts
in sediments of which 63 percent were at or below the 0.1 mg/kg threshold
(Figure 3.22). This value indicates a substantial portion of the STORET data
base falls within Levels 2 and 3. These points are equally distributed
between Levels 2 and 3. In addition, 17 percent of the data is classified in
Level 4. Other criteria for cyanide have placed the threshold level as high
as 100 mg/kg which would result in about 1.5 percent of the data being in the
upper three levels.
The historical lack of concern about accumulation of cyanide in
sediments has led to a paucity of field and laboratory research concerning the
effects threshold appropriate to benthic organisms. In the limited review of
the literature, no surveys were found that were indicative of what these
threshold values might be.
3.33
-------
3162
9999
3161
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CJ °
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31
EA
A
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10X THRESHOLD VALUE
"rx'THRESHOLD-VA-LUE
a
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^^"^~™~~~~
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B
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B
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CUMULATIVE FREQUENCY (IN PERCENT)
100
LEGEND. A = 1 OBS. B = 2 OBS. ETC
733 OBS HIDDEN
FIGURE 3.22 CUMULATIVE FREQUENCY PLOT FOR CYANIDE
-------
4.0 RESULTS AND DISCUSSION--MARINE/ESTUARINE
To evaluate the status of sediment quality of various marine and
estuarine locations, concentrations of chemicals of interest in sediments
were compared with the defined sediment quality criteria discussed in Sections
2.1 and 2.2. The marine data base was treated in the same manner as the
freshwater data base.
With special regard to the marine/estuarine data base, it is necessary to
reiterate several disadvantages of the equilibrium partitioning approach to
derive sediment quality criteria, identified by JRB Associates (1984b). These
disadvantages include:
1. Synergistic interactions among various chemicals are not known,
and are difficult to quantify;
2. The role of environmental variables (e.g., sediment organic carbon
content, pH, and redox potential) on the chemical behavior of
chemical pollutants in sediments often is understood and cannot be
quantified;
3. The bioavaiTable fraction of the total sediment pollutant
concentration frequently is unknown.
The following disadvantage could be added:
4. The carcinogenicity and mutagenicity of several PAH compounds is not
taken into consideration (e.g., that of indeno(l,2,3-CO)pyrene and
benzo(a)pyrene).
It should also be pointed out that severe biological effects have been
documented in several cases. These effects could be attributed to sediment
contamination, even though concentrations of individual pollutants did not
reach alarming levels. As noted earlier, this discrepancy may be the result
of an inherent problem in using non-site-specific sediment quality criteria
and ignoring possible additive or synergistic actions among multiple
contaminants. Several such instances have been documented in the Puget Sound
and New York Bight regions (Mayer, 1982; Malins, 1980).
4.1
-------
Biological effects data were better correlated with site-specific
sediment pollutant concentration data in the marine/estuarine literature than
for freshwater data sets. The limited number of marine/estuarine data points
for each chemical do not permit the generation of cumulative frequency plots
or extensive statistical analyses more suitable to the extensive freshwater
chemical data sets. An enhanced tabulation of the marine/estuarine data
provides an overall perspective of the sediment quality status in these
environments.
4.1 METALS AND ORGANIC CONTAMINANTS
An estimation of the status of the sediment quality of various marine and
estuarine sites in the continental United States was based on first-cut
sediment quality criteria using the equilibrium partitioning approach as
discussed in Section 2.1. As an exception, polynuclear aromatic hydrocarbon
contamination was estimated using the background approach for sediment quality
criteria. A sediment total PAH concentration of 1 ppm dry weight was chosen,
in this case, as the cut-off value between non-polluted and slightly polluted
sediments. Selection of this value was based upon data contained in a
publication by Hites et al. (1980), entitled "Polycyclic Aromatic Hydrocarbons
in Marine/Aquatic Sediments: Their Ubiquity." Provisional sediment quality
criteria using the equilibrium partitioning approach are expressed on the
basis of organic carbon, rather than total sediment mass.
As previously discussed, to allow comparison of these criteria with reported
sediment concentrations of metals and organic contaminants, calculation of the
sediment-threshold concentrations were based on 4 percent organic carbon in
sediments. This estimate of organic carbon content is on the high side for
most marine sediments, and its use throughout this document has an important
effect on the threshold values used to determine sediment quality status. If
2 percent organic carbon had been chosen as a national average, the threshold
levels would have been half as high, and more sites would have been identified
above the threshold value.
4.2
-------
4.2 NATIONAL PERSPECTIVE
The results of this limited literature search on the national status of
the sediment quality in marine/estuarine waters are summarized in three sets
of figures-Figures 4.1, 4.2, and 4.3. These figures provide information to
assist the reader in assessing the quality status of marine and estuarine
sediments of coastal states for each of the various groups of chemicals.
Chemical groups were merged were appropriate, to enhance data presentation. In
Figures 4.1, 4.2 and 4.3, the concentration ranges are grouped and presented
as symbols which denote the quality status of the various sites (See Section
2.2). Whenever a discrepancy was found in overlapping data sets, the data
denoting a higher concentrations of the chemical were selected. In addition to
visualizing the sediment quality status of specific marine and estuarine sites
for various compounds, Figures 4.1, 4.2 and 4.3 also clearly indicate the
general paucity of data for nationwide marine and estuarine areas, with the
exception of certain classes of compounds such as PAH, PCB, and metals.
The complete data set for coastal sites is presented in Tables 4.1, 4.2
and 4.3. Sediments of marine/estuarine sites containing levels of chemical
exceeding the threshold values identified in Table 2.1 were analyzed by
including as much specific information as available in the data base. The
numerical designations contained under the column headings (underlined in
text) on Tables 4.1, 4.2, and 4.3 are indicated as follows:
• Sample location
• Name of the chemical, including a numerical value designating the
category (Cat.) to which the chemical belongs, i.e., 1) polynuclear
aromatic hydrocarbons; 2) pesticides; 3) other chlorinated
hydrocarbons; 4) aromatic hydrocarbons; 5) phthalates; and 6) metals
• The chemical concentration. (Concentr.)including units in mg/kg dry
weight; Range of values found, and an indication whether mean or
median concentrations were used
• The concentration status (Stat.), identifying whether the sample
location was characterized as level 2, 3, or 4, using criteria
discussed in Sections 2.1 and 2.2.
• Any recorded biological effect: 1) tissue or whole organism
concentrations of the chemicals, 2) a change in species diversity
4.3
-------
• - NO VALUE AVAILABLE
• = LEVEL 1
O = LEVEL 2
9 = LEVEL 3
• = LEVEL »
CALIFORNIA
L.A. County, Wastewater Treatment Plant
Los Angeles Metropolitan Area
LOUISIANA
Lake Pontchartrain
MASSACHUSETTS
Charles River, Boston
Boston Harbor
Cape Cod Bay
Buzzards Bay
"Mud Patch," South of Nantucket
Outer Channel, Gulf of Maine
Massachusetts Bay
Gulf of Maine
CuU of Maine
NEW JERSEY
Arthur Kill
Newark Bay
Kill Van KuU
Hackcnsack River at Hackensack
Sandy Hook Bay
NEW YORK
New York Bight
New York Bight "Sewage Study Oumpsite"
New York Bight, Hudson Canyon Area
New York Bight, Christiaensen Basin
Outer New York Bight
Cowanus Canal
Newton Creek
East River
Lower New York Bay
Raritan Bay, West
Hudson River
Pierhead Channel
Atlantic Ocean off Sandy Hook
TEXAS
San Luis Pass
WASHINGTON
Sinclair buet
Southwest Commencement Bay
Puget Sound
Seattle Waterfront
Duwamish Waterway
Hylebos Waterway
Commencement Waterways
Elliott Bay
Outer Elliott Bay
West Point
Browns Point
Budd Inlet
Case Inlet
Port Madison
• •
i
o
9
©
9
9
FIGURE 4.1. AROMATIC AND POLYNUCLEAR AROMATIC HYDROCARBONS
4.4
-------
• » NO VALUE AVAILABLE
• = LEVEL 1
O * LEVEL 2
• • LEVEL 1
• • LEVEL »
CALIFORNIA
Pita Verdea, Whites taint Outfall
L.A. County, Wanewater Treatment Plant
SMI Francisco Bay
Malibu Lagoon
Fatal Verdea, JWPCP Outfall Syttem
CONNECTICUT
Naugatuck River at Amoma
New Haven Harbor
CanectiGut River at Hartford
Housatonic River at Stamford
Connecticut River at Ban Haddun
Connecticut River at Middle Haddun
Hodcanum River at Can Hartford
New Haven Harbor
Stamford Harbor
Tharna River near Mohegan
Pavcatuck River near Paweatuck
Connecticut River at Middletown
QumnipuK River at North Haven
DELAWARE
Delaware River
Philadelphia Sewage Sludge Site
Altamlc Ocean
FLORIDA
Fort Lauderdale, South at New River
Fort Lauderdale. North of New River
St. George Sound
St. John* River
Choctawhatchee Bay
Catoosahatchee River
Calomahatchee Estuary
South Bbcayne Bay, Turkey Point
Biacayne Bay
Indian River, South of TltuivUle
Big Pine Key
Perdido River
Perdido Bay
O
Escambu Bay
Tampa Bay
Appaladuocola Bay
Sebastian River, Melbourne
Santa ROM Sound, Manatee Point
Tomota River
Boca Raton, Canal E-4
East Bay, Tampa
Halifax River
East Bay, Bay River
Pine bland Sound
St. Joe Bay
Amelia River
Estero Bay
St. Andrews Bay, Panama City
Blackwater Bay
Crescent Beach I
Peace River
Roosevelt Bridge
LOUISIANA
Ulmmlmmtfjl Qetta
Lake Pomchanraln
e e e a
FIGURE 4.2. PESTICIDES AND OTHER CHLORINATED HYDROCARBONS
4.5
-------
• s NO VALUE AVAILABLE
• * LEVEL 1
0 * LEVEL 2
O » LEVEL 1
• a LEVEL *
MASSACHUSETTS
MMMdMMttl Bay
Buzzard) Bay
Baton Hvfaar
MARYLAND
Chesapeake Bay
MAINE
Puiubscet Bay
Portland, Including Back Cove * Fore River
Cam Bay, Portland Harbor
NEW JERSEY
Newark Bay
Kill Van Kull
Manasquan at Allen Wood
Raritan Bay
MUUca River at Pleasant Mills
Hackemach River
Sandy Hook Bay
NEW YORK
Hudson River
N.Y. Bight, Sewage Sludge Dumpaiie
N.Y. Bight, Dredge Spoil Dumpaite
Pierhead Channel
New York Bight Apex
Cowan us Canal
Lower Bay
Newton Creek
Raritan Bay
Arthur Kill
Chriitiamen Baain
Upper Bay
East River
Sandy Hook
Outer N.Y. Bight
N.Y. Bight, Hudson Canyon
TEXAS
Espirctu Santa Bay
Carancahna Bay
San Luis Paaa
Keller Bay
Corpus Chrlstl, toner Harbor
San Antonio Bay
AransacBay
Sabim River
MatagordaBay
Buffalo Bayou
LagunaMadra
Redflsh Bay, Conn Brown Harbor
NueeesBay
Brownsville' Ship Channel
Guadalupe Estuary
Baffin Bay
San Jadnto Estuary
LavacaWTre* Palaoo Eituary
Taylor Bayer, Neehes River
Trinity Bay
!
B
1 § ; 1 3 • 1' t
isl llsisiiiftiJ,,
a ! 1 § 1 1 IIS III : 1 1 1 1 1 fi
*
• • •
......... ....... a
9* . . (| . . ....*••
FIGURE H.2. (Continued)
406
-------
• = NO VALUE AVAILABLE
• = LEVEL 1
0 = LEVEL 2
9 = LEVEL 3
• = LEVEL 4
WASHINGTON
Harbor Island, West End
Hylefaos Waterway
Duwamish Waterway
Southwest Commencement Waterways
Hylebos, Blair * Commencement Waterways
Puyallup Waterway
Southwest of Normanor Park
Harbor Island, East End
Seattle Waterfront
Port Madeson
Hood Canal
Elliott Bay
Mid Elliott Bay
Outer Elliot Bay
LUiwaup River
Oak Bay
Strait Juan De Fuca
Port Susan
Saratoga Passage
Pleasant Harbor
Shelton-Oakland Bay
Sinclair Inlet
Edwards Point
Browns Point
Columbia Beach
Nisqually Beach
Budd Inlet
Johnson Point-Case Inlet
Arcading Pickering Pass
West Point
Commencement Bay
FIGURE 4.2. (Continued)
4.7
-------
• = NO VALUE AVAILABLE
• = LEVEL I
O = LEVEL 2
9 * LEVEL 3
• 3 LEVEL *
CALIFORNIA
Palos Verdes Outtal Zone
Joint Vater Pollution Control Monitoring Zone
San Francisco Bay, Beemar Point
L.A. City Hyperion Outfall
Lower Newport Bay
Bolsa Bay, Outer Bay
Bolsa Bay, toner Bay
Oceanside
Huntington Harbor
Santa Barbara
Point Conception
Dana Point
Dana Point Harbor
San Diego
Bolsa Bay Flood Channel
CONNECTICUT
New Haven Harbor
Cedar Creek at Black Rock
Black Rode
Pawcatuck River at Pawcatuck
Mystic River Estuary
Quimipiac River
DELAWARE
Philadelphia "Ocean Dumpaite*
Philadelphia "Ocean Controls*
FLORIDA
PerdidoBay
St. Johns River
Turkey Point
Card Sound
GEORGIA
Savanna, Ogeechee, Altamaba and Satilla Riven
LOUBIANNA
Mississippi River Delta
Lake Pontchartrain
MASSACHUSETTS
Boston Harbor
Acushnet Estuary
Buzzards Bay
MARYLAND
Patapsco Estuary, Baltimore Harbor
Chesapeake Bay
Black River off Chesapeake Bay
MAINE
O
O • 9
• i 5
• 0 9 0
o 0 o e
0 .
6 •
o •
0 0
9 •
© •
•
o •
• o
9 O
• 0
•
0
• 0 0 • •
• • • 0 •
• • • 0
0 0 . •
• •09 • 00
e 0 e e • 0 •
• • • e • • e
NET JERSEY
Kill Van Kull
Arthur Kill
Newark Bay
N.Y. Bight, Cellar Dirt Dump Site
Atlantic Ocean, off Long Branch
Sandy Hook, Raritan Bay
Atlantic Ocean, off Bradley Beach
Atlantic Ocean, off Belmar
Great Bay
Atlantic Ocean, near Sandy Hook
Hackensack Rlmr new MarkMw*
•
•
e
•
•
• i
• 0 9 • •
•99-0
89 • •
0 • •
• • 0 . •
O • • • e •
• • • 0 • •
• • • •
e e •
i
i
•
s
FIGURE 4.3. METALS AND PHTHALATES
4.8
-------
• = NO VALUE AVAILABLE
• = LEVEL I
O = LEVEL 2
9 = LEVEL 3
Raritan Bay
Arthur Kill
Lower Hudson River
Hudson Estuary
Upper New York Bay
New York Harbor
N.Y. Bight, Sewage Sludge Dumpute
Long bland Sound, Branf ord Harbor
N.Y. Bight, Dredge Spoil Dumpsite
N.Y. Bight, Hudson Shelf
Atlantic Ocean, off Long Island
Off Long Island and New Jersey
RHODE ISLAND
Providence River
Narragansett Bay
Fix Island
Rhode bland Sound Dumpsite
SOUTH CAROLINA
Charleston Harbor
Wmyah Bay, Coastal Rivers
St. Helena Sound
Ashepoo River
Foster Creek
TEXAS
Colorado River
Corpus Chrbti Harbor
Corpus Christi Channel
Corpus Christi Bay
Texas City Channel
Freeport Ship Channel
Aransas Pass Turning Basin
Houston Ship Channel
Conn. Brown Harbor
Sabine-Neces Line, 3efferson
SJ=. Point Comfort, Cox Bay
Gulf of Mexico Shelf
Laquinta Ship Channel, Nueces River
Mesquite Bay, Nueces River
Esperito Santo Bay
Christmas Bay
San Antonio Bay, Victoria Channel
Nueces Bay
Laguna Madre, Rio Grande
Matagorda Bay, Palaoos Channel
East Matagorda Bay
Keller Bay, South of Olivia
Tres Paiacios Bay
Brownsville Ship Channel
San Luis Pass
WASHINGTON
Budd Inlet
Commencement Bay
Sinclair Inlet
Elliot Bay
Port Madison
Case Inlet
Duwamish River Estuary
Bellingham Bay
McCalister Creek
• 9 O © © 0
• • • 0 • .
• 90* • ©
e •
• • • 9 0 • © •
• • O O • • 0 •
• 0 e • • •
• • 0 • •
e •
• •
00. • 9 © •
9 • © • •
©
9
O •
0
O
9
•
0
•
•
©
•
O
0
§
O
0 •
0 •
0 0
0 •
0 •
0 •
0 •
O 0
O
©
O
©
FIGURE 4.3. (Continued)
4.9
-------
"" ""
s
STATE
LOCATION
CONTMINANT
MICE
CAT.
STAT.
EFFECT
CA
CA
CA
CA
CA
CA
CA
CA
CI
HA
I1A
M
RA
IM
M
HD
M
M
NJ
NT
NY
NT
«Y
NV
NV
NT
NV
XV
RI
II
M
NA
HA
•A
M
•A
REFERENCE
l.A. COUNTY. tASTENTR TREAT. PLANT
PW.OS VEROES, NH1TES POINT OUIFALL
PALOS VERDES PENH., JKPCP OUTFAll SYST.
PAIOS VERDES PENH., UNITES PT. OUTFALL
SAN FRANCISCO IAY, BEEIIAR POINT
L.A. CITY, HYPERION OUTFALL
JOINT HATER POLL. CONTRl. IWTRNG 1ME
PALOS VERDES SHELF
BUINNIPIAC RIVER
CHARLES RIVER, BOSTON
BOSTON HARBOR
CHARLES RIVER, BOSTON
CHARLES RIVER, BOSTON
ACUSHNET RIVER/NEK BEDFORD HBR
ACUSWEI RIVER
PATAPSCO ESTUARY. BALTIROPE HARBOR
ARTHUR KILL
HEMP* BAY
KENARK BAY
NEK YOR* BIGHT
EAST RIVER
NENTON CREEK
GONANUS CANAL
LONER BAY
SEMAGE SLUDGE DUNPSITE
HUDSON RIVEP (NV HBR TO KH NO)
HUDSON RIVER
HUDSON RIVER: NYC - INDIAN POINT
PROVIDENCE RIVER
CORPUS CHRISTI CHANNEL
PUGET SOUND: COMIENCEHENT MTEPNAYS
PUGET SOUND: OUNARISH NATERNAY
PUGET SOUND. NEST POINT
PUGET SOUND: SEATTLE NATERFRONT
PUGET SOUND: HYLEBOS NAFERMV
PUGET SOUND: CONNENCEHENT BAY
DDT
DDT
T. DDT
L ODT
CADNIUN
CHROHIUH
CHROHIUH
CHRONIUH
HERCURV
PM
PAH
PAH
PAH
PCBS
COPPER
CHRONIUN
PAH
PAH
PCBS
PAH
PAH
IOTAL PAH
TOTAL PAH
TOTAL PAH
DDT
PCBS
PCBS
PCBS
CHROHIUH
HERCURV
PAH
PAH
PAH
PAH
PAH
ARSENIC
0.191
0.66
140
90
1000
280
310
1100
322
87
12
87
120
181.00
7300
490
12
40
3.68
76
49
182
16.4
9.9
O.OB4
3
428
18
13
10.3
44.7
10.7
16
470
nits i
HS/KG
HE/KG
1G/K6
IB/KG
KG/KG 1
KG/KG I
HG/K8
HGKG
KG/KG
HG/KG 1
KG/KG I
HG/KG
HG/rG 1
NE'KG
KG/KG 1
HG/tG I
HG/KG I
HG/rG
HE/KG
HG/KG I
HG/KG I
KG/KG 1
iG/kG i
HG/KG I
HG/kG I
HG/KG I
KG/KG 1
KG/KG
US/KG 1
KG/KG I
NS/kG >
KG/KG I
N6/KG 1
NG/IG I
100-280
7.3-130
-1300
-1500
1000-1300
24-880
5-900
I 3000-1300
< 4-4240
047-.I20
0.5-60
0.3-140
0.3-26
0.3-30.8
1.39-29.3
0.33-49.3
0.83-47.2
» GOSSEIT, R.I., I9BI
1 YOUNG, D.R., 1982
1 SMOKIER ET 41., 1979
1 SIEPHENSON ET AL., 1975
» STORET
1 YOUNG, D.R., I9B2
1 YOUNG, O.R., 1982
1 SHERNOOD, N.J , 1982
» STORET
» BEITER ET Al., 1981
1 BOEHN ET Al , 1984
» KITES ET AL., 1980
1 ONDSOR, J.G t R.A. HUES, 1979
1 HALL.EI AL.I9B3
1 FORSTNER 1 IHI1IHMN, 1979
* HEll. G.P., 1976
* BOEHN. P D . I9BO
» BOEHH, P.D , 1980
1 ftUBINSIEIN, N 1. El Al.. I»B4
» >OONS, C.B. 1 i P THOHAS, 1979
i BOEHH, P D., I9BO
1 O'CONNOR El AL. I9B2
1 O'CONNOR ET AL. 19B2
1 O'CONNOR El AL. 1982
1 O'CONNOR ET IL. 1982
1 O'CONNOR ET Al. 1982
1 BOEHN El AL., 1964
» BOPP ET AL.. 1981
1 E ISLES, R. ET AL., 1977
1 NEFF, ET AL., 1978
1 HAllNS ET AL , 1980
1 HAllNS ET AL., 1980
1 HAllNS El Al., 1980
1 MLINS ET AL., 19GO
1 HALINS ET Al., 1980
1 NAIINS El AL., 1980
4.10
-------
TABLE 4.2.
COASTAL U.S. REGIONS CONTAINING SINGLE POLLUTANTS AT
CONCENTRATIONS EXCEEDING PROVISIONAL SEDIMENT THRESHOLD VALUES BY
THREE- TO TEN-FOLD (LEVEL 3)
STATE
U
CA
CA
CA
CA
CA
CA
CT
U
>u
U
N
M
NJ
tH
NY
NV
NY
NY
NT
NY
MV
NY
•r
NV
NV
NY
NY
NY
m
HY
N1
NY
m
N>
Rl
P.1
II
TJ
II
II
Tl
II
II
M
NA
NA
M
M
•A
LOCATIB
L.A. COUNTY, MSIENTR IDEAL PLANT
PAIOS VERDES PEN, LA COIfflTV
pAios VERDES SHELF
PAIOS VEROES SHELF
LOVER HEWORT Wl
PALOS VERDES SHELF
JOINT HATER POLL. CONIRL. IMTRMG ZONE
CEDAR CREEK AT BLACK IDC*
TILL VAK KULL
•EMRK IAV
ARTHUR KILL
ARTHUR KILL
KILL VAN KULL
NENARK BAY
MR I IAN BAY NEST
(EN YORK BIGHT
CONIAHiNANT
PCBS
CKRomun
COPPER
LEAD
HERCURr
NICKEL
NICKEL
LEID
PAH
PUS
LEAD
REKURT
HEDCURT
PAH
PAH
CONCENTR.
0.«34
240
420
4 10
;.!
Gl
44
430
8.7
1.4
1627
1
4
B
11
38
HE* VOW BIGNT RES: CHRIST1AENSEN P«SIN TOMl PAH 4
PIERHEAD CHANNEL
LOKR BAV
•EN YOU BIGHT: SEKA6E SLUDGE DEPOSIT
PIERHEAD CHANNEL
90IANUS CANAL
(ATHUR Kill
MEN mi BIGHT SEMGE SLUDGE DUHPSI1E
SENAGE SLUDGE OUHPSIIE
KEN YORK BIGHT
NEN VOPr BIGHT: BREDGE SITE
NE> YORK BIGHT 'DREDGE SPOILS'
KEN YORK BIGHT 'SEKAGE SITE'
RARITAH BAV
K» YORK BIGHT: SLUDGE SITE
HE* YORK BIGHT: SEHAEE SLUDGE
NED YORK BIGHT: SPED6E SPOIL DUUPSIU
RAP1TAN BAY
LONER HUDSON RIV'EP
RAD IT M BA(
NEW «ORK HARBCI
ARTHUR KILL
MARRAGMSETT BAY
PROVIDENCE RIVER
TEIAS CITY CHAMEL
HOUSTOII SHIP CHANNEL
CORPUS CKBISII CHANKL
CORPUS CHRIST I, INNER HARBOR
CONN. BRONN HARBOR
COPPUS CHRIST! CHANNEL
CORPUS CHRISTI HARBOR
PUGET SOUND! SINCLAIR INLET
PUGEI SOUND: S» CONRENCEICNT BAV
HfLEBOS, BLAIR, 1 COKSENCEHENT NTRNVS
HARBOR ISLAND, HEST END, PUGET SOUND
PUSET SOUND: HVLEBOS
COHHENCEKNI BAV
TOTAL PAH
001
PCBS
PC1S
PCiS
PCBS
PCIS
PCFS
FOS
CHPOKIUH
CWOItlUN
CHtOHIUH
CHROHIUB
CHROHIUH
COPPER
LEAD
LEAD
HEPCURK
HEPCURf
CHRDHIUH
COPPER
CHfiOHIW
CHROmiRl
CHROmilR
LEAD
HEPCURf
ZINC
2 INC
PAH
PAH
PAH
PCBS
PCBS
ARSENIC
^••^•••B
J.2
" 034
1.13
1
1
i.;
1.1
2
0.92
IK
192
so:
130
110
181
101
415
300
7.1
101!
189
13T
82
389
4
4033
33N
4.2
1.8
9.371
2.]
0.3
233
UNITS SAN KEO. RAKE
HE/KG I
K/KS 109-1480
IK/KG 370-430
HS/kE 140-440
JI6A6 1.2-3.7
RG.'KG 74-91
HG/rG 1 -130
HO/KB I
US/KG
nt/kf,
H6'«6
ItGttS
WHS
HG/KE
KS/KE
KG/KG
HE' KG
US/ KG
KG/KG
KG/ KG
K/CG
NG/rG
IC/KG
WIS
N6/'S
KG/KG
KlfB
KG/rG
no/re
fS-rs
«6/rG
KC/KG
ffi/rs
1
I 0.04-2.2
( 3.32-;
•110
2-240
U. 4-1230
I
I-9B3
1 2.7I-34.B9
RG-KS I 1.3-J1
ffifKG 1
RG/K6 I
K/CG
KG/KG I
ICKS I
IG/CG
DG/rG I 229-I1MO
IKIK 1 1.43-17.7
ffi/KG I . K.244-I4.G
KB/IS I 1.803-28.3
JIG/KG I
HE/KG I 0.027-1.2
KG^KG 1 1-4-470
CAT.
3
4
4
4
4
4
4
4
I
3
t
4
4
4
1
1
1
1
Z
3
3
3
3
3
3
j
t
6
4
i
i
4
6
4
4
6
t
b
t
*
4
t
1
• 1
1
1
3
t
•H^V
STAT. EFFECT REFERENCE
3
3
1
3
J
3
3
3
3
3
3
;
3
3
3
3
3
s
3
3
3
3
3
J
3
3
3
3
3
3
3
3
3
5
3
I
3
5
3
I
3
3
3
3
3
3
EOSSETT, ».»., 1981
HERSHELHAN.GP.fi Al, 19!
SHEPNOOD, n J., l'82
SHERNOOD. U ;., 1982
SIDRET
SHERNOOD. IU . 1982
YOUNG. D.R.. I«B2
STORE!
MEW. P t., 1930
IOEHN ET Al . PB4
2 BRETELER.R , ET AL., I9B3
2 BRE1ELER.P , ET AL., 1983
2 BftEIELEM . ET AL.. I9B3
2 BRETELER.R., ET AL., 1983
BOEHt, P.D., 1180
HUES E1 AL.. 1980
O'CONHDR El «... 1982
0-CWW19 El AL., 1182
O'COMOR £1 Al , 1'82
TOEWET Al., 198<
O'CONWR E! Al , 1982
O'CONNOR El HI . 1982
eOEHH ET Al , IK*
MESI, R H. t HA1CHER, W:
O'CONNOR V PL i98?
ENGIER, P.I. E! Al., 1981
tOUNS, D.D., I9B2
EISLEft. t V M.., 1*7.'
EI51EP, R. ET «. , 1977
2 BREIELEP.R., ET Al., 1983
tOIKG, D.P., 19B2
2,3 STEIHLE ET AL.. 1 '82
2.3 STEIHLE ET AL.. l<82
2 BREIELER.fl., EI «l . 1983
: BREIELEP.R . EI «L . 1983
.: BPETELER.R . EI AL., I98S
RUBINSTEIN, I.I. ET AL.. I9B3
STORE!
GOLDBERG EI M... 197?
EISLEP, P. ET AL., 1«77
NEFF, ET AL., 1978
KEFF, ET AL . 1918
HEFF, E! «... 19!B
STQRCT
STORE!
NEFF, EI «... 1978
EISLER, R. EC Al., 1977
NAUK ET M.., HSO
NW.IKS ET AL., 1990
,2 RllEV ET «L., 1911
S10RE1
MIINS ET AL., 1190
IONS. 1982
4.11
-------
TABLE 4.3. COASTAL U.S. REGIONS
CONTAINING SINGLE POLLUTANTS AT
P2R)°VISIOIWL S£DWEHT THRESHOLD VALUES n
STATE LOCATION
r> PALOS VEROES SHELF
CA OCEANSIDE
CA PA10S VERDES
CA POINT CONCEPTION
CONIANINANT
CADMIUM
CHROMIUN
CHROMIUM
CHROMIUN
CA JOINT NAIER POLL. CONTRL. NNTPNG ZONE COPPER*"
CA L.A. CITY, HYPERION OUTFALL COPPEP
CA PALOS VEROES PEN, LA COUNTY COPPER
CA JOINT HATER POLL. CONTRL. HNTRNG ZONE LEAD
CA PALOS VERDES PEN, LA COUNTY HERCURV
C« LONER NEDPORT BAY nERCURY
CA JOINT HATER POLL. CONTRL. MNIRNG ZONE HERCURV
C« L.A. CITY, HYPERION OUTFALL
U PALOS VERDES PEN, LA COUNTY
CA SANTA BARBARA
CA L.A. CITY, HYPERION OUTFALL
CA OCEANSIDE
CA PALOS VERDES SHELF
CT NAUGATUCK RIVER AT ANSONIA
CT NEN HAVEN
CT CEDAR CREEK AT BLACK ROCK
CT BLACK ROCK
CT CEDAR CREEK AT BLACK ROCK
DE DELAKARE RIVER (HP 30)
FL ST. JOHNS RIVER
FL ST. JOHNS RIVER
FL TURKEY POINT
LA MISSISSIPPI RIVER DELTA
LA MISSISSIPPI RIVER DELTA
m CAPE COD BAY
NA BOSTON HARBOR
MD CHESAPEAKE BAY
MD PATAPSCO ESTUARY: BALTIMORE HARBOR
MD PATAPSCO ESTUAPT: BALMHORE HMBOR
HD CHESAPEME BAY
HO PATAPSCO ESTUARY' BALIIKOPE HARBOR
NO PATAPSCO ESTUARY. BALTIHO'E HAPFOR
W KILL VAN VU.L
NJ NENARK BAY
NJ SANDY KOOK/RARITAN BAY
NJ NENARK BAY
NJ NVB, CELLAR DIRT DUMP SITE
NJ KILL VAN MILL
NJ ATL. OCEAN OFF LONG BRANCH
NJ NV8, CELLAR DIRT DUMP SITE
M ATL. OCEAN OFF BRADLEY BEACH
NJ ARTHUR KILL
INY NEKTON CREEK
NY SENAGE SLUDGE DUMPS ITE
NY HUD-RARITAN ESI: I3KN N OF THE BATTERY
NY CHRISTIAENSEN BASIN
NY HUDSON RIVER IFRON KN 13-66)
NY DREDGED MATERIALS DUHPSITE
NY NEN IORK BIGHT (SEMGE SLUDGE DEPOSIT)
NY LONER BAY
NY NEN YORK HARBOR
NY UPPER BAY
NY DRED8ED MATERIALS DUNPSITE
NY CHRISTIAENSEN BASIN
NY NEKTON CREEK
NY CHRISTIANSEN BASIN
NY NEN YORK BIGHT (DREDGE SPOIL DEPOSIT'
NY RARITAN BAY
NY ARTHUR KILL
NY NEN YORK BIGHT APE! DUMP AREA
NY NEN YORK BIGHT: SLUDGE SITE
NY LONER HUDSON RIVER
NY HEN YORK DIBHT -WEDGE SPOILS-
NY KEN YORK BIGHT: SEVA6E SLUDGE
NY UPPER NEK YORK BAY
NY NEN YORK BIGHT -SENSE SITE-
NY NEN YORK BIGHT: DPEDGE SITE
MERCURY
NICKEL
NICKEL
NICKEL
NICKEL
ZINC
PCBS
MERCURY
MERCUPY
MERCUPY
ZINC
PCBS
LEAD
MERCURY
NICKEL
NICKEL
NICKEL
PAH
HERCURV
CHROMIUM
COPPEP
LEAD
NIC) EL
NICKEL
ZINC
PCBS
PCBS
CHPOMIUH
LEAD
LEAD
LEAD
MERCURY
MERCURY
MEPCURY
ZINC
NAPTHALENE
TOTAL PAH
TOTAL PAH
DDT
DDT
DOT
PCBS
PCBS
PCBS
PCBS
PCBS
PCBS
PCBS
PCBS
PCBS
PCBS
ARSENIC
CHROMIUN
COPPER
COPPER
COPPER
COPPER
COPPER
COPPER
COPPER
CONCENT*.
52
79.6
47
12.3
46.9
:BO
300
164
240
1
1.2
1.7
j 7
52
-II
ll
59
23.7
1700
0.37
1 5
0.8
0.8
1300
0.46
143
0 83
23
12
40
I 3
2 1
'40
34u
26
36
0 37
0.3°
53
267
200
368
1.48
2.!
1.00
847
120
I.I
2
0.16
0.013
0.009
0.4
0 7
U.7I3
0.27
0.4
0.7
0.4
0.75
0.62
0.38
50
52
140
225
142
220
214
142
140
••^^^^••^H
UNITS KAN
HG/KG
HG/rG I
RG/KG I
HG/rS I
NG/KG I
HG/kS 1
MG/KG 1
NG/KG
MG/KG I
MS/KG
MG/KG
NG/KG 1
HG/tG
ffi/rc I
HG/KG I
HG/KG i
HG/rG
HG/KG
NG/KG
HG/KG
MG/KG
HG/KG
MG/KG
HG/KG
RG/KG I
HG/KG
RG/KG
HG/K6 I
HG/KG
HG/rG
HG/kG
NGr'lLG
NG/P6
HG'PG
HG'kG
RG/KG
NG/KG
HG/rG 1
MG/KG
HG/KG 1
HG/KG
MG/KG
HG/KG
HG/KG I
KG/KG
M6/K6 I
NG/KG 1
NG/KG I
HG/KG I
MG/KG I
HG/KG
HG/KG 1
HG/kG
H6/KS
HG/KG I
NG/KG I
NG/KG I
NG/KG
HG/rG
HG/KG
HG/kG
NG/KG
MG/KG
HG/KG
HG/KG
MG/KG
HG/KG
HG/KG
HG/KG
HEO. RAKE CAT. SIAT. EFFECT REFERENCE
« 4--J7 k
6
37 0-32.3 6
24.8-44.' 6
•940 6
-1000 6
I 14-937 6
-380 6
I 0 13-5.4 6
I 0.3-5.7 6
_• i ,
-3.1 6
-6.1 6
I 16-134 6
14 0-29.3 6
-170 6 2
6 2
1600-1900 6 2
3 2
0.25-1.5 6 2
6 2
6 2
6 2
3 2
6 2
6 2
6 2
I L 1
1 62
6 2
I .300-6.700 6 2
6 2
6 2
6 2
6 2
6 T
t 2
3 2
I 38-33 6 2
6 2
X 126-280 6 2
6 2
I 0.93-2 5 6
I 1.3-3.3 6
I .
* 6
6
1
2 2
.OIO-.OI5 2 2
2 ?
1 060-2.2 3 2
« • 32
I 0.46-7.28 3 2
0.13-0.40 3 2
3 :
3 2
3 2
0.05-1.5 3 2
.003- 400 3 2
0.27-0 3 3 2
18-140 2
44-55 2
-240 2
2
8-J95 2
2
2
80-240 2
-3W 2
SKERMOD, I.J., 1902
(AIZ, ». t I.R. KAPLAN, 1981
KATZ, «. 1 I.R. KAPLAN, 1981
KATZ, A. 1 I.R. KAPLIN, 1981
'AIZ, «. 6 I.R. (APIAN, 1981
IOUNG. D.R.. 1982
YOUNG, D.R., 1982
HERSHELMAN.GP.EI AL 1981
YOUNG, D.P., 1982
HERSHELRAN.GP ET M., 1981
STORET
YOUNG, D.R., 1982
YOUNG, D.R., 1982
KERSHELHAN.GP El M., 1981
KATZ, A. i I.R KAPLAN, 1981
YOUNG, O.K., 1982
KATZ, A. 1 I.R. KAPLAN, 1981
SHERNOOD, H J., 1982
SIORET
FORSTNER t WITTHANN, 1979
STGRET
STORET
STORET
BOPP ET AL., 1981
STORET
STORET
EISLER, R. ET AL., 1977
PRESLEY, 8.J ET AL., 1980
PPESLEY. B.J. ET AL , PBO
HUES El AL.. 1980
SIORET
HELTZ. G P , 1976
HELZ. C R., 1976
HELZ, i P., 1=74
HELIZ. E P , 1976
HELZ, E.R. . 1776
HELZ, E.»., l«*6
BOEHH. P.D . I9BO
BOEHN, P.O., l?80
SHERNOOD, M.J., 1982
BRETELEP.P., El AL., 1985
STORET
BRETELER.R., ET AL.. I9B5
SIORET
SIORET
STORET
BRETELER.R., ET AL., I9B3
O'CONNOR ET AL., 1982
O'CONNOR ET AL., 1982
O'CONNOR El AL., 1982
O'CONNOR El AL., 1982
O'CONNOR El AL , I9B2
O'CONNOR ET AL., 1982
BOEHH, P.D., 1981
BOEHH ET AL., 1984
RUBINSTEIN, 1 1. El AL.. 1983
BOEHH ET Al , 1984
O'CONNOR ET AL.. 1982
O'CONNOR El AL., 1982
O'CONNDR ET AL., 1982
BOEKM El AL., 1984
BOEHM, PD., 1981
BOEHH El AL., 1984
STORET
SHERNOOD, H.J., 1982
YOUNG, D.R.. I9B2
BRETELER.R., ET AL., 1983
EISLER, R ET AL., 1977
3 STEIHLE ET AL., 1982
BRETELER.R., ET AL., 1983
EISLER, R. ET AL., 1977
YOUNG, D.R., 19B2
4.12
-------
TABLE 4.3. (Continued).
!"!E. .l^4T_[™ CONIAHINANT CONCENTR UNITS HE
NY ARTHUR kill IES|) .„ m/(B
NY NEM YORK BIGHT 'DREDGE SPOILS' LEAD 147 BG/IG
NY LONG ISLAND SOUND BRANFORD HARBOR LEAO 265 flG/'G
NY NEM YORK BIGHT 'SEMAGE SHE' LEAD 173 nG/IG
NY HEM YOPK BIGHT. SEMAGE SLUDGE LEAD IV «/r6
NY NEM YORK BIGHT: DREDGE SITE LEAD 141 w/rG
NY UPPER NEN YOPK BAY LEAD |'| Bf-,6
NY HEM YORK BIGHI. SLUDGE SHE LEAD i;t> nG/KG
NY NEM YORK BIGHT SEMAGE SLUDGE 1URPSITE NEFCURY 1 31 mm
NY KEM YORK BIGHT: SEMAGE SLUDGE NICKEL 29 KG/rG
NY NEM YORK BIGHT 'SEMAGE SITE' NlCkEl 23 US/KG
NY HEM .ORr BIGHT 'WEOSE SPOILS' NICKEL 25 n/tl
NY NEM YORK BIGHT: DREDGE SPOIL DUflPSITE IIICrEL » ni/>6
•< NEM lORK BIGHT: DFEDGE SITE NICIEl -4 n£/l6
NY RARITAN IAY ,||CHEL -j Mfts
«Y KEM YOP> BIGHT: SLUDGE SITE NICHEL 24 KG/KG
•I NARmtGANSETT BAY ruonMiim
m RHODE ISLAND SOUND DUHPSITE ctwn ** "^''^
HI Fli iciuin RQHIUH 12 NG/KG
jjl glL CHRDfllUH 13 «6/r6
(HwnHoMatlT JAY COPPER 5ftrt Btc/vc
•1 PROVIDENCE,,*, I" £ *
Rl NMPAGANSETI BAY N1[rEL ;, ^ll
Rl PROVIDENCE RIVER BIC(EL 5, „,,„
II SAN LUIS PASS MH . 06B J°,;°
II CORPUS CHRIS! ER HARBOR ARSENIC 33 9 KG/KG
II CORPUS CHRISII HARBOR CADHIUN 63 Kill
II GULF OF HEI1CO SHELF CHROHIUN 49 KG/KG
II FREEFORT SHIP CHANNEL CHROHIIW „ B6/K
H HOUSTON SHIP CHANNEL LEAD 207 flG/tG
II CORPUS CHRIST! CHANNEL LEAD 316 KG/KG
II S.E. POINI COBFORI, CO! BAY KERCUPY | i nB;rG
II ARANSAS PASS, TURNING BASIN flERCURY , «,„
II SAN ANIONIO BAY. VICTORIA CHAN1EL flERCURY 2 36 flE/KG
II COPFUS CHRISTI, INNER HARBOR flERCURY ' 2 HG/rG
II ESFERITO SANTO BAY BtRCUPy , „, ™/|
II ARANSAS F'SS TURNING BASIN HERCURr I s« MJ/K
H FREEPOPI SHIP CHANNEL NICKEL '44 NG/KG
II IEIAS CITY CHANNEL HIOEL 48 KG/KG
II HOUSTON SHIP CHANNEL ll(m ,' "™
II GULF OF NEIICO SHELF NICrEL 29 KG/KG J
H CORPUS CHRISM. INNER HARBOR ZINC 1070 flG'K
II FREEPORI SHIP CHANNEL 2Ire "., ","
MA PUGEI SOUND: OUTEP ELLIOTT BAY PAH j 9 «.„ ,
MA FUGET SOUND- ELIOI! BAY PAH i '3 M/KB
MA FUGE! SOUND, SM OF NORHANOR FARr PCBS 0 33 ffi/KS
MA ELLIOII BAY, PU6ET SOUND PCBS °0. ™ r '
•A PUGEI SOUND: DUMANISH MATERMAY FCIS 0.3 «G/r6 1
•A PUGET SOUND: SEATTLE MATERFRONT FCBS 0.3 TO/KB I
MA HARBOR ISLAND, EAST END. FUGET SOUND FCBS 0 374 Kin
MA ElllOT BAY prjU j_j2j IKIU i
MA DUMAHISH MATERMAY. FUGET SOUND FCBS 0 31 KG/KG
MA FUGET SOUND: BUDD INLET ARSENIC 98.5 HE/KG
MA PUGET SOUND: ELLIOTT BAY ARSENIC «3 NG/KG
MA PUGET SOUND: SINCLAIR INLET CHROIHUfl 61 HG/rG
MA PUGET SOUND: COmEKEKNI BAY CHROHIUN 31 H8/KG
MA OUMtfllSH RIVER ESTUARY CWOfllUH ,J M/,B
MA PUGET SOUND: FORT MDISON CHRONIUfl 34.5 TO/KB 1
•A PUGET SOUND: CASE INLET CHRONIUN 37 NG/rG 1
MA FUGET SOUNl: ELLIOTT BAY CHPOHIUfl 42.5 I-G/KG
MA PUGEI SOUND: BUOD INLET CHPOHIUN 4T KG/KG
MA FUGEI SOUND: SINCLAIR IHET COFFER 140 KG/KG
» ELLIOT BAY LEAO 310 KG/IG
MA FUGET SOUND: SINCLAIR INLET flERCURY 1.03 KG/KG
MA BElllNGHAN BAY flERCURY | nG/KG
W FUGEI SOUNl: CONflEKEHENI BAY NIUEl 27 flG/KG
•A PUGEI SOUND: BUDD INLET NIUEL 43 1G»G
MA PUGET SOUND. ELLIOTT BAY IIICrEL 43 KG/KG
MA PUGE! SOUND: CASE INLEI IIICKEl 33 KG/rE- 1
•A FUGEI SOUND. SINCLAIF INLET NICKEL 4? 5 ta/tt
MA PUGET SOUND: FORT MDISON NiCkEL 3: flG/KG I
MA DUMAfllSH RIVER ESIUARY NICKEL 21 1S/rG
AN BED. RANGE MI
I 220-1100
n-\J"
1't
104-233
•3 0
,
0.18-4.90
13-37
3-33
/'
>.-30
" Jl
13-81
I 0. 430-28.830
2.0-130.0
1 0-5.0
10-23
I 339-8037
0.214-3.79
1
i 0.13-1.4 :
0.099-0.67 ]
0.16-0.69 3
i :
3
I 0.15-2.4 !
57-140
1 84-280
I :9-72
I 26-59
I 29-57
21-53
I 28-70
I 33-50
1 47-180
1 2.3-630
1 O.P2-I.9
I l'-64
I 35-48
1 24-38
19-47
I 36-33
1 20-23
SIAT. |
Z
'
2
2
»
•
2
2
2
2
2
«
2
'
2
2
2
2
2
2
:
-
*
2
2
2
•
2
2
2
2
2
2
2
2
2
2
2
1
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
A
2
TFECT REFERENCE
3IOREI
EISLER. R. ET Al., 1977
DONS 1 FITIGEPALO, 1980
EISIER, R. El Al., |977
.2.3 STEIflLE ET AL., 1982
rOUNG, D R., I9B2
2 BPEIELER,"., El Al., 1985
YOUNG. D.R , 1982
TlflOTHV ( GRAVES. 1982
2,3 STEIfllE ET AL., 1982
EISLEP, F. ET Al., 1977
EISIEP, P. El Al , 1977
2,3 STEIKLE ET AL., 1782
fOUNS. D.R., I9B2
2 BPEIELER, R., E' AL., 1985
YOUNG. D.R . I9B2
EISLER, R ET Al , 1977
ElSlfP, R ET Al , 1977
EISIER, F ET AL., 1977
GOIDBEFG ET AL., 1977
EISLER. F. El AL., 1977
GOLDBERG El AL , 1977
EISIER, R El Al., 1977
LARSON ET Al , 198!
STORE!
EISLER, R. El AL., |«77
EISLER, R. El Al., 1977
«EFF, ET Al., 1978
NEFF, ET Al., 1978
NEFF, ET Al., 1978
STOPET
STORET
STORET
STORE I
STORET
STOPET
NEFF, El AL., 1978
NEFF, E! AL., 1978
NEFF, ET AL., 1978
EISIER, R ET AL , 1977
STORET
NEFF, ET Al., 1978
MIINSET AL., 1980
HAIINS ET Al , 1980
STORE!
STOPET
flAlINS ET AL., 1980
HALINS ET Al., 1980
STORET
LONG. 1982
STOREI
HAL INS ET AL., 1980
IIAIINS ET AL., 1980
HAIINS ET AL., 1980
HAIINS ET AL. 1980
SHERMOOD, n.J , 1982
IMLINS ET AL. 1980
HAIINS El AL. l«80
HAIINS ET Al. 1980
MIINS El Al. 1980
flAlINS ET Al. 1980
IMG, 1982
HALINS ET Al., 1980
LONG. 1982
MIINS ET Al., 1980
HAL INS ET Al., 1980
flAlINS ET Al., 1980
HAIINS ET AL., 1980
MLINS El Al., 1980
HAL INS El AL., 1930
SHERKOOD. H.J., 199:
4.13
-------
resulting from sediment contamination, 3) the elimination of a species
as a result of sediment contamination, and 6) notation if biological
effects were not mentioned in the publication or report
• Reference, allowing identification of the report using the
bibliography included with this workshop document.
Table 4.1 includes the marine sites with the highest concentrations of
the chemicals of interest, based on the presence of one or more chemicals
considered in this report at levels exceeding ten times the preliminary
sediment threshold value as defined in Table 2.1 of this report. These areas
include the Puget Sound region in Washington; the Corpus Christi area in
Texas; the Providence River in Rhode Island; the New York Harbor region;
Baltimore Harbor in Maryland; Boston Harbor and the Charles River in Boston,
and the Acushnet River in New Bedford, Massachusetts; Blackrock Harbor,
Connecticut; and the California Sewage Sludge Outfall area off Palos Verdes
Peninsula. Tables 4.2 and 4.3 are lists of coastal areas which contain
contaminant levels exceeding threshold values by 3-10 fold and 1-3 fold,
respectively. All sites are listed alphabetically by state. Based on this
data set, areas of sediment quality concern appear to be localized; the vast
majority of marine sites are relatively unpolluted or unstudied. A more
extensive data search should be conducted to substantiate these preliminary
conclusions.
4.14
-------
5.0 GEOGRAPHIC DATA
5.1 OVERVIEW
As described in the methodology section, freshwater and marine/estuarine
data were taken from the tabular listings and placed on maps at two scales -
national and regional. The data shown on the maps consist of Level 4 and all
or a portion of the Level 3 data. Map locations for the data points are
approximate. The regional maps allow further spatial detail and resolution of
areas containing densely clustered points.
5.2 FRESHWATER DATA
5.2.1 Metals
As will be apparent, the geographic distribution of the high
concentration areas is distinctive for each of the contaminant groups. As
Figure 5.1 shows, the metals data are predominantly in the eastern portion of
the country. This distribution reflects the higher density of older urban
areas and more industrialization. In particular, the major areas for the high
metals concentrations are the following:
• The Northeastern coastal areas (EPA Regions I, II, and III) including
portions of Massachusetts, Connecticut, downstate New York, New
Jersey, southeastern Pennsylvania and Delaware. The clustering of
data points in New York, New Jersey and Massachusetts may be viewed
more clearly on the respective regional maps (Figures 5.2 and 5.3).
With the exception of copper (which may be due to the smaller data
base available for this chemical), all seven metals are present at a
number of sites.
• Southern Michigan, central and eastern Ohio, western Indiana and
Illinois in the Chicago area (EPA Region V). The clustering of points
on the western and southwestern portions of Lake Erie is better viewed
on the regional map for Region V (Figure 5.4).
• The Gulf and southeastern states (EPA Regions IV and VI) exhibit
clustering of data but have a more dispersed distribution than the
previously discussed regions. Tennessee, Florida and eastern Texas
have the largest number of locations. Alabama, Georgia, Mississippi
and New Mexico have relatively few locations (Figure 5.5).
5.1
-------
FIGURE 5.1. CLASSIFICATION LEVELS FOR METALS
-------
01
I
SYMBOL
•
0
it
**
•
D
A
A
T
V
*
o
f
0
V
0
CHEMICAL
Lead
Lead
Arsenic
Arsenic
Mercury
Mercury
Zinc
Zinc
Nickel
Nickel
Copper
Copper
Cadmium
Cadmium
Chromium
Chromium
RANGE (IN MG/KG)
1320-19000
396-1319
330-6800
99-329
8.0-40000
2.4-7.9
7600-90000
2280-7599
200-280000
60-199
1360-7500
408-1359
310-19300
93-309
250-1100
75-249
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
50
100
150
.•RHODE ISLAND
CONNECTICUT
200 Miles
FIGURE 5.2. REGION I
CLASSIFICATION LEVELS FOR METALS
-------
Ul
I
SYMBOL
•
0
*
•6
•
D
A
A
T
V
•
0
A
0
•
0
CHEMICAL
Lead
Lead
Arsenic
Arsenic
Mercury
Mercury
Zinc
Zinc
Nickel
Nickel
Copper
Copper
Cadmium
Cadmium
Chromium
Chromium
RANGE (IN MG/KG)
1320-19000
396-1319
330-6800
99-329
8.0-40000
2.4-7.9
7600-90000
2280-7599
200-280000
60 199
1360-7500
408-1359
310-19300
93-309
250-1100
75-249
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
100 ISO 200
t
FIGURE 5.3. REGIONS II, III
CLASSIFICATION LEVELS FOR METALS
-------
01
I
Ul
SYMBOL
•
O
*
-------
01
1
°" SYMBOL
•
O
it
£
•
G
A
A
T
V
•
o
4
0
•
o
CHEMICAL
Lead
Lead
Arsenic
Arsenic
Mercury
Mercury
Zinc
Zinc
Nickel
Nickel
Copper
Copper
Cadmium
Cadmium
Chromium
Chromium
"v y v
\_r
RANGE (IN MG/KG)
-_ : _>
1320-19000
396-1319
330-6800
99-329
8.0-40000
2.4-7.9
7600-90000
2280-7599
200-280000
60-199
1360-7500
408-1359
310-19300
93-309
250-1100
75-249
so iga IM
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
j
FIGURE 5.5. REGIONS IV, VI
CLASSIFICATION LEVELS FOR METALS
-------
• Large sections of the central U.S. have no significant concentration
of sites. These areas include EPA Regions VII and VIII. These areas
are^also relatively far from major urban-industrial centers (FlgJre
• The Pacific Northwest (EPA Region X) has a cluster of sites in
northern Idaho and eastern Washington along the Spokane River in the
vicinity of Coeur d'Alene Lake (Figure 5.7).
t The southwestern U.S. (EPA Region IX) contains several clusters of
points (Figure 5.8). One of these clusters is in southwestern
Arizona, one is in Nevada in the vicinity of Lake Tahoe, the Truckee
River, and Lahontan Reservoir and a third is in the Los Angeles area.
Cadmium and mercury are found particularly in the Sacramento and San
Joachin Valleys and the San Francisco Bay area.
5.2.2 Pesticides
The national geographic distribution of pesticide locations is shown in
Figure 5.9. The data are more uniformly distributed across the country than
was the case for the metals. The pesticides distribution appears to reflect
heavy agricultural usage areas although manufacturing or disposal sites are
also present. Specifically, the major areas for elevated pesticides
concentrations are the following:
0 New Jersey and western Pennsylvania have a large number of sites of
high chlordane and DDT concentrations. This distribution probably
reflects a combination of use and manufacturing areas (Figure 5.10)-
smaller numbers of points are shown in upper Maine, Vermont, and
Massachusetts (Figure 5.11). Upstate New York also contains locations
near Lake Ontario's southern shore.
e The largest concentration of sites in Region V is in Michigan.
Chlordane, toxaphene, heptachlor and aldrin are the most common
pesticide chemicals present particularly in the southwestern portion
of the state and in the extreme northeastern portion near Lake Huron
(Figure 5.12). Smaller clusters are present in northeast Ohio and the
Chicago-Gary, Indiana industrial region.
• The southeast and Gulf Coast states contain the largest percentage of
the locations, with the North and South Carolina, Georgia, areas along
the Mississippi and in eastern Texas being the most tightly clustered
(Figure 5.13).
0 As was observed with the metals, the Great Plains and Rocky Mountain
regions contain very few locations (Figure 5.14).
5.7
-------
01
I
oo
SYMBOL
•
0
*
•fr
•
a
A
A
T
V
•
a
•
0
•
0
CHEMICAL
Lead
Lead
Arsenic
Arsenic
Mercury
Mercury
Zinc
Zinc
Nickel
Nickel
Copper
Copper
Cadmium
Cadmium
Chromium
Chromium
RANGE (IN MG/KG)
1320-19000
396-1319
330-6800
99-329
8.0-40000
2.4-7.9
7600-90000
2280-7599
200-280000
60-199
1360-7500
408-1359
310-19300
93-309
250-1100
75-249
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
ill 1IKIIM 200 Mill
FIGURE 5.6. REGIONS VII, VIII
CLASSIFICATION LEVELS FOR METALS
-------
Ul
YMBOL
•
0
*
•Cr
•
D
A
A
T
V
•
0
t
0
m
0
CHEMICAL
Lead
Lead
Arsenic
Arsenic
Mercury
Mercury
Zinc
Zinc
Nickel
Nickel
Copper
Copper
Cadmium
Cadmium
Chromium
Chromium
RANGE (IN MG/KG)
1320-19000
396-1319
330-6800
99-329
8.0-40000
2.4-7.9
7600-90000
2280-7599
200-280000
60-199
1360-7500
408-1359
310-19300
93-309
250-1100
75-249
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
XI
FIGURE 5.7. REGION X
CLASSIFICATION LEVELS FOR METALS
-------
I
l-t
o
SYMBOL
•
0
*
-------
-------
un
I
N>
SVMBOL
•
0
*
it
•
D
A
A
T
•
CHEMICAL
Aldrin
Aldrin
Heptachlor
Heptachlor
DDT
DDT
Lindane
Lindane
Chlordane
Toxaphene
RANGE (IN
0.210-25.66
0.063-0.209
0.200-3.33
0.060-0.199
0.060-140.0
0.018-0.059
0.120-1.19
0.036-0.119
0.20-48.1
0.20-19.5
MG/KG)
•NEW JERSEY
**y
DELAWARE
RYLAND
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
100 IbO 200 Mile
f
FIGURE 5.10. REGIONS II, III
CLASSIFICATION LEVELS FOR PESTICIDES
-------
MASSACHUSETTS
SVMBOL
•
0
*
£
•
D
A
A
T
•
CHEMICAL
Aldrin
Aldrin
Heptachlof
Heptachlor
DDT
DDT
Lindane
Lindane
Chlordane
Toxaphene
RANGE (IN
0.210-25.66
0.063-0.209
0.200-3.33
0.060-0.199
0.060-140.0
0 018-0.059
0.120-1.19
0.036-0.119
0.20-48.1
0.20-19.5
MG/KG)
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
JO
SCALE
100
150
'RHODE ISLAND
CONNECTICUT
200 Miles
FIGURE 5.11. REGION!
CLASSIFICATION LEVELS FOR PESTICIDES
-------
Ul
I
SYMBOL CHEMICAL RANGE (IN MG/KG>
•
0
*
•fr
•
n
A
A
*
4
Aldrin
Aldrin
Heptachlor
Heptachlor
DDT
DDT
Lindane
Lindane
Chlordane
Toxaphene
0.210-25.66
0.063-0.209
0.200-3.33
0.060-0.199
0.060-140.0
0.018-0.059
0.120-1.19
0.036-0.119
0.20-48.1
0.20-19.5
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
FIGURE 5.12. REGION V
CLASSIFICATION LEVELS FOR PESTICIDES
-------
Ul
I
H
Ln
SYMBOL CHEMICAL RANGE (IN MG/KG)
•
0
*
-------
MBOL
•
0
*
if
m
a
A
A
T
•
CHEMICAL
Aldrin
Aldrin
Heptachlor
Heptachlor
DDT
DDT
Lindane
Lindane
Chlordane
Toxaphene
RANGE (IN MG/KG)
0.210-25.66
0063-0.209
0.200-3.33
0.060-0.199
0.060-140.0
0.018-0.059
0.120-1.19
0.036-0.119
0.20-48.1
0.20-19.5
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
Ui
i
FIGURE 5.14. REGIONS VII, VIII
CLASSIFICATION LEVELS FOR PESTICIDES
-------
* lUfnJf KiC N?rth^st locations are confined to a small number of
points along the Columbia River (Figure 5.15). "u'noer or
• The states of California, Nevada and Arizona are densely clustered
KSri'S's k*^ff iffi.2: ^J?^N£ ° SI.
are near Lake Tahoe, the Truckee RlSer and ?he JKonUn Rese^olr? *
of
5-2.3 Cyanide. PAHs. PCBs. and Phthalates
This grouping contained few data points. The chemicals are present at
elevated concentrations in only a small number of areas (Figure 5.17). The
two principal contaminants are cyanide and PCBs. The major regions for high
concentrations of these chemicals are:
• New Jersey, Connecticut and Rhode Island contain the highest
concentrate of sites in the Northeast (Figures 5.18 and 5.19)
in the sediments of Michigan water bodies was frequently
noted; PCBs and cyanide were found less frequently in northeastern
Ohio and in the Chicago-Gary region (Figure 5.20)
• The southeastern U.S. contains a scattering of points, particularly
PCBs and phthalates, but without clustering in a small area (Figure
• Regions VII, VIII and X have almost no sites (Figures 5.22 and 5.23)
SSnAi?35
Arizona (Figu
contamination.
* SSnAi?35 S f?W™lteSMScattered across Nevada« California and
Arizona (Figure 5.24). Most of these are indicative of PCS
5.17
-------
Ul
I
00
MBOL
•
0
*
it
m
D
A
A
T
t
CHEMICAL
Aldrin
Aldrin
Heptachlor
Heptachlor
DDT
DDT
Lindane
Lindane
Chlordane
Toxaphene
RANGE (IN MG/KG)
0.210-25.66
0 063-0 209
0.200-3.33
0.060-0.199
0.060-140.0 .
0.01B-0.059
0.120-1.19
0.036-0.119
0.20-48.1
0.20-19.5
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
200 Mi...
FIGURE 5.15. REGION X
CLASSIFICATION LEVELS FOR PESTICIDES
-------
'MBOL
•
0
*
ALASKA
HAWAII
^- {>
FIGURE 5.16. REGION IX
CLASSIFICATION LEVELS FOR PESTICIDES
-------
FIGURE 5.17. CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
I
ro
MASSACHUSETTS
MBOL
•
0
*
it
•
D
A
T
V
CHEMICAL
Oiethylphthalale
Diethylphthalate
Dimethylphthalate
Oimethylphthalate
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE (IN MG/KG)
12 8-30.0
3.84-12.
19.6-30.0
5.9-195
2.8-100.0
0.84-2.7
1.0-98400
10.0-182.0
3.0-9.9
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
\^RHODE ISLAND
CONNECTICUT
50
SCALE
100
150
200 Miles
FIGURE 5.18. REGION I
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
I
co
to
'MBOL
•
"
*
it
m
a
A
T
V
CHEMICAL
Diethylphthalate
Oiethylphthalate
Oimethylphthalate
Oimethylphthalate
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE (IN MG/KG)
12.6-30.0
3 84-12.
19.6-30.0
5.9-19.5
2.8-100.0
084-2 7
1 0-9840.0
10.0-182.0
3.0-9.9
DELAWARE
RYLAND
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
200 Miles
FIGURE 5.19. REGIONS II, III
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
01
I
M
U)
'MBOL
•
O
*
A
m
a
A
T
\7
CHEMICAL
Diethylphthalate
Diethylphthalate
Dimethylphthalate
Dimelhylphthalale
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE ON MG/KG)
12.8-30.0
3.84-12
19.6-30.0
5.9-195
2.8-100.0
0.84-2.7
1.0-9840.0
10.0-182.0
3.0-9.9
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
100 150 200 Milct
FIGURE 5.20. REGION V
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
Ul
M
SYMBOL
0
*
•
D
A
T
V
^N
CHEMICAL
Diethylphthalate
Diethylphthalate
Dimethylphthalate
Oimethylphthalate
PCB
PCB
Cyanide
Total PAH
Total PAH
^ \
\
\
RANGE (IN MG/KG)
12.8-30.0
3.84-12.
19.6-30.0
5.9-19.5
2.8-100.0
0.84-2.7
1.0-9840.0
10.0-182.0
3.0-9.9
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
FIGURE 5.21. REGIONS IV, VI
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
Ul
I
M
MBOL
•
O
*
ft
•
D
A
T
V
CHEMICAL
Diethylphthalate
Diethylphthalate
Dlmethylphthalate
Dimethylphthalate
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE (IN MG/KG)
12.8-30.0
3.84-12.
19.6-30.0
5.9-19.5
2.8-100.0
0.84-2.7
1 0-9840.0
10.0-182.0
3.0-9.9
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
FIGURE 5.22. REGIONS VII, VIII
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
'MBOL
•
0
*
A
•
P
A
T
V
CHEMICAL
Dielhylphthalate
Oiethylphthalate
Dimethylphthalate
Dimethylphlhalate
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE (IN MG/KG)
128-30.0
3.84-12
19.6-30.0
5.9-19.5
2.8-100.0
0.84-2.7
1 .0-9840.0
10.0-182.0
3.0-9.9
Closed Symbol* Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
SCALE
200 Milts
FIGURE 5.23. REGION X
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
Ul
I
MBOL
•
O
*
it
m
n
A
T
V
CHEMICAL
Diethylphthalate
Diethylphthalate
Oimethylphthalate
Dimethylphthalate
PCB
PCB
Cyanide
Total PAH
Total PAH
RANGE (IN MG/KG)
12.8-30.0
3 84-12.
19.6-30.0
5.9 19.5
2.8-100.0
0.84-2.7
1.0-9840.0
10.0-182.0
3.0-9.9
Closed Symbols Represent Level 4
Open Symbols Represent Level 3
Map Locations Are Approximate
PACIFIC OCEAN
SCALE
100 ISO 200
ALASKA
HAWAII
FIGURE 5.24. REGION IX
CLASSIFICATION LEVELS FOR
PHTHALATES, CYANIDE, PCB'S TOTAL PAH'S
-------
6.0 OBSERVATIONS AND CONCLUSIONS
6.1 FRESHWATER
Several general conclusions can be drawn from the results of this survey:
• "[he national maps indicate a clustering of a variety of chemicals at
certain sites rather than a general scattering of data. In general,
coastal areas are the most noticeably affected regions. New York, New
Jersey, Michigan, Arizona, Nevada, Washington and California contain
areas which repeatedly appear on the national maps. This distribution
indicates a broad spectrum of contamination within certain areas.
• The limited analyses of station-by-station data for the top 200
measurements indicate that: (1) areas are widely scattered around the
country justifying development of sediment criteria on a national
basis, and (2) the highest contamination levels for many chemicals
represent potential "hot spots" rather than generally high
concentrations over a broad area.
• Metal concentrations were, for the most part, classified in Level 1
Only nickel, which had 42 percent of the data in the upper three
concentration levels, was an exception. In situ and bioassay data
suggest a need to reevaluate water quality criterion derived threshold
values.
• Almost all of the polynuclear aromatic hydrocarbon data were
classified in Level 1. A wide span exists between the currently
suggested threshold levels and even the highest observed
concentrations. The biological impact data suggest a need to
reevaluate threshold levels.
• A significant percentage of phthalate data fell in the higher
classification levels~36 percent in the case of diethylphthalate and
35 percent for dimethylphthalate. However, no biological impact data
were found to indicate a need to review threshold values.
• The vast majority of the pesticide data were in the Level 1 range.
Chlordane, DDT, and toxaphene had 16, 7, and 14 percent of the data
points in the Level 2 range, respectively. Biological impact data are
needed to evaluate threshold levels.
• The PCB data were distributed with 18 percent of the data above
Level 1 using the sediment-water partition approach. However, only
0.4 percent would be located in Level 2 at the highest proposed
threshold value using alternative criteria. Biological impact data
need further evaluation.
6.1
-------
• Much of the available In iHu or _m vivo data were inappropriate to
«! ?h^-6 ?ediment/el?ted toxic eFfeEts because parallel measurements
othpr h!o?n 9°n«njjat1ons and biological species distribution on
other biological effects have not been made.
6.2 MARINE/ESTUARINE WATERS
Based on the literature survey conducted to gain a national perspective
of the sediment quality status of marine and estuarine sites, the following
general conclusions can be drawn:
• Only a limited number of sites contained the chemicals of interest at
high concentrations. This inventory include several of the Puget
Sound waterways; Corpus Christi Harbor, Texas; the New York Harbor
region; Baltimore Harbor; Boston Harbor and New Bedford Harbor
SS*?"8!^?? Bla$krock Harbor« Connecticut; and the California
sewage outfall system of Palos Verdes and part of San Francisco Bay.
* «SSTiSaJSi.Jf m^ co"cern were those that exceeded the provisional
sediment threshold values at several coastal locations. These
thtrinvPnJnrJUnl tOXi£ T6**!8' W PCB* and DDT' Other chemicals
e
PCB* and DDT' Other chemicals in
dld not reach or exceed the f1rst cut
The marine/estuarine survey was based on a very limited data base. A
more detailed literature search may reveal additional chemicals of
major concern. Important data gaps in this review exist for the
New ?orJ9H^°UndH:R-P?? and.other aromatic hydrocarbons outside the
New York Harbor and Bight regions; several pesticides; all of the
other chlorinated hydrocarbons except PCB; and all the phthalates.
Threshold concentrations for chemicals in sediments based on sediment-
water equilibrium partitioning are probably set too high for the
majority of chemicals considered, most notably for PAH compounds and
metals. This over-estimation was best illustrated by the discrepancy
between biological effects observed in New York Bight sediments
despite corresponding sediment contaminant concentrations of
inventoried chemicals which rarely exceeded threshold biological
effects levels.
6.2
-------
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7.6
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APPENDIX
TABLE GENERATION AND INTERPRETATION
The tables contained in this appendix were obtained from a computer
tape listing STORET data on solid matrix samples for 25 chemicals. Although
an attempt was made during the generation of the tape to eliminate all but the
sediment data by elimination on the basis of sample type (sediment, sludge,
and so on), a quick review of the tables will reveal that this process was'not
entirely successful. For example, the highest concentrations of several
metals were clearly data on sewage treatment plant sludges that were not
correctly classified within STORET. The data on the tape were sorted by
chemical from the highest concentration to the lowest. These measurements
were then manually examined to eliminate non-sediment data such as sludges and
solid wastes of various types prior to map preparation.
The 200 highest analytical measurements were examined further to
produce a set of concentration measurements at individual locations for
transfer to the maps. The monitoring stations where multiple measurements
were made are shown in the table as a single location with a mean
concentration and the number of measurements (N). When transferring data to
the maps, latitude and longitude coordinates were used to decide whether
points represented a single contaminated area or multiple locations. If
measurements were separated by less than a few seconds of latitude or
longitude, they were represented as a single map point. For this reason, not
all of the tables contain the same number of points as do the maps. Accuracy
of transfer of the data to the maps was assured by cross-checking
approximately 10 percent of the sites to determine that they were at the
correct locations. In addition, there may be more data in the tables because
a second computer run was made to compute data for additional locations than
those sites used for the 200 highest measurements used to generate the maps.
A-l
-------
TABLE A-l.
FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF COPPER.
CONCENTRATIONS A«t IN nig/kg.
LOt
m
1
2
j
6
tf
10
II
U
11
1H
16
17
19
22
25
2ft
2«
2V
r S
ro ti
33
JM
Ji
Jb
JJ
JU
41
Ml
Mb
HI
MO
IV
bU
41
Si
Ss
1Mb 1Akb:> M.K1H Ul d A HI, IK *Jr>Lt
LArt NHUllllb Nk HuTIUMOIIU LlllLtbt
UAT! t 5 l<» TLlAHliAkA IhM
iUUTH Uf !>AN bltU< tHIl trflkANtF
LAKt HHODUibb • VflUL^t INALllVt 7S
LA 111 fhAHCIS CAit ku liAH
LARI htlUUhiJi t bHUIUI kH bAlOk M.
LAftl hHOUltl 5S kH AftHUkbT IkALTIIL 1
LAM (JAP*. Mh UAf.
CIKAkHOk htfkfl MIDH CUTHhli.
LAM VMAN(.i:> CAM Nfc »LH CklL*
LtkL OAhK kM fOLlllLH LU
HOILk Ch kk kUTttt ktUiiDTOH ( LC IriJLT
LOMl, CBtER NL1U hut It I NlVLk ^»-Hili(.b
PlLfcck »-K • iillbM NH CATALOOLMtt 1
URL SAKAAAKt* Af UAH
flCCALLlAfcl) CH kk V4LUISI Jk«L'TJ*L 7
Llkl MHUbHiSS • !iNl»OI Nk lihLILL kt
• JSsnum kivik if NtkiuN MI
11*1 1 CHELA SL Of THAMIAN* AHA
BIChAND.sOk CKFIEK k ik 16UO Nh bUkkb
LAktb CK * Sblfc12 kit KJLtEhS kC 1*A
LOktk C> * SklbOl DM nukbAkTON ML H
BIKL CkILK MtAH LAIOOiA
ST HiAMlli kJHIk AT LAKt C1TI AH
BOC1I kltlfc kEAk kCkklJUU. kl
COTTOkkOOO LkEEk AT '. UAkl)
SHACAOVI'N CMLEK k Cf 511 AC A OIL k Ak»
lllUCHAMkfcL HURTH Ul HAI ISLl
kjoucnroBK ct HH CATALLOCHEI »t IKAC
HOLkl H REAR OAlbOkO kC lk»LT-7<08l
POTIAU kULH Mtkk HbA«LkEh
CACkr Slfth kk
TIKUkZA hIVtk ktAh TM1ST Ak».
UUTCH UUFTALO CK -l «t HUT .1)0 IMkCl
BAIOU MtTU MkAk LUkOKt. Ahk.
LITlLh CttALUUChLL LA kk <. A1 ALdOCKL
POTIAU kivth vtAk luki :niTH,AkK
AklAk^kb klttR kttk t.U-kuCIt
kfkl GkAhAft LUCr./UAn kFAH ikULk
ktOMIO kl«t« NbAk ft- <. ibMik
lALAMAbH Lk 1.2 nl US SklltH IkltT-
10V IDS kIST U» Ulk lAkTON kALH
A1AHKII1 Hlftk ktAk AklLEH^
ILLlkOlS kl*LN ktAk lAHLKOlAlt
CALhUR LktLR HIST Ct lUIKAl kkk
it IhAHtlS k M Ul |ll LIMA kl K
CAlALCIOXMlt \.HLLk ktAh l»M LUULIII 1
SUkTI T bkl AT MAVT HUUIS
DUI tUkk kf.lh nni. .
ttkl'lbHI'- kltLk ttMK llAHi.il/ltk
HrkMbHI1.. KIILH mAH IkdLA
hUCKI h * 1>I. HiUV kk Itlil'fc5» till l*iii
Al.k/UbAS klVtk Mtkfc HlhV.* *.JT»
LAI ItUKKIA
kUvTn CAhOLIM.
kutlll t-lkvH IHA
-------
TABLE A-l. (Continued)
5/
La
59
bO
61
63
61
65
bb
tl
b9
10
71
7J
71
75
76
77
7tt
7*
DO
61
bJ
BH
> 87
Btt
B9
90
91
92
93
96
97
9B
100
101
IC2
lull
105
106
10/
10(1
'"9
110
III
112
CAkAlilAk hlVLH Al (.ALtJk
Hlb HAIUU Nh Jl hurl AkK
LITIIt nlVtk NH fUKILA A UK
nliSISbllPI HlVtk AT HAHIIIU,
bAIPU LOUThl Nh JLhLlluk Clrl Al.
hi Ml I. a ILK A'l LATdllbA
llUIXAU IkLtK bdUfH (II U.rVILtL
kill ill H tfbhlHM* Nh UIHtEbt. kC lk«LT
HtU UVlh NtAil kAllhlnA
HIAMCHl MVtH kLAh HJI. IcIAH
bLUt KlVtH HhAN IllUc
COk (.Netft *T MAUhllA
SAL1 IOHK 01 AkHAKSAS hi Ail JtT
REP hIVhh NLAN UULUkllX.! AhH
BAIOU ULVlLN kh (.iHbUN. ARK.
CAChl kl>th MR LA .H, AhK.
MOtUf Hlltk UK AI.«-L« LIHt
NH1TL ft AT LI.D kU 1
FONT HUHAfcO PAPth Al UhEFk riAI. k|.
HEO H1VFH AT UtkALB. Ill
UlFt- FOhA NEAH Aki AD1A
AHH HMIR AT IIUHHAI LCM. II Akb bAn
NUHTH CABAI>IAH HIVtH klAH nAnlAH
BAIOO BAkTHOLOHtk kk JukKS LA
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50 1AHUS U/S Of CUAbT HkT Ikll'CE
LJTTLl HJVfctj HEAH lOAhf.L
SPAtllAH C N Of CHEkUME C1TI AH
__klTTJ,E BIS50UH1 HIV MR bllULIITOI
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LlfAkhUk hlVKH NtAh hll»FAL(.
klb K1IIR ktAH IlkhAL
ILLINOIS R1VLH .HI. (-.c,,!
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-------
TABLE A-l. (Continued)
LlUS
IIJ
111
IIS
lib
III
lit)
I2U
121
111
1J6
UB
m
130
Ml
bill lUkk MLAh .ILlil UN
ClrrANHON K1ILI. Al PMl.li:>
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ILUNOIb MAIUU kk VI UuVtk Ahk
kULIll IUHA U» mi khb HIVKk hi AH hi
CAkAblAk HJIEB Al bkl l>b» HOkT
llUllklCkkt CHI til Hk '..IhPlS AhH
• HHAkSAb HIIEB AT OA11U 11 IfckUI I.OC
5K Sk bB M.C. 14 !ik 101 In
CUJkAbRlA HItLk ktAk hLACKkbLL
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IlkOb fclVrk NB hbkBKILLt:, AHK.
IIUJ.btHhl HMI.H Al LTIHilAlt
-------
TABLE A-2. FRESHWATER REGIONS CONTAINING ELEVATED
CONCENTRATIONS ARE IN mg/kg.
SEDIMENT LEVELS OF LEAD.
2
J
V
b
o
d
V
10
II
12
M
Id
It
i f
III
20
22
io
f J0
in Jl
J2
Jr. »OhK NLAH MAChtTT. A 1 it .
• m .ifk1:!! ZINC IOOM I.OIFAIL
— lupin bALme m»m AT iiu^fc LAM
2400r ttk.il Ift 4tLLtN ILii
LOM ».LH HOLLOA Al JOILJN. HO
dAIUU TICHL. AT OLlHILk. L».
etlifc.hLd^li-JUST fr| ion r.uoso tl.
COLOIIhOi bu STV Al COLOhhUi UA CHA1
041 I.Akk»k C Nk NAhHl^bUHC UM
NUhhlNS SLOUCH OS-MMI
CHAkLtS I.J1> STf b|Ufc&Tt.b bLUUCt
MJL!>OII K>bt.«llull)
BHA7IL tkMn MEAh WAILS OK
AHKAkbAS hlVLk «T «HKAkSAb >.ITI
LAKJ |-HO»li,tllCl! NOnlM UI LAkt H.u»
Lilt HAPATO. SO IHDS »U ASOTIk ^T U
BO ML CAkAI.
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LA»L HAIA10. 100 INJb »H iLOTIk bT
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SAN .IALIN1U H-IlL nnlL'Ut
SOOhlb I.Mrh IN »Ull,IILf!. 41.
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7/Mu.U
l*dOG.b
1 11.00. 0
IOJOO.O
10300.0
bOOO.O
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bouO.ll
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3200.6
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229(1.0
2074.0
2000.0
2000.0
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isno.o
-------
TABLE A-2. (Continued)
Jl
I
a>
bb
bO
1 1
tJ
bb
bb
b4
btf
b'l
40
71
Ij
71
7b
74
70
79
el
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an'
bb
64
bl»
b9
90
VI
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101
IbJ
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104
lull
lu'i
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III
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SIIVII. lAki 11 IT ln(in h -.hl.hl
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LAki KAPATU, 70 IhDS IH JIT. rl, riAIN
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-------
TABLE A-2. (Continued)
Ui.li
I1J
111
lib
III.
II /
II''
120
1^1
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LAUt fltklUN
LAkl tHlt nilUTM 01 UTTnUA 1. 1VIR
HOKA L IHOUIT k. flUkA Lk fk" kUHlOk
L*k> Ihll BAUBH. 1 HAkKhL
L«M EMU HAL«^ IhAkMrL
MUP1H bkAkCH fi««CUL*b LhMik Al PHIL
LAK> IHI» HAUntk. IHAIIktL »tH UbtDbL
KLAfATH HIVeh IT K MK, rRIUi.1
LIKt KAl-Alu, iUJ.imi TO kiLLuy ISL
LAkl IHIt nOUTH U» HlV^k NAIblk
LAK» tnlL HAUNtl tllAkNIL
FOMIbT C1TI iTP SLUOUi
TALOhA LfctEl ULAN bTltlKH UK
SHUhVAl AtllUlO MtAh WATLhUO.. nn
OUAbAlUIL hl«KM AT SAk JObl. CALIF.
SPLkLth Ch Thlb. MTL J
-------
TABLE A-2. (Continued)
It,* him HIM Ml* Hltfch (IIAhNcL M 111 I, O» H
I7U LAM |H|» HAUfltL CHAfckLL TOLIU) HAI
171 JLlit HAI HARhUM A-l bbp 1AM U» 1 L 1 1
172 HIAIII LAkAL A1 HO..-J L :,/ I AT LAll
I/J MIArntUO h. AT rilLL '.HifPl; llf| o
1/4 MILMIN :,TI' AT kllbOk II L AT COklEHTL
Mt nakONLAhM.* hivth niLi O.H
17b HIVAIlKrHlUH ill- AT II IZAIIIIHTUk Tk
^*H A|i Art ^TP JIT (fhAHAH f'L f O TUfctt L H A
l/ll JUCIJR IhlLK AT Jdl-Ll*. nil
Mil "tfcfhH t«l..r«>i_ab«iit lAu/aijj. m .,
Ibl •'»:>i»lt' Htfct»N«l fl.htACH (HNL.Ik.V
lt>4 .tASlsJDf si). AT DHH HJINI »C"TO hi
IBM VAIift^VJLLt LUKE
l«i I2H1 ».A1T Ijl SAkUl HLOK ST fk
IBb LAM tMIL SAkUUtKI BAI KtSl O» COAL
III/ ItlLkKbT n»L iLUUbl
IBB LA bAPAlO. AI>Ph US IfbS fh SOUTH 7
IBS it JostrH.ii AT to ku HN HRJ^TUL
190 M10 DC LA PLATA Al TO A ALTA. tl
MATt
khH lUkR
CHIC
ktk lOkH
f L< klliA
PJLHICAk
M
-------
TABLE A-3. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS
CONCENTRATIONS ARE IN rig/kg.
OF MERCURY.
vo
1
I
t
1
ft
1
H
10
\i
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IS
Ib
17
18
20
it
2H
^*
JO
Jl
JJ
JJ.
JM
At
ib
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JH
,»*
MO
III
Mil
Mb
•41,
1.1
ID
bl
=••»
bl
bb
bb
hnlll.' Mktk-uLI. lilAMUL
HL1hl.l1 tl*rH
I'M hull 1,1 VI h
III LI; HAT
lAhlUk h. » HlVtl.VIH
ML* Nltlh Af (.ILLl^lt [>»f.
NAblLlVII 1 IIAI
ALAHO | AKt
LlhJ L«»t
nUKLLUIIkt h A1 H lib L 1, 1,1 lib 1
11LLA-JUJJJL !!LAh «Ah»l»ILLK
kAhULUI bAMUUll
AlUhUAI. hi AT tLI.ANTl' if,
Tuiiiurm hivLh AT ruuLunnt 1.111
UUTIALU IH »T AntnRAk HIV1H
liUUIULH tUi.tlt AT ntUlH
OtftUb H bi. Tl.tLHAHA I.JL.
SAkIA ANA hllLH .11 lOd fhtUll Unit
ALADU h kh LAlilAfhlA
UUULUtH IhHK AhOVt HILDtN LhlLK
SAR riiAktlbCU h. A1 LLIFTUk
MUUlMlih LHJtH BHUB nilLHOLIAMII UAMI
AMtHICAk H. AT MAIl^ AH.
Lm tRIt bAHOUuM BAT M/01MWn;i CO
COH-Ek Cktl.1 AH bl.Ulbth CHtLR
LAKt TAhOt IT '-*(.!, HAhhOfl
LAM LHie HAUnkk hAI NtAll IIP UP CL
LAhONlAN UAH
LOLC.hAUU kl»tR lit LOU fAhKtl. UAH
LAk» tHll AUUTH lit !>A«II LHIKK
LAM tHll. >,AkllUSKI HAI kfjl Ut COAL
LAKt tHll. r.AUflbl lliAlNtL
LAM t. bit. tA^T Ul bTllktl «*li|pf
LAKI MJt rAUnit LliAdhtl
LAHL tHIt flAllntl. CHAhkH TLLLUO II Ah
LAM Milt hUKhOf LnAhNtL
L»»t Fiiit. kuhTHti.r ur HUkc« thtAiik
LAM Lklt nAUnii tH«»kiL
LAM tHll HOUTH lif ^AkUU^kT b*l
. LAM MIL "-oUllmril (it BOUT H (.1 oi T
LAKt thlt IhlhtKh nllhUN AMI HthHILL
LAM toll flAUntt CHAkHtl 1)1 U LMI.IX.I
LAM tkll r.UDTH lit blONtl thrift IN
LihL LklL HLU1II lit blTLB (.1-Ktt.
LAM tilt kUiiTIi 01 I'UtT CLIKTON MAh
LAKf Lhll nilUIH 01 HUMJN HiVLh
LArt tkIL XAIllll-l LIlAkHLL Mr. tMtlll.t
LAM >., It HJIllllK. •! ut :.4NLU»I IAI
LAM Lhll SAKbU^nl hAr Kf\| oi n|.||i
LAt t (Hit tA:n|VUHA
AhlZUkA
CALlrUbHlfl
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H.10 j
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C II | (J q
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b 1 J J . 1
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1 llliM .C
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i. to i.o
lib'I.O
130b.li
1JU2.0
U76.*0
I/7J.O
1272.1
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1200.0
11/0.0
1110.0
ttJO.O
tJi.C.
l.tl.O
M6.0
MO.U
bflO.U
IfL.O
MV4.V
MllO.U
MHO.d
11,0.1.
UlO.t
M Ji.ll
-------
TABLE A-3. (Continued)
•Jl
'.'»
bU
v 1
bi
LI
bS
b7
6B
70
n_
u
7n
76
17
7b
74
60
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0 64
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Vi
vs
90
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101
102
tat
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LAM LllJt k» .1 ill IIUI.I H Uhil't-t. il'lll
LIKI 1*11 I-AkllOjM HA 1 NLAl VMilLI
LIU thlt kUiiTII (it HUMik HhtA*k*Ll
ktl) HOUR ILirS bol.lrt StCI.AT MAI Hi
LIRt Ltill kUhTHtA^T Ul COBllintN I'OH
LA hi Ffcll ItOkkOI IHAkkJl
LAM tnlf btltftth k*il> CArilL AkO CH
LAiit mil nouTH (Jl J"*N cmti.
LAkL I'HII 100TH Ul '.»klll Cliltk
LAkt IHlt kKAh fliLtkiU «UHU.tAbi Ul
Htll tiUOK tLtfb kUhlll bfctT.AT l-Af Ml
LlH» LhlL bOUIh.tbl (Jl »tLlt»b liLA
LAl» tNII !.A»l>USIlT HAT SOU'iH f>» JOH
Vim tkll HJT U> CAlAkllt l^LilU Hi
LftK» rHll.»(JHTIilt:.T 01 OLU .On A Mb t
LtVl LHll nokHDt i-tlANRkl.
BUOkl HthUlHiiB - -
LAfct FHll HOUTH III k!Vt!N HfclSIII
LOkG lbLANI> SOUHu
LAlt tkll HOkTH ui HUI.UH Hl»i.k null.
L*kl tBlt hLIUkkk DflhUU Akl> HUhON
ti»» ihit KAST ci cun:.unr« n>vtM l-L
LAHI IHlt NUhTH Of fOKT LUklOk HAk
l»KL KKU hUHTII 01' COOIEI CKKLK IIOU
LAIL tklt BIAN bAkUUbKI bOMIMi^tl) L
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LAKI thlt Slhl)Ubt« B11 IttAfc HUUU1 L
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Ltd KkJl CXST 01 OTTId CMlfK
LA lit "tHIl flUUfH Ul nutlll Cktth
bABlLL HOkb HHIliul
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LAHI Efcll 1ULCUO LUlbON ril>!>HIJIIb 00
Un»l.OII MJHOUL roh lilhL*i STI1
LAII tKlf tAbT Ul UTlm CrttLK
Ltlt LHll kUkTHLAM Ul PuKt CLIMIOk
kIChl.A»0 LkktU •. M. H«b NtAK Ult.h
U»L tkJf H£Ah HilhOK iUbllr Hi.Hi Chili
LAHI tK!>.HOUTH Ul Old kUHAkb CHIIX
LAI.L EHit roniiut rimni ILAUT EIFLUI
LAri can "ist or I-OKT ciikton <*ni
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thill
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1
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2
1
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31H.UOO
317.SUO
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310.000
300. 000
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290.000
270.000
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2bO.OOO
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200.000
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1 *#ti «U(JU
17V. 000
-------
TABLE A-4. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF ZINC.
CONCENTRATIONS ARE IN nig/kg.
I
3
t>
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II
1 4
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U
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FLA1 1. »»T«i-«ib (.blil (IU1IALL UUIj_LUH
Mill l.l Ih.m J->»h Tilt VlhDt l!l»U
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bl LuUFh (itLtm u Al •nAvlki.l, i
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lU.k.JfT ^1p
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4UOt»h bALLlh»*hHil>-S11tLNI VUltli
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JOHN OLtht SLUU..I
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ttlAH LAKK « LHISkIL flAHKfh If
kfkTUV* Cll kOHTH U» ntTNUPOLITAH AV
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lllbktbT HIC blUbbt
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-------
TABLE A-4. (Continued)
J>
ro
UH'j
bl
•jtl
fcU
bl
LUl
kTSl :,TI IL'I UA* MlH.t 'Ik Tl. tA;T Id
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-------
TABLE A-4. (Continued)
yfei_
in
lib
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120
121
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141
2» 142
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tlkTI.H thtlK Ml LOW H1NLKAL IIHAIIH
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ktNTLH tNttH DtAh SajlnMi!ll>. HO.
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JBi'r^M'iiLI! STP Al JACHSOkVILLl »L
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TOmi Chtlk AHOfl JUUIH. no
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SPOHAIIt. IkbllSTfclAL PAJII STP HF
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• THIIIS STP AT AlrtlkS AL TO '.KAN CM
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HOhlHllD tITI STP AT KtlHKHIAU C1TI
100 nil SOUTH or UAH
BAZODikJL STP
tllLLlMkHkH UA1
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t. *>IUt. LNk At MKNA Mr.TS IH- hAIM
UHT CRllK STP AT NASHV1LLL TN TO 01,
UOUtNUOU up AT KOLLIk'UOD FLA TU A
DLCUkAH STP SLUUCL SIT»
Hcmgvii c« ^tii or UOTCM KILLS
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LtbANUk STf AT LLbANOk TN lu HAIllUN
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100 fFLT NOHTN \'t 1SLAHD
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2270.00
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2233.00
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TABLE A-4. (Continued)
OKI
Lot
IbV LI) Ml)'. (.HhlVll IkktM MiPh kM k»)i l»
lit) nukkut sir AT nuftKbt M. TU kJiiiAkus
111 ml, Ctunk JIT..T Ukit UTILEI DJjii HA
IU ttriUlllt k.-blMH 1
IU HubMTAccii mttk At jtiFthji.* i»i 111
ll« COkAM.H> i-TV DIUkbTtD SLUUI t
11% UhlltLt b.-l)«blk ?
lie POlATu Ik 1.TP »T CillllH C» Tb PUTA
111 POkCJ Ck APPM U.Oi Ml «IU lllkt KITH
1/6 t lUSTIi IIIDDLt
l)« TSALA Al'Ofk L «k MC HtilttkbOk t
I«U CtftlEk IkCl* bllOtl LAktSIOI, «U
|t| nokt»»kTt)ii bf> AT nonCAitToi ki TU HI<
ItH IITlk-OUIAL PUkb II IT uUkE AthlS 1*
I«J l||tl.|klilti« lAVAt AIH STA SIP AT nit
IB* PASS* 1C K.LklU.a.Ur kJILLIILTUk MIAU
faa pun ST,| u bOAt AL TC SLU ci:ttk
IKt HA* LHttl
ibb' ciior.A itp IT Boviconm AI TU AIAH
1«9 PASbtIC k-Llll bk. AT Cl»fm Of »I. .
190 IKHAkl PAI IAVT MUfct VmAtLIL TU S
191 PkBPABCH HbHCklS BO 1 iLUWl
192 CO Dfc JO hltok k*T» KUOOa:; hUOkSO
H| ATRCIS SIP «O J AT ATktkU tA IU hill
m it rkoii • -tAni< i cm TU JHHE&UI tu
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IVl HAPI<( CM STP •» l»OIIAS»lltl HC Tu H
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199 S*ttT«ATkU STP »T SbtlTMATtk TN IU
JUO Cr«MA &TP AT UtRfctA AL TO PEA «l«t
IQI ABI-S IMttl 1H** I.H HI AbTP lllbtSTIU il-UDl.t
2uj msi PAJII ttJCH m.h SIP AT ntsT pAt
llili
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kiiuiLkii
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llhUUfcT
ittkblA
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kin JtkSCI
ALAIiAltA
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ALABAMA
• fir Jt«!irl
k»M Jtk^tl
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f lUkCIA
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WITH CAkUlIHA
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ILAbAIIA
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1799
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i ti^o*
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-------
TABLE A-5. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF NICKEL.
CONCENTRATIONS ARE IN mg/kg.
1
2
J
M
b
1
a
t
10
II
12
U
11
11
16
II
ta
19
20
21
22
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26
2?
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29
I 41
— • J2
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42
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111
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51
bi
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fUMTHUk blTltHl
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Hllilb H»lb DkSTIi lOkb Itl'tH.; Ill
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nkklTHOV blTTtlil
bOCCI bllUU Ilk kt lli1»lLl» , LI
HLI> t»l>lk lOOlt tl'i.1 UllLl.k U12>L;KI
run* BUI to it
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Llkkt.IICt.oUhl. HIP.. 11 tt«kr.m.lbUh<. 11
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-------
TABLE A-5. (Continued)
LIK
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TABLE A-5. (Continued)
UP.J
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lib
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119
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-------
TABLE A-5. (Continued)
— on*
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»L
-------
TABLE A-6. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF ARSENIC.
CONCENTRATIONS ARE IN mg/kg.
1
V
10
j~ —
1 J
11
• L
It.
) /
141
19
f)
21
Id
ib
i1>
n
"
JU
Jl
)t
m
Jb
j i
j»
JV
no
....,..,. ^
44
•H
lib
• u
ft
Su
il
•^ ^
j, j
^i
•,b
^ML.Unr JrMMil : LU|.(.t
jillllllh 1 k.^lL M1IULSL Mil
hlUfcM.Ak :.TI Sl.fhILA* till HILI kk.i h
VklMKf MtttkTIUk HlHt
lUkf Lit kft lUHTLK (..I- 111 kf "t.'.S
SrUMkr Jkl,U^TkJ«L P*Mk '.fl HI
bf * a Ul fc LJk«. Lkkf fcn S>.OU
lkL*»l> iniitK l-iftk c.l» m b^.i
IHil-ftAH MkK. kJ :.Tl
HI III l<*1
CHJIklf^ 1 IJ 1 ilV I.AH :,LUI)L|-
ik lUkklk (>» riklttrkrk Lirfc
CrtlthltJ LI1I ktf blul&ftil :>LUIK.L
NlLiikuOll tAKK Al 1 UOT Itlllbi fe
kOUStVELT L»I>L i*LT k. »Hfl
SUblMMtST hktkfU k*Kt;t'V*^ Uk nAlk S
HlkullALL ill Ik HlkbblLL.lLl
StLibUkl MJJL >.»nl LI
• FOikU H»tk »IH IT. C.IUSlk
PuTItU kltKH kl»h »UkT ^ntTb.kkk
I-01MU »If»k rik loftT -HJTH. «.
kiH.k»UkD Si* GIUkT fcOUihf»hl jAktl H
SlLMibal cit'SUH SluliCt
D^IVLK IkKtt kk thOITthS. »K
DOkktl C Ilk DUUkCkUfT VI
CHH'kUU Mr^T SOtlM «tbl nbl-JL
TtflklTI « It SHJ| • U| TNIM«IU
»L*H(J tnkt
ILLIkUl^ klftk ki.«K CUkt
U«» LJUI CMiklTI "HI Mlukl 11 (1*11
HtLU Mt
UHk^SI Lhk»* kl*k Hullkf H*l.kK, 1C.
Lull ti> lUUkt Mllik 11 liu>t I*"-
Lkl.l LkU il^T Cl lUkhLfcHt:*!)
ioblH tulm htlkbkASS IhtLk If LUUli
(tUr.lCHl hltLI k>»« IkTLtH1
UtkllLLt Ml *T UlkllUfc II Tt) CL*h
GUI 11 '• IKK'ljS ««JTt 'jLUDul
I.III IlkLk »T tlLLI^fll! Okr
LIU tklt \,l*UUl,H mi Mf'tl Ul CU*t
JM*» rukf HIUULI
ntkll blVIn kk LiiUlu litiol, «L
Mk TNIb kiltk C.H; It.J^i.Ji
Milt Cl, ;«.v<>. .W-.jlt
kill.!.!1. Lli' >HJI«J|! fJI
MM Ol «)L'*r 1.1(1 1 »;•! Jl1. J.' i -Jt
uix.i'hut t IK; M.I-.; Jl j ; j».
Jll- in; Hi 1 •; id; ji
K.I Lh; b»l'<; JI:<;J»
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kiksiilki.lok
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k^k JtLbfl IV
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kkk JLkSM
ILLINOIS
Ju»A
CKLlKUflt
IKllBOnjI
CkLlHUIII
Ilkk^lLVAklk
ULIkUU
Idkt
kUMM UtROTI
viiiHikt;
ILLIkOIS
ltl»S
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ckkiufini
tri»mm«
ILOklti
HtHtJl
re 10 HI no
IbkHO
LhlO
luk*
mkTucm
cm. i Hum
klkllllll
lOkl
IfilZUkl
LIHC
killild lilkOIi
CI'H.tl»
>I.M.Uk
1 rill- OH
ftliiUk
•hll.uk
HILllH
1 1 LUlik
H...OI.L
. OU.IL
I'lUUt
blUlU
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h.-l'U
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MI III)
JI'IU
^ 1 1 'j
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1 4l*i 0
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7 U4*
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iib
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lit
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l\ C
^»*o
ii.lll
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-------
TABLE A-6. (Continued)
•j/
b«
VI
tJ
M ._
l>2
bJ
lit
b'j
to
b /....
ta
o
70
71
72
JJ
7i
7b
/7
7tt
t'l
no
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62
I»J
04
> . B>
ro **.
11-
ut
40
SI
S4
*i
t*
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•tb
2J_
no
•»»
luo
101
102
. IHJ
lu«
lOb
106
107
IUU
!"•«
llu
III
114
Mill- lh; :.k|'l; )| ..ji
Jlf. Lh; :>i 1 j. jls;/i
LlllLtnllt LM Milj.JUi.x
iNib or iiiTunm ih. s.ij.ji<.4i
tinir :UK:.HI»L in: i«./:ll-.;}|
ihhUTT Lh; Sc 1 ; Ji:,; J»
^UI.bll|HI Ifc; HI J; jl:,; J>
nCULL lh; N.I; l|-j; ||
THll 01 «|.|iUTT IN; Nkt; Jls;.M
H Thlli 01 h IhK AIMUTT Ch;«tJt,, JOi .
!JHl!_V!f_Atil!UlI IJt; :,*.»(.: JO:,:; i
UlkJTT I N; Sy]u; juj;2i
Tuih o» ILK t»; SH^7;J^!>:lt
IL*T Ch;S» UF U«T Ct>;»L^O;^5;|l
SHILL CH;*k^/; J^;|t
JOfctS Lh: SC^i.^-.lh
THIb ul LU lH;»t^7; J^^;lt
sucmm in; hc^3.^j.it
OUlit Clem hh IUMI LLk Ck;kHJttv; J^b;It
Ml»h t,t;Hi^iJ^^:lL
KLtHuHk CV;*(.IU;j/S;lt
• tllLK lk.MUb.iU(.*HPI«t (.M.^LJI.ll^.U
^U(.*hl»lBI. CM. Mill, J2:.. It
sui'm Ch.cm.ijs.vt.
HUTTUI Ck.llb.J^b.^L
t THJ) &CU4H Chi *kl).j2i..t
ILkta Ch. bCI7.J2!>.2t.
HtfTTVh Hi. MC21.J^:..2t
St Ihlb of bUTTbh cH. :>» JO. J2:..2t
THIh 01 jALKSuh Lh. »LlO.ILs.ll
LULI CM. L^. J0s.lt
Tmt or Jic.fti.aH CH. i«.^.jo:-.u
TMIt- OF J«l«!>O* Lh. RLI.iU:.ll
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Tkbfiri Ck. M iL. ..••>:>. Ir
Ihll. 01 JALKbOh LI. HLI..JII-. .41
ThU Of J»L»JO» In. rU.jl,:,.^
tHJI> of J»LK:.J» ch. MLJ.JU. .<(
tlillT Lh. KC2.JU-, ,7t
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T«ILi>k CII.KUIO. J0i,l»
II A LI H Lh: illlaiJUl III
Sim*H Ch. ! t«. ibk.lt
ThIL 01 Li.»L"4 LAhlbl Lk. iklb.Jlii.l
ULAIH LAhluh Ch. hM22. (Oi.lt
Thll- O| ^v.u»« Lh. HJ. J0b.lt
AOUAH Lhltl Sh2«.jCs.l»
.Ulklt.AN (h. J»JM. Jll', . It
bOLI Ch. bliU. JU...U
• rillKLf lh. bk^O. IU..)!
DM! IU1 In. hkl (.JO:.. II
_J*Tt
( .inoii
< iiLi.Cih
LhlObh
Lhlbllh
lltl.Uh
L- I.LI. (IN
llhKI CN
Lhll.Oh
U I.I (.Oh
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Lhtl.Uk
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. ChLLtiM
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11 H.Ok
Or HUH
Llill (Jh
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4bl
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400
200
200
200
. 400
400
4UO
400
4oU
. Jl
4110
-------
TABLE A-6. (Continued)
IU
IIH
II 1
II/
lib
II 1
120
1.2
124
I2b
121
I2h
UO
UI
U2
IJJ
IJ6
111
Ut
140
111
ro 1" .
— ' IM
IMA
1*0
14*
liU
t'.l
142
lid'
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lt>2
IIH
Ili4
Ibfc
Ibl
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INM'LIIUI 1 K.kU »r. 11.. . Ik
ThJI- <>» JillillN ih. k>lb. 10^, II
bkAkbbk IklL* M (i.U/i./'t
nllli.l.Lli.k Ik. '.rii . Jib. *t.
• H-h 4kik-.Uk Cfc.k.l. Jijj^L
THlli U» Llh Id, hi 2l.jlb.2t
LLK Ck, HI c\ . Jl4,..t
fkll UI 1 LH ch; k> 2«. II:,. 2i
* Lk 1 k HW.iv. Jf..4t.
SO Will Ch Mkl7.J24,2t
LIU Ck. kka. a: .i?
L Ih* bklibii Ik; bkii.>.:,jt
N IM Ilkl'iM IH( kk3. CJk.JI4.ll'
NCC*I L Ck, it2. JlS,2C
NEL Ilk (.N. SNll.JIU.2l
UTTII. bUkjNIlt Ck, bull, ll'j.21
i lk« CO^UILLt k; -jdlt.i/i.^.
THII- 01 S Ikk COOUILLI Hi kl.jJ4.11
S Ik* COUUlLLr ki 4t7.J35.lU
su,u»ii en; Kk.^0, j3h.llM
IlkukklD UUt Ci; SII7. 334.11*
Hfkk CH; kt9.JJ4.ll*
LOCkMlNT Cki kk«.JJ>, ItM
CN1TIK Cki knly.Jll.lU
l>*ll Ck; bblk.J3S.llk
4*111 CRj kriJU, JJb.llk
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k Ikr ki-Ck Ck; ^»^l( j J..,I2»
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bILUNCb Cf; 4t7.JMb.ll*
roiiTkk (k; kkld.mS.lln
LOkl Tktl I'*; kk(S,)«S,lU
t«c niLl Ck; &i>l<.3«.>,llu
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4ilk!l» CuMk Ck; 4k4. J4S.1 1*
THll tit kuLUI B; 4l7.J4S,ll«
Iklt Cb; Ntlb, JM,,H*
THIf UI ULIbbl4 k: C UI kulOt ii ; ktl4^l!.b.U>
TnlK UI HAIL kgk Ik; Si 21 , jV.,1 2k
41JI »«!• ck; kk^l. Jii.U*
lu!>llk Ih; Hilll.jllS.12y
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Tkll UI IHkSTt illSTk Ch; 4k4.iSS.il
INII ui 4iikSTi IOMI it.: 4i •.. .>:>:,. 1 1
Ikll UI 4h*41* Cu^Tt IB; i» -i.Jbi. 1 I
thlh UI 4M*S1» LUblt Lk; 4ib.Jbb.l|
bLUI Jkl Ck; •tl2.J4L.l2k
('••I i~.uk
< hi l.Ok
( ktl.Uk
Cki CUM
IC»1 bk
UiLlUk
lyK.U»
lr.fL.Uk
Li.ll.Uk
1 hlCCk
C. it. ok
i.kl 1.1)1
11 M.dk
l.nli.Ok
loll.uk
LnM.UI
tkK.uk
Cott.Uk
CkM.Uk
CklbUk
lSH.Uk
LNM.Uk
t 1 tl.uk
CkfCbb
(klCi'k
LklLUk
ll ICilk
Lbli.Ok
Uhtl.Uk
CklbUk
Ukli.uk
till i.Ok
(kM.uk
fklUOl
CklkOk
CI M.Uk
Tkli.uk
(. k 1 l-Ok
Cllbllk
Ckli.Uk
Ct.ll.Uk
khil IK
tNtbU*
IklCUk
UklL-Ok
2l>t
21*0
2lib
-------
TABLE A-7. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF CADMIUM.
CONCENTRATIONS ARE IN mg/kg.
01)..
till
LUlt
i
J
4
b
b
1 .
t>
9
1U
11
U
II
14
Ib
III
11
ta
\*
m
t\
2J
a
24
?> _
26
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2d
«
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~ Jil-
" .
J4
Jb
Jb
31
ja " "
J«
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01
Mi
4J
44
4S
46
41
40
si. _
bO
bl
b2
bj
b«
bb
i«.
IrtlMi IMJn Ml- Al jl Air .1*11.1.1 m. T
THIhO Lktlfc V>TP At JltTIUMLLl HI. 1
nlfcUHbk llAlltMl
IIAtiAlllOk tltnrtil
nilikrbt Mi. MUM.*
nthtlNOK bAITtht
f*HOd li t »m thflht
HOULtttK tkttk *1 (1UU1II
&*k1« tk* blVKR lifcLUt »-htl«. tiAN
LUt^Lh LfcH.0 Ad UUULUth Chi LK
l>Mi««Mt«T CluntfcTL MO 1 jtbtut
(.ULlhlUU Ul«f.l blLOV V-»»llKk UtH
UUt lilt h LHMK flllHi nULHOLllkNU »*SM
l>tkr»MikT 1-K.HtkTb lib 2 SLUbl.1
D«k«ThUk b*TTtfcl
FUUIbHf L0\tt
Olilki H til TINthlM* fct.b.
UOULUEM Clttk -(.
• UJil|l |.UIt<|li Ml' *T tnftk-IOkO hC
Ufs nuikr- bTr UJOIITIL ^LUI<«.I
Diim H(.*Ld «i*t- iminr, IL
• U tHU IU»: AMtA JJL. Ifll Sk or M ^
HtihlH LAhULIM
kOIIH (.AhULIkA
kin fuBK
Nlfc Ibkl
11 k»
k»» fuhK
Nl IAUA
IHIiLUItA
IkLIIOMklA
AhUOkA
KAribAS
Afl/ONA
Al. iZllkA
kAkblb
*Lk lUkK 1
khk lUkl
(.AL1IOMBI1
AklZOMA
kkh fbkk
AlkTUCkl
l»k IOHH
ni^SACHur.eiT^
fcik lohk
Itk Ibkl
UlSLUHblN .
nl(.HICA«
II. hA
TtkHtbSkt
CALirukNlA
CfLirOhMIA
CALirOkkIA
LALIFbkllA
LALlrONMIA .
CALlFbHIilA
(.AtlfOHII*
LfLIIUIIIlA
CALIIbNklA
KLIIOMilA
C«LI»OkklA
CALirou«IA
IHIU
ItHlf.Stt
IDAHO
nUM.fcCUH CO.. HI
JILlkOli |
k».k lOkk
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MbSlbblt-l*!
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k»k jih-.rr 1
ktk lUkk
kOI 111 LAhULIk*
ICkA
IILIMOIS
»lulilVA
IH.-IUU.L
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1I1UU.O
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S^uO.U
ui »o. u
bPi^.u
in i/. ii
1144 .b
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701 /.(J
bJbl.O
4«bO,U
4db4.2
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tiot.o
2000. Q
1»1J. 1
1UOO.O
IbbO.O
IJbO.O
llil.b
IObO.0
lOOU^U
1000.0
1000.0
1000.0
IUOO.D
1000.0
1006.0
looo. u
1000.0
1000.0
1000.0
touo.o
1(100.0
tsu.c
870.0
no.c
7^0.0
S/B.U
bi.U.0
blll.U
4lb.U
SlJ-P
MO^.C
J7'J.tl
Jfci.O
Jbli.L
Jib.U
i
-------
TABLE A-7. (Continued)
LOL
ro
Sf
bO
bl
61
bi
bb
t7
bb
b9
10
74
IJ
7«
70
77
Jb
80
bl
B)
b*
bb
Bb
bd
90
92
tl
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IU2
IOJ
104
101
lOb
107
tub
lui
IIJ
III
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ftUUAUUI ft II Al llhnlkLlOU, LI
L. llALk (ha AlHLIkl ll.l; IfcUIIKJHl
bUklUHbt LU •ttt AT AblKIILl kL TO 1
bOkLlkl. Ibt-bh bl* AT IOHUM, OHtbN
CAhkOLL 11 ICt bit* IblTllA SLIlUUt
TMlb k(J i 10 SHkt.Hi Ik 1HIH AT ILt
200* bL« HtHSMtH till (lib OK 4 HI IOH
SFttLIk Lh ThlB. bIK U. - ILUbAk
•tblOMK LU SOUTH VI t.kuH'jtl klLLb-V
-»tOOn JW.ti bllbOk Hill AM ILk
eULllSH MLL'j Lk-k ur bHm*N Lk-Kl
• LkTObN LHIbk, H»A|i NAblO r<'«cf,-k>«
CHAkLtS L1K -Sll- lilbiibTtn '-UHH.L
CUKkCLTlLUT ill Hlb At bOLIOkt, HA
r.Hk. IlLtCk b. Hl^blltCTOll Alb.
bLAtt HMtk n.r. 10. b
IAST k • ALrubT ULCS
KOhTH HUriALU STV AT CktLMltlUhO bL
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LI1TLL bLlCft Ch tl flfcbT bT . ; HUH1O
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CBAIILbb C1T1 bT» btv blUUUt
CUtikCCtlLUT blltH AT ACAMAt . lit
JAIIIb fOkl «LAH MACCLIT. tki.
C|f:)JbH klLLb bCOTM 01 CHAM) A»t-Ki
LAiCbTOk Cl bL bb 4!>J I CLATIHC OUT
ft H)C»IH ^Tf *T »T MUCItR AL TO CL
blkTub* Ch Sk ur Hkkl hklll.t-uUttk
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HOLI lAft- AT q^LL LAM. ill
E. SJOc Ollb tl ilbkk HUTS LK; fctlUl
ST JUitIM b Uhk->lh ur CttlCkdu bT !•
COkfUb LHklbTl HAhfaUb - «li>LA TUHMl
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bLttKSlikc ril«l.b If niLLdllk, HA
)I)k)l IttLk STF AT CHAtlLOTll kL' TO
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aukt L moon *. nun* LI en" MIIUUII.
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bPiUTd LthOLlHA
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161. 100
lt>0. J )J
150.000
1UO.UUO
liU.OOO
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11 j.oou
110.000
llli.OOC
1 IV. 000
109.400
I(lb.lb7
100.000
100.000
ti.aaa
b7.2
-------
TABLE A-7. (Continued)
UOi
I1J
lit
IK
lid
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120
121
122
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Ul
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lit
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ANHkbll, hll INI L«kAL « LIUMUL :.C..
out con IH mikkiL '.o ut PHUT MI
Cll II LINK ninHUk
DO* tli IT pnlVATh kL Ull LlUHM
COUHi l)»Lt»t NIVtk IT NU'.t LAkl
lOti u hb rumun IM> h) hf •t+.'i
lAMIILLL hlSUOk.MlHlk.kll
HI LI) nil
U:> AUDI bLULbHA^J LlfOl if UllNUTU
NUIKLMU H1HHOM fcUklM «» O.Lb H»kb
CUIttlbU^ VB 47 bfabTB Iub&. it.
nuMtk Cbttn MKik tiiiti ni
• I.KLK p Ilk LUDMIILl^, Afcl/.
CU Dk JO tifitliM kMTI* HOOUHi; hhOK'.O
»ut.«a thUK iir
(iRLtkLVH.lt ilP «1 ChltllLVlLLt Tk T
CLFk CO»f CM LHAMbtL ktlh MrilbE III
ASh mat ouriLQ. >h IHOHI-. MILL, nu
UkkintO ThJb UHST 5T JUf k; FklClTE
. tblkTI k • SB J* ik Ul bO^ilH Ik II
nUhblSTOMB iTP IT IIUkHlbTCIkN 1b
BUUTH 01 bllSU Ik. IUU lOi Uf&l »bOH
•EkTUHk Ikttk <1 »OSCIUS10 bklUCl-l.
L tlACK Ck DkS fct-kkllP. StMt.:HillItl'H
1
ILlllOlS bllih »T ttlC^HtH ISLikO. J
tHJI HARHOk
. ^lU7HO^ttST nlTitOUUl LS Llkt OTt 'j
*tii srr AT UA« hiuct Tk ro t»bi ro
1 HI if OP VtikliAkll
Tkll-UTAfcl TU Ckttk HKLH 1O1.J
. ZUSLDBbll iTf It TUJCUaUil kl TU >t
bEli CeOkk b fcl Cbu Hk bH; hlfcbl TMlr
CllTLUHU HibbOb
ktklOk* CM HIST Ul DU1CH (ILLS
flOfck L 1IOOIT tA'jl Htkbl kb; kOmoM
INblAMt BAhbOk
CUkikllS CkL OM |] iT l>kUSI tCH tlf-
fWUST till STf itUKCI.
bChtlLUlLL H AT II L KClC'H FOOL Nh I- MO
Skirc LKIlk HLu« kilt. L1KI. AT RUL
Uli TLllkl^ klltk IT blAKIULt.. IL
DLI t'LAlk'ti fclli.fc bj. LbA«r Lk kK.Ul
Ukfc Tklh TLi bUFf
UT JOSLIb k AT HiiOkt M>; I1H.1TE Tk
HOkA L 12(.U»1 Sfb L LI.AC*, 1 li J fcOhlC
HOMDM lllhnoh
bk«t«kAII klVEN .b ntLI OOfcl.:.Tht*n i
UCbktk. klltk MLIH 1 »'- hOlb lObt LOU
ioUTn hltib - S»*lHki- SdoxLS
:IIIK >
KttlTUCM
l>|k |ONk
• Lk fV TObl
flUMl»I.Uk CU.. Ill
MISKC(.Uk CO.. Bl
Ikltllbi .
klM lOkk
]LNA
1-tkk.SILIlNIA
klSLUMMk
IlLlkOIS
IlUkOli .
» Ifcdlkl *
r IChlOnl.
ru^hicoN co.. nl
Cll hCI.
btli^OIA
At kf.
uu.oour
If.UJUQ
«/.b IUU
Ul.UUUt
UO.UOUO
tiS.bUOO
li J.OOOO
tu • isuu
*• 2 vttbCU
VI. fall UU
lU.UOUU
40.UOOO
ou.ouuu
uu.uoao
lU.CUUd
JV.SIOO
IB. 0000
37.UOOO
Jo. 0900
J6.0000
Jb.OOUO
Jiioooo
m.uouo
33.3J13
J.J.JJJJ
J3.UUOO
.JJ.UQUO
ji.uoOb
ji.ooau
ji.uoou
31.0000
31.0000
jo.eauo
JII.24UO
JU.29UU
3U.OUOC
lu.oaoo
JU.00UO
JO. 0000
JL.OOUO
ill.QOUO
JO.UOUb .
jll.OUUU
71.VIUO
2*.t)oac
/v.toou
/v.oouo
^V.uOUO
-------
TABLE A-7. (Continued)
OoS
Jo*
l/u
in
us
1"
176
114
OLMJLl.lt hl4»h lltAH lUlUk »AIM Ilil
UCrLLblt hl«t.H .1. HI UkMUTILAn Tout
ALIAHAHA HI Ilk .t HI LUtf kL 1 HtAII Of
bATILLA k. Ck II. It. IS t 141
SUhAkULI klILk klfk U:. IIHI Dill
ULhUICKiit» H. bHIil. J./ni I.ST LN
FLlkT HlVtk N»«k OA NVI V4
M.UT hlVIk «LAh ILANT niTlbtLL HAT
1-HAlTitllJCJLtltt klllH JIT CllHIi LL. (ATI
CHATTAhOOLHLt milk AT t.A H«I 12
CMATTAHtiULhlt hltm ktAfc CA HU1 11
l.ttlkl.l A
LIOHblA
I.IUhf.lA
l.tuhl.1 A
Ltlikl.1 A
LIUM.IA
r 101. 1.1 A
(.tOMLlA
UllkLlA
CtUkbl A
LIUkblA
* llhAh
j*i
M
cn
-------
TABLE A-8.
ARE IN ug/Kg.
SEDIMENT LEVELS OF «™>PHTHALENE,
1
J
J
7
0
10
u
u
m
is
it
U
18
19
20
21
22
U_
24
JS
26
26 ~
1 30
INJ )|
0* 3j
34
J<
36
31
Jtt
no
11
»2
•*
18
•IS
SO
Sb
T t HAKIR -,ir AI ntnpnib rk TH n.Sb
BILLIRblOR SIP AI IIILIHOfOK TR IO
TONIk CHLI1 1C AL LO AdiA HA£AHUrUS MA
TUklh CHtHICAL Lo ANtA HAiAROliUb kA
. H»PpblS TtltR AT IKiLLIbl.UU til ARtA S
HtRfHIS TtRR AT UOLLINUOO 1.0 AHtA S
bUISUR HAI S. 01 BIUOLL (.HOUND
HEM IUMH SLOUGH
S.r. AINPUkT lkl)UMnlAI PLJ.RT
TOklk LHtfllCAL CO AktA HAiARDoUb HA
BLDIHIS IFkk AT thAffSfrli IffiLh auk* v
BtBIRlS TtRR AT IkAfblh POkD AHtA b~
HOOfctR MAMLL kOAD CULVLNT
IABPA FL IT Slbktl MIR* NA7ARIUIUb k
. TAHIA FL AT *IOHEI R1RE MALIHOOUb H
COR DOR 5tRIK.CS CO IT UORllUR CA TO
CONDOR ^ERIICE!. CC A.1 CORUI.R (.A TO
COROOR SEkllCKS CO AT LORObl GA TO
. GURUOR SLRIICES CO IT COHOOR 01 TO
COR DOR StRIICEb LO AT GOtfliOl GA TO
. CUkOUR StR«ICES LO Af GOiillOR CA TO
SBITHS UUBP ilTt IT BROOKS Al TO UL
TtRktSSCK tIPOSURt R1SR SUh»EI
PICtOR k|ttR tIPObUNfc R1SI STUI>|
CHtflTRORICS IMC RRSI AT ASRE«ILLt R
CHLBTRORics IMC HHSI AT ASREIILLC R
ICIDtfll DfcUB UMb AT CMARLUTTt RC
-iCIPtni DROB MRS 41 C«AkLatTr ^
ALADEBt DkOB MRS AT CHARUI1TE RL
ICAI>LI|| bHdn MRS AI CHARLOTTE kC
OLD Mill 21 DUBP AT HT HOLLI kt
Oil) MMI 21 OUnr AT BT BOLLI RC
J A 1)10 HUChtb PROPIRTI AT HILRORT Rl
IRbllSTNlAL tHKB 10 PLAIT SITE in Mil
IMDUSTRIAL CHtfl CO AHtA RLAk ROCA B
|RI>UbTRlAl LML-B CO PLART b|Tt RM RO
IRUUSTR1AL CHtH CO LAROFIL1 RR ROC A
ETBIL LOHPORATIOR CMEBJCAL U|l AT O
MEMPHIS TtMR AT ROLLIRUOU RD AREA b
BtntdlS TLkR AT ilkSJUR lid AkfA bAH
MEMPHIS TERM IT RlkSTOR OR ARtA SAB
. HEHPHIS TtkH AT kIRblOR bit ARIA bAB
RtnlHIb TtkR IT IkAfbtl POkb IREA S
PtBPblS TtHM IT IRII^LR PULD ARtA S
BEBPHI-i TtkR AT IKAISlR PORU ARtA S
«tH|H|» Ttkj IT IkAISEk PUkD AkEA S
BEHI-HIS TL»H AT IkAIStk PUkD AREA S
IUIUN1& TLkR II thAISt* PUkU IREA S
MFRPMIS TtkR AT »kAlbtR Pukb AREA S
Htfll-IUS TtkH A| fnAlblh PUj|i ARtA S
BtKPNlb ItMR AI rilAILIN Pukb AkEA S
BIM-lllb TlhR Ar (hAI^tR ru»l) AktA !>
HtrPHIb TLNR Al IkAfSlk |Uhb AhtA S
BtDIHIS TtkR AT IkAlbtR PUkli AREA b
. 1 0 P h
l»kkESStt
MUBIUA
riukiOA
IfkRtbSU
ItRRESStE
CALIIOkklA
LALIIOkHIA
tALIIOkkIA
ILOfclliA
llkktbSlE
ItRREbbEE
ILOfclbA
FLORIDA
GtORCIA
GEORGIA
GtOhGlA
ttOkCIA
CtOkGIA
GtORCIA
RERTULAI
MISSISSIPPI
•UMTR CAROLINA
RURTN IAROIIRA
RORTM CAROL1RA
•ORIH CIFOL1RI
RURTM CAHOLIRA
ROkTH CAHULfRA
ROR1H LAROL1RA
RUM1M CAkOLIIA
RUhTM CAROL1HA
kOhTH CAKOLlkA
kbfclM CAROLIkA
SUUTM CAHOLIkA
£CUTH LAkULIRA
SOUTH CAkOllRA
500 1R CAfcOLIRI
SCUTR CAfcOllkA
ItfcHtSSfK
TtRRtbSIE
ItkkEbSEE
llRMtSStC
TtfeRtSSIt
ltkHt!>Stt
TtRHEbStt
.- ItHHCSSte
Ttkkl:.&tE
IlkRt bStt
llkHLSStl, ,
jnooui
BOOOO
30000
JOliOO
^0000
20000
10000
IJOOO
10000
1UUOO
10000
10000
10000
sooo
soot,
sooo
SOOO
sooo
sooo
sooo
sooo
sooo
I Suoo
sooo
sooo
sooo
sooo
SOUO
SGOO
sooo
sooo
5000
sooo
sooo
suoo
SdOO
sooo
SUOO
sooo
sooo
sooo
sooo
SdOO
sooo
StiOO
it DC
Suoo
SliOO
!iOOu
ItRRtbStE ', SDIID
-------
TABLE A-8. (Continued)
bo
DU
61
62
66
67
70
71
72
11
11
15
76
.77
78
7*
ao
tfl
• 2
3> «b
r^j "
™ ea
.•9
VO
91
hi
91
100
lul
IU2
IUJ
IU«
Ibb
106
110
111
112
ItkktStlt LlfOiUh) hlba bUb*t.T *1 *
TlkMtUSLt riPUbUht HIM1 SUh«tl »F H
TtlNkLSStt LlPUSUhl HIM SUkVfl AT J
fltrl'UIS AfttA NIZAIiiUUS kf.lt SITt 1
ntni-niv |hM H.»iA»i(uii:. NAME riTt i
Hint-Mis AklA HAZAhUIMi:. MiSlt SIT* 1
funinib *hiA uizituuu^ »4sit sirt i
kANJLIIIlLI fcil
KOI! SLOUbh 41 bfLT* 111- SHI ML
SAH JOAl'Ulk R AT ABTIIX.H HiHH
LAS »rU*S HASH AT ICMTH SBOBfc •UAD
.CALLdlLt tAI L«U BIAU
LAS «tb«S BAT LAfct nCAO
... 9ti JOIOUIH mitt it *»ai:.i>us co.
LAKE HEROOCUO IT HUI 20 nkllICK
BUSS1AM klVLI If IlKlAH TBKA.TRLIT fl
BUSSIAI it net - HOHTE mo
. ntU »l»t» it *55Z1 lllfc
SANTA CRO£ BfcLON KI1CLB ROAD MASTt H
B1LO BJI
SPORARe Af SPOKAHt STP UUTfALL
SPORARC O.S BL SPOIANE SIP
_ SrOKAVC |.b Rl VI SPOIAkf STP
SPOKABC AT POiT PAILS IB
.. sportHt .s ni AM cveoH O'ILERE s
SPORANI * HH »S .J HI AB C U'ALIN
SPOtllE MHEk j.b HI. BeLOH CCJtUh D
IAR1HA klttB * b«l 22* kR. klCBLAIlO
•ichcs fl t MftiBi au». mi nme i
HAtUCS B • HUBTH * THIN bklDbtS "»
COLUnbU t 4 Vl&Cb HIP l»T»llt |Hn}3
PUfeTMBUI N IM HI ABI POCATLLLU bIP
PUhlkKlir H |/» "4 HtLd^ fflLATtLLU &
POkTNtUI II J/H Al BFLUN ftlLlTlLLO S
.BA1ISE SfhllCS i/1 HI HtLUk »WflVlk«i
RltHLAkD kTP UTAkt (LULUHflA k|
SKDrDniSH mil* A1 bT*fl NICHbAI 1U
BIC llUlLlk-kE Hl«tk AT PUMT TObkbLNIi
HOkbr IRttR *f II.:.. 1OI UNIDbt
CHAH LARt « BUM*. UntoOH HATCH 1
ttl LARt • LAttblUt. UHlWIl klTtR 1
.. fir tfi LAK*. i MtliiPUkl. UNIbON VA|t
Blkr CD. ktSlRIUIh * LUliUilLf HAlIk
HUfcRISIMLt IfctA bilifcUOUS MkSTfc ^i
ALAHO LAkt
AHlbUB MIL (bllt)
HunroLT bittv • iri*i
lUlt. NMtk kLAM HINISIIILI.I!
AHIIIILJIk U. Al ILHANrO ST.
BU»IALU Lh «T APtNllAk Nldk
kkLIKAb klktK 11 bUk^ALL^
hUUlUKN Cfclfck AT f.UUTM
CAkbOl k. w NlfthlJI.ll
ItkRfebStE
Ttkkfc^JIL
IIHNFSSIK
UkRL^StE
It. ill
llLlfUklllA
LkLIIUHHIt
•KIAUA
R1«A04
kCIAUA
CALIIUkllA
1AL1IUHR1A
CAIirUHIIA
AkIZUkA.
V*APA
• Akin
klSMIMCTUN
NASHIRVIOI
Ib* HO
.1111 HO .
IBABO
IDAHO
kkbHIIClOk
klMHIblUR
Ml^HlRCIUB
11AHO
1EAUU
JCAhO
ICAHU
•ASHIICTOH
IIAfrniUCTbk
kASlllkbTOB
MA!.kJkC1OH
CkfCU*
CDICUR
CktCUR
kCkTH LAMOLim
kff AltA
t-ALtlOMUl*
CIlllOkllA
(.A LI 10 dill A
* HI U>» A
buUO
bOBO
SDUU
•jbbU
bbOO
iOOO
JOUO
2bOO
JSUO
2SUO
2bOO
2500
2bUO~
2118
2000
2000
2UOO
2000
21)00.
2000
2000
2000
2000
2000
2UOO
2000
2U flO
2000
200D
2000
2VOU
2UOO
1CCO
20«IO
2(100
2000
2000
7000
ivn
l»00.
us?
IIMU
Hit
ib^i-
KM
-------
TABLE A-8. (Continued)
UbS
flMli
Ill
114
lib
lib
11?
iia
m
uo
142
1-
UO
m
112
ui
us
Ub
111
IJrt
111
> l«2
* SH
lib
l«7
|U9
1!>0
111
Ib2
Ibb
Ibb
Ibl
1*B
IbO
U2
tbi
Ibb
Ibl
o«t»:> N M TmtniM ki:..
blkll Ikl blVEB HI lUk Pk4J( OIH
TNIKltt klttk IT IbCbMOOU
BUULUEk Ckttl »HOM HUbCN Ckttl
km hid* k. iui>»t *.UkM^C Hi
*H».HIClb k. IT kllTS lit.
lUt-ftR Lhtlft Ib bUlliUtk CHI EH
till Nl»tb IT CJllliHt DIK
LlhUkTIk Ptfl
CO^tiNIDO h. * Il»«*
IIBUL01 NAMBOB
PCIML BAHH k CT Lull
ill bll ClkkL
C. IUMI Ok|Bte klVtH • OHTHtt
ciksok • « ken tHrikt
S. (UBt TOLT 11 MlttLl D.h. IBTiU
CEOIk B. UN LIIDSbllkC |bK*1Tll: P.H.
DUBIBISB IlirB ttlk Ktkf (bfl 15. iO)
TkuciCE kiiet IT rikiu
Llftt tlkOt IT Skkb BlkBUM
SfOklkt k 0.5 HI Ib SfUllkt STI>
SCKJfltkT kk I041B HITLk Ikllkt
BEIILkTOB Ci Ik TtKTIibkll ttt
bfVtkTUk CB .b«l bl TLkBOkll L»f
BL«»LkTOk tk 4 TtklKOkll OUTMLL
TOMIk CHLHlCti L<1 «ktk NAilkDCUS fc»
1UHLB CBtlllCIL CO IBEI HkZIBDOUS HI
TUklk ChtnlCIL CO IkEl HlZllbOUS »*
PCBMCUt* BIIIIIUVU'. VISTe SITt BtUl
MEKI-BIS IkLt BtZlkDUOS VISIt SITE 1
BIHILI BOIIi l>B10l>t
fcllLROID bklUCE
BUOSKftLT LIKt SILT k. IhH
IMTkttk KILL |b2O)
CtSI 3B1B. STkltT tifclblit
Llkl tlkt
nomLUflkt k »t kuuuukiuce
TUOLUHkl kl*»B IT TUULUHkk CIII
PtllCOBll Lilt
ILIHII B Ilk CkLlfUkll
Slfc tHlkLlM.0 B. IT (.LIITU*
CltllSltU k »T ff.S LIKK
•KFHLs'k 1HNJ kU O» fObT IkTHUk
UUfCBJTI k-CIHbtk VITI.B SUH LI
BIO CKIkllt BlttB 11 l&LITI UlTKB^lO
k*iini utitit ikt«n |i«im« k)
^•rkOHlbfl klVKB IT SkOhOfllSH
VUllLLur Rlttk 11 I'UIILLUP
IIM-dk ISLIkU : tfrlt It (IM
• IMiuii ISllkO : KtlL tt (bl)
UkluH M t hkr>l*n.k HUH ytltN IktlK
siknimsH ki«ei 11 koouikiim
CILIIUnlll
IILIIU4IIII
CILItOkkll
CILilbkBII
klllDI
IB17.Uk!
Blklll
BIVIII
kllflll
BtVIO!
klSHIICTUB
klSMIkCTON
Cktl.01
CkKtUk
CktbUI
CktCUB
ILUBIUI
FlOKIIil
nokio*
rLokioi
TIHBES5IE
It*«ESStl
iikkEbstr
kkiiutk
•Lfc TOk*
ItkbtSbKC
IhlZUkl
CILIIUkkll
ikiiom
cu iruHkii
IklZOkl
TtllS
Brk fltllio
klhHIIK.TUI
W*SIIIIII,1UM
KlSHlkblUB
IbHU.bO
IbJl.LO
Uli.VO
IbVO.OO
IblJ.tO
|UBi.UO
Ubl.OO
Ii99.00
12N2.CO
mu.uo
1^50.00
1JOV.OO
UuQ.OO
1200. dO
UOO.DO
llub.UO
lll«.b(l
IOI«.bO
1000.00
1000.00
1000. UO
1000.00
1000.00
1000.00
IUUO.CO
IOOtl.00
luoo.oo
1000.00
.900.00.
~ bSU.OO"
BOO. 00
BUO.OO
Ibb. 10
131.10
12S.UO
bVJ.no
bbl.Ufl
bJ4.JO
bJ6.40
bOO.bO
^uo.uo
tiuO.OO
50U.UO
quo, no
UtlO.OO
4II.O.LO
(II.O.CC1
ittO.UO
UVO.bO
uuo.uo
-------
TABLE A-8. (Continued)
I7U
in
172
111
I7S
I7b
171
100
161
Id2
I6J
tan
!«*_
lab
Ib9
190
HI
19J .
. m
I9b
| ISO
ro 19*
VO jflO
201
202
204
206
2Ub
210
211
CHthALI:. k kit CtklhAllA
kl kEkkUkUA H i ItkTHALIA JkTAkE
lOkA klVPk AT MAhSbAtLTOkk kTI
TkltaUTAkl 10 CbATTANOUbA ChtEK 0.3
LilTLt SIOUI k U».JT 01 &ptkiKk
LITTLE S1OUI I AT Llkk GtfUVE
ion A klltk IIHHST 01 «Ak!.lUIL1bkk
••k kATtk IkTAtt AT DAttbPtkT
DUHAblSb k. UtLUk ktkTOk STP (kH 9.
AkCAkSAS k ktAk Otlbl kAkSAS
AkkAkSAS klftl Abl
cokskii CIIEE AT boovER sr s
LITTLE AkkAkSAS k AT kJPS ST
IT LACIkG STATlOk
UllSOb kOAO bklDLt
TklBUTAkl TO CHATTIkOOCA CktK 2.2
PObD kEAk TERbtS?tf-i;tOkl.lA iTATB L
TIlBUTAkl TO CMAIlAkUULA CklEI 4.4b
.. BOUlDEk CktEk btiOk HULMOUAkU M?H
DOkkSTItAM SlUt kMI 2bU RH
& IIOIkEi R li
T E IIAIOk STP AT HMFUIS Tk TO HISS
6 P4LCS EASI Of SAkOI NOOK ST PR
O.bHI EAiT Or SAkDI ROOK ST PK
NIO LA PLA1A RE^LRtOIB bEAfc OAH
Otkbl kAI kEbULATUfc CSO "
. 7>4H| CAST OP SAkUl ROUE >J PI
JObl P. PAilO LAkllfJLL. BCLLHAHk k.
fk-250 SCIOTO 01C lUk kk 1 270 kk C
OASTP UlSroSAl Ikt. ktlFOkl.kJ
HA01SOH pAkk CSli
•ABAPO • kk UAkllkkTOk kj
MATf
kAMilkuTuk
HAbblkbTOb
lUkA
T»kkKSStE
IOVA
IlkA '
lUkA
kAbblkCTUk
KAkSAit
AAkSAS
kAOSAS
kAkSAS
IFOkCIA
ItkkCSSIf
llkktSSEE
ItkkESSCK
ItbkE&SEE " '
ItkkESStE
ItlktbStE
ICKA
ICkA
nikkfSOTA
CALlPOkllA
rotbTo RICO
KAkSAS
kASHIbCTOb
PULRTO R1VO
ItkbtSblE
ILk JEkSEf
•K* JLHSEI
I'H JEkSEf
kik JCRSRI
CHIC
kEk JEkSIl
kASMlkCTOk
kilt JEkSEI
m Jiasu
J lit Ak
400.000
400.000
.'62.000
260.000
2bO.OOO
Jilt. 000
210.000
.100.000
200.000
200.000
JOO.OliO
200.000
200.000
J .goo -OOP
200.000
200.000
200. OUO
190.600
174.000
* ULiOfiii
146.000
. I10.POQ
100.000
. 91.000
92.000
76.790 ~
66.000
60.000
S8.000 *
41.000
29.790
20.00Q
21.000
20.000
17.000
10.000
.IO.OOC.
-------
TABLE A-9. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF ANTHRACENE.
CONCENTRATIONS ARE IN ug/kg.
1
I
J
II
tt
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ituCHCB BIBttL kUll (.UiVr.HT
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nmi-MlS Tti.ll 11 HU|LlkUOO 10 IkLl S
• tntHIS TEm IT HULLIMIOU kb 1MK1 S
TkibtiTkki TO CMTTIBUOI.I cnei O.j
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bUl*>Uk till !.. 01 ftlUblt CKUOkU
Ptk IUHR !>ivut;H
S.r. IlKfOkT IBDUSlHlkL PI.«kT
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ffiT 1H1M. STitlT HB1IH.1!
ruifft ft IT STItktt HIM HllihtOUi tf
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cukpuB stance^ co IT CONDOB r.i TO
coipo* !>t«tices co 11 CUHDI.B u» lu
COkllUB SEBtlCKS CO It (.UHinik CA TU
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riCtOB tlllB IltOiUfct UI^K STUU1
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ftCli.tni PkUB HMS 11 CblKlOITt >C
ACipeni i»kun MH IT cutkioitt ic
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jiPCtf Bor.Hti Pki-niTi IT urirbBT *c
1B1IUSTIII1 CBCB CO PL«BT SHE BR BU
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1BDUSTB111 CkfeB CO l>tl«T SITfc BB kO
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ntriNis TruB IT kikbtuk PN in* MA
BtDfHIS Tl*k IT IBtTStk FONO IRtl S
«mmlS Tt'-« (>1 IkilStN VUkp IkEk S
ntntbis »*ti Bk2kkiioub nksrt SITE i
nrnrkIS mil MAZtkliuiis *»sii birt I
IUIUHIS IBII B*^ikpous Kibje SITE i
kBTHUB Mil |i>07)
BUC1 SLOUCH 11 DtLlk kU BhlPCt
Skk JO*l.iU|k k IT kkTIOCB kiflC
CEL hltlk IT HlU llElL, UlfIS ilKlLT
Llii IHC1S H^M »T kUkTH ^HOHI kUlll
CkLLIILLL toll L1K» «t»0
L1S »tC*J Ml Ll»i IIIAII
SIN JOlfaUlk dlllk At iTAKlSlAUS C«l .
INHUk* I
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liilF
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bttmcii
kUklH CAkOLlkfc
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BUkTB ClkULIk*
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kllhlH CikO|.lkA
kOkTB Llkatlll
kbhTII C«HOlik»
SLU1N lthOI.I«A
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SUUTH ClkOLIkA
SLblri L»HOLlk»
sou in ckkOLlk*
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itkktssie
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muuao
IhQOUO
tiUOOO
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1 )UOO
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10000
toquo
1HCO
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sooo
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suoo
bflOO.
suoo
sooo
SOflO
SUOO
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suoo
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sooo.
sooo
suoo
suoo
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MO 00
1I..2
JOOU
PSOO
JSOO
2SUO
-------
TABLE A-9. (Continued)
Obb
b7 LAM HfckDOLIkU AT likl 10 Uklbt.k
bB HUS!>l«k kldkk Al VIIAH TkfcATItkNT PL
b9 kUSSItk hltkk - hUkTk hlU
60 HAD kl«kk AT tbSII LAftk
*l SAkTA IHIU BkLOk hUCkR ROAD kASTk k
62 TOPAZ LAkk
61 . HILH MAI
64 HOUSTON !>MIP CHAkkkL AT TMk TUhklkC
tb SPOKANE H O.S HI Afc MPUkAkl iTP
66 SPUKARL k AT SPOAARk S.TP UUirALL
__67 SPtlk'AlE k O.i KL SFu«.«r tri.
60 &PUkAkE k l.b Bl PL !>POkAkk STP
6V SPbkAkL R AT POM IAIL* ID
70 SPOkAHE R .S HI Abi'cOLUM D'ALkME b
'! .. SPOkAHE R « HM 9b .1 HI AH C D'ALER
72 SPOAAMB kJVkk J.b HI. BkLUk LUkllH D
. . 7^ IARIIIA kltEM * Hkl 2*4 Ml. RIIMLARD
»4 RACHES R 4 IAI1IIA HUH. RTR IHTABL (
7S_ BACHES B * RUOTB < Tklk MBIUCkS kk
76 COIOHBIA k • PASCO MTP INTAKE IMH11
71 pokTNtor a. 1/4 m *b« 4-ocAtktto ^TP
70 PUkTREOF B 1/4 Bl BkLOM POIATCLLO S
^Jt POkTkCUl B 1/4 HI bkLUH PULATtLLU S
•0 BATISt SPRINGS 1/4 HI BkLUk PUHPlkC
$' IICRLABD MTP IBTAkE (lOLUNblA Rl
62 SIOROBISB kllCB AT STATE HIGHHAI 10
1*1 PIG UUlLrCHB B|lkk AT PORT TOHBSEBD
•4 BARCNESTkk. MA. MATCH SUPPLY ' -
. _*4 UObSE ChEEA AT U.S. Ibl HklDGk
06 CLEAR LAIE t BECE1A. OkECOR HATER I
.•• ML LAIR « LAIk&lDC. UBECOk MATBk 1
66 CLLAB LAAE * BEEOSPOBT. UlkUlk MATk
-»»...- Ijkk CR. BBSkBIOlk • CO(|lllllE MATER
•0 BORRISIILLB AkkA HAiARDOUS bASTE SI
«l ALAMO LAIC
»J BUHBOLT RIIER « IHLAT
94 IUBA BULB BLAB BAkTSIlLLI
»5_ _ ABTbUB (ILL (S20)
96 AHEklLAk B. AT tLHARTO ST.
22 bOMALO Lk AT ABLfclCAk RIILR
94 SALIkAS RIVER AT I.UNZALES
*9 BOUIDEB CBkEI AT HOOTB
100 CAhbUR k. • RIVCRI1EM
101 _ OrikkS k BL TIRkBABA ktS.
02 SARTA AHA Mlllk btLUH PRADU UAH
101 TRUlICk klVLB AT LOCfcHOOD
104 BOULDEk LkkEA AbOlt MILUKR tkkEI
106 ~ AHEklCkk B! AT kATTb Al""""
107 COPPLk LktEk Ab bUULIitk CMLkk
JOd GIL* R|«kk AT CIlLEiMk OAK
110 coLOkAiio ki«Ek bitty .Akitk I>AH
Ml AkTUUk (ILL (SOt)
112 '
CALirOkkIA
CALIPOfcklA
iALllOkklA
KLirOkkIA
AhlZOMA
IMAS
HAbMIMbTUH
kAbBIRbTUR
ktSHIKCTOR
IDAkO
IDAttO
IbAHU
IDAHO
kASHIkCIUM
«ASHIkCTOH
ktbUlkCIOk
kASRIRblOR
IDAHO
IDA DO
IDAHO
IDAHO
DASHIRCTOH
kASHIBklOB
kASHIRGTOR .
kASMIMCTOR '
kASHlHCTOR
CRrCOR
Obi COR
CkkCUk
GNEVOR -
ROHTH CAROL1AA
AklZOMA
IkHkESSfk
MtlADA
CALirOkHIA
kkb lOki
CALirORIIA
LlLirOkRIA
CALiroRRIA
AMIZORA
kktAOA
rALIIOHRIA
CALirORRIA
AklkORA
lAt-lfUBMA
CALIFORNIA
AkIZORA
AkIZUkA
DkVADA
AkIZUkA
km lofcr
IkNNkbStk
• rrtk
^M'O.OU
2i>OO.UO
ysuo.uo
2bbO.OO
•f ^00 *UO
4 1 Jtt • 00
2000.00
2000.00
200U.OO
21)00.00
2000.00
2000. CO
2000.00
200U.UO
2000.00
2000.00
2000^00
2000.00
2000.00
2000.00
2000.00
2000.00
2000.00
2000.00
2000.00
2000.00
2000.00
jooo.qo.
2000.00
1900.00
IB&7.VO
1610.00
1600.00
1750^00
172fc 00
I69M.OO
1698.00
1664. faO
1640.00
1611.00
IbVU.OO
lino, op
Ibl J. 00
I4tl.0
-------
TABLE A-9. (Continued)
Obi
tor
lilAIL
1IJ
111
Mb
Mb
11;
na
111
120
121
122
I"
124
I2S
I2b
1"
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IJO
131
IJ2
I3J
134
US
lib
HI
na
140
141
3> IH2
£» 144
^ 14*
Mb
141
14B
ISO
Ib2
Ib4
Ibb
Ibfc
Ib7
IbB
IbO
Ibl.
Ib2
1*1
164
Ub
Ibb
IbT
COlOhAUU ft. a ILHA
RABULUl bAfcuUli
CLIhL Blkbl'B t. lulu
All Mil liHAL
L. tOkl UHlBtC BlttN • OHIHtt
CAk.MJH t « BEM INI'lkt
S. fUbk T01T AT btATTLE U.H. IDIAKE
CBUAN H. Bk LAAPbbOttC. (SCI1TIL O.b.
OUHAfllbM b. BELUH hthTUB STP (kB 9.
OOMAfllSB RlVi.ll kLAB ktNT (IB IB. JO)
TROlBtC B1VLH AT FABAB
1AIL TAHUE AT SABb BABUOB
B.bBl EAST Of SAHUI HOUk SI Fk
'SEDIBKBT kK ADMI HATLR IklAftl
TO* IB CBEH1CAL CO ABLA BAZAMULUS kA
TUNtk CHEMICAL CO AktJ BAZAHMiUb MA
TOktl CUBICAL CU AHLA BAZAhbuU* MA
PEH&ACULA BAZIBDOUb hAVTt MTl BtUL
PCISACOU BACABI»UUb HASTE >ltt BEUL
" BEIIIBIS ABEA MAZAfellUUS BASIL SJTB 1
•UOSCItlT LAKE Sill k. AHfl
"botBBADA PBOBTEBA BOO II BOkKTHCAII
LIB1 Lilt
BOBELUHIE b AT BGObMkJUCIi
BUCBtlE CABAL * L1TCBIJELD
TUOLUBBt BlfLb AT TOOLURBB CITI
.MTAQOBJA LAkB
ALAMO B kk CAL1IA1BIA
SA« rkABCl^CO b. IT CLiriO*
ASH1ABULA BAbbOt
4OBB t, fAiJO blbbllLL. BBLLBAkk B,
CiLLiSItU B AT KO^S LklE
VBCh)i> H SBttl Bti of fOkT A|iTl>Ok
1-90 rkLCvtl OkAiH LAIt kASBIBC
PC> nOllCS. B AT IUCL1D AIE Bk
tkltUTAkl TO Ck*ITA*UOI.A Ckt» 4.4!>
. «OkkSTktAe SIDE «k| 2bO PH
BAH kATtb 1BTAAC AT DAIEBPUHT
.SHILLBOCk B. UPiT Of lOBTNkUOO
2000 fl. ibO»t k. PUUNAL D*H TO HI
»LLbO bATtB lBTA>f ICOkLITl HI
IALAHA MATtk IHIA6t (AALABA b)
HUUDLABb HATLB UTikl (LE«1S k)
SBUBOB15B BltEb AT SkO«OPIli,»
PUIALLfP BltrB AT POJiLLUP
IASBOH ISLABb : ktlL II Hlkl.TUB
NlM JthbH
klk JEKbtl
biSHlkl>T
-------
TABLE A-9. (Continued)
tOL
Ill)
171
112
I1J
176
180
10.1
lit*
las
|04>
1B7
tbD
192
194
19S
I9b
197
• 198
200
iO\
202
20J
204
i OS
20b
- 208
20 1
l\T {IMANCb HLP CLlf CdtU* lit. AH 111
•ITt* DI^TklLT 1JT1IE bETNLCt ffllb
pomji tibt Cbussi*c l.b ni >HLIE PI
CLlkTOb b «T 1-94 balttCtl HbbblSOb
. T I BAlOb 1TI- »1 IICHPIIIS T» TU (115S
SCBIHKCTIPI CbLBJCAL tOHPOKATlOb HO
CABfcllZO (1AL.O tOJtk) Dt$l(li«0|k HU
opr LIPHA* PT AT IH: UUTI-AII. TOIIC
CAbHAllO fL«pU L(>|^|) BCSCklOill
9.&HI SOUTH OP IIKbtJC HEACH
bUICKTU* 1.* >7H1 bL TilTHUb ttf
•UbTM Or LA*I LADI ISLAND AT PUN 4
STMfc" PM|b 7 --- Lilt «tSHmCTOk
bCllCNTOb Cll • TLftTiONII OUTFALL
ADJACENT TO AflbhO^C LlfANHIfL
UUFbbiPA PHUbTLHA 10 H biLliU bTE J
. . ClIkTOI h »T CBOCHH) iT B«: CJT1 Ot
LE01I klVLH AT HUUTN
lohic CHtmcAL conr. biuflifci.ii«n. u
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CAKJiJtlZU (LACU LU1ZA) (EbEkfUlk
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FH-i'jO SC10TO DIG tub bb 1 270 Nh C
MbFUb)! $lbiCT CiO
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Bt«k bMAIIP bk kH OAKLAND NJ
Pill Hl»lk AT mibnT&TUNb. tl
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CLIHTUb N SPILL* hAkft.1 irt; CLINTO
PULhTO NICO
PUCHTU iICO
b»k JtHSLI
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b»k JtiiiEt
ffhllOKT
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kA&NJNClOb
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lAHFOaklA
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riLNIGlb
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lOlhtO NICO
itknubT
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bib lObl
CktbOb
iribiioiT
bA&aipglQI
CNICUN
btk JUb&lil
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klbNIntiTON
bib JJ-HStl
bASHIbCTOH
VUI MTU lllLD
CktCUk
CN10
NLk JEkiff
ktb JLtibET
flliUHb LU.. HI
240. OUO
210. OUO
20(1.000
2uo.ouo
20O.OUO
tva.uuo
IbO.OOO
IbO.OUO
UU.OUO
140.000
Ml.fcUfl
Ilil.OUO
110.000
loo'.ouu
SJ.ogo
HO .000
ttU.OOO
*> 1.000
bO.OOO.
bO.OOO
bolooo
4B.OOO
•i.OOO
40. 000.
40.000
10.000
2^.000
21.000
14.000
2J.7SO
23.00U
2^.210
22.000
20. ISO
io.ogo
20.000
Itr.i^O.
10.000
Ili.UtIO
IO.UUO
.Ib.OUIL
10. OUO
-------
TABLE A-10. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF BENZO(A)ANTHRACENE,
CONCENTRATIONS ARE IN pg/kg.
titoi
Lot
MAIt
HI Ilk
t
2
1
b
1
11
18
19
20
21
22
2J
Jb
21
26
24
i/
J3
li
is
in
tt
m
*o
SJ
ss
bb
gUrkfl Lilt III1. ill! nMLr VALLII/II*
UUtM till 1)1'.. ill* IIAiLc. VALLtl/l'U
VULtk CITI HIS Sill tlAPLt V*LL(.I/PO
ILlUbtH 1-AlkT Cv) HI ATLAITk bk TO A
HI LI, IIAI
(Ml- AT ULklSOk kAt kAiTK
fAkrrttiT MkAL LLABII1KU KIP
lAHCITAM liAH
tttlULUIN LkltK AT tLIITH
aURI'ULT kUlM • IKLAT
bLOl kllTIII AT SlOknllhim
bLUt k)»LH itUIBtkl AT (.UlkOlT)
DLUl kllLk StUlDtkl AI l-4jr> h»
BLUr felftb AT llAkLatSltk UhlUUt
bLUI klftk MDlDEkT AI In bl
HlUt Rite* SltilMkT AT Ib t-T fa*
bi.UF k. kk Cuir./MSSUUHl hlftft
BtUr BlIIEM STATIC* 10 (bk-«0)
PUILLICS ALII MJUH VATtK STBIC t
"pMltLIPS kHl IklLbINT
•OI'ILt MINT Alb CO not ILL AL TU Ul
IOCII CHIA STI> AT CHliTtk if TO BU
AlttklCIt 1. ASOIt iUkkJSt liH
bUMALO Ck AT AHtklCAk illtk
AHLklCAk B. AI ILNAkTO ST.
CULOkADil Illtl bLLUli fAkAEIl DAD
COLUkAUU «. « 1UHA
BUCkCTt CAkAL * UTCHri till
CILA BlltB AT CilLt!>fU CAB
ttAhu'lAIA
ALABU b •« CcLlfAlNIA
OHlkS B bL TI'tflAKA bCb.
bAHIAS fejltk AI UCklALKi
SAkTA tut klltB btLOk VHAIIU UAH
FtAkL BAktHj* 1. LOtt
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kABlLIHILJ BAI
(AHIlLUI HAliBlik
CAhfUM *. • HlflnllLH
CABUJI k • •*• lB»-lkt
TOI-AZ IAAI
K. IOkA OMIHLK IIMr.ll l (JKrMIK
COt-liN Iktll AH bl'ULkrii CnH«
DOUIUKIi Lkfltk Al'UHL MllDrM L'krt*
HUULDLk LULU bl LU. nbLHukLAkl) HASH
PHIILIP:> ALAk sunn nAitH ^i»u- i
CTIIII. l«.>hfU*ATIlik LHlMCAL I>1 * »1 O
LOUbAhAILHIt Ikl tkLkflUk utfll^ M>k
HOOIilli « MLR TIIOM 1HIIT
LIS »lt;»i »AbH kl kDKllI jiH ilk hUAD
BILL ini kumu koctu KUAU CUTIALL i
bA:.HI»CT(,N
U*: HlkCTU*
kAMIlkbTtll
Mt.AII
UNA
IlkA
IAI IFUklllA
kl VAUA
AHlZOkA
kMAbA
m^iuuki
nissouki
KlbSOllkl
A*kSAS
ktkSAS
ALA |i AH A
SOUTH CABOLIBA
(.ILirUkklA
CALirOKIIIA
AhlkOkA
AklXUkA
AkllUHA
IklZOkA
Akl'tOkA
LILIIOkkIA
LAI IIOMIIA
ULIIUkMA
lALIIUHillA
IIAHAII
HAKA1I
BAIAII
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klVAIII
kit ADA
ILIADA
kllAUA
AKIZURA
At>UUkA
«*kSAS
HAkXi.
SLUIH LAhOllkA
PllSIUkl
LtLIIOIiMlA
HM»Dk
AblltlkA
IUI.UU.C
lluuu.u
2*>UU.U
IbUO.O
lUOU.b
1000.0
. bSO.O
bSO.U
b^U.O
MJ.5
HOO.t
noo.o
dO«.0_
200.
:oo.
200.
117.
Ili.
1UO.
100.0
1110. U
IdU.O
40.0
50.0
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so.o
iO.O
40.0
4U.O
50. L
bu.0
JO.fl
5U.O
4U.O
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40.0
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MI.O
•jit.a
MI.O
'.0.0
bu.o
JO.O
JO.O
25 ".li
-------
TABLE A-10. (Continued)
OoS
uic.
I Alt
111**
b«
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b/
bl
bb
66
67
bit
70
71
U
7J
71
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77
7»
79
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02
a*
es
3> at
« 11 -
01 «9
VO
92
Vb
96
100
101
102
1(14
101
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tun
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III
112
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Li!> »fci.is oil Lint MID
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kUS!.ltk hl«LM - nukTl «IU
Hill kilt* IT I5il» URL
THUlfcfcF klKEk 11 IUl.tl.oOU
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LIHI TIHO1 IT MfcD fllkbUk
inthicik fc. IT HUTS i>e.
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TIHPI IL IT 5IUJ.ll fllNL NIZIkllOtIS k
TIBPI Pt IT STOkll HIM' HIZIHUOUS k
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III III
nokiiii
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ktJKTk L«hOLlkl
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SCUT* ClkOLlkl
ICUtM LlkULikl
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lUkl
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HlklLIkO
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llkGII.ll
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likkSILVIkll
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PtkfcSTlVjlkll
1 tkkJTL'Ikll
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1 fkkJILIIkll
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1
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20
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20
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-------
TABLE A-10. (Continued)
Obb
LOl
iTAIt
114
114
lib
11}
lid
in
120
121
122
12)
121
UO
1*1
1J2
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11*
1 Ji
Ub
III
138
mo
w IM
14b"
141
Ma
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1>I
IS2
ISi
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fiokbtALi HIV IT hr 20 HOIITH 1U
Ak«A«!>AS fc ktAk ULkttl klMSAS
kAkSAS C1TI hlTtli IhLAIMLMl »L1 .
JOkkSllk CO ttlTtk LIS1 kOl IkTAie
ni5iU|)HI k.l»l» kT riATTSnOUTk
HISSUUHI kiitk in* iiiao nkiout
rHIlllCS PITkOUVC <-0
tnoio-si Lint: SLUH.I DISCI ooj
HUb'AI lfft.HI<.lL LbHKIHATlOk
trnuckT LiuiDki i>i:»(. HI tee
l*RL till AAf IkDU^TklAl IU.
MtaTtkli lltOVLATt irrLUtNT
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HATMILLk SOUTH STI- ttlLOCkT 001
kAI^*4LLt SOUTH bTt- crimtkt oo i
IkllfcSAS kllKI Akl
COLKIIAk LO-HIUkAULIC &1-OUI DISC
Ck&bfcA MILLACe l-LAkl OUl DliCH
COLLHlk CO kOlfTH, VLAkl 001 UILCH
All CI AH An 111 kCk U02 UI^CdAI.Cr
kALLHIkk LAkDS lllLUCkl 11
BkLLaMC CAMPS UlLUtkf 12
in keciuk setek LAUOMATONI
cuopitik ToptA* kpoe& ovrri ouj
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bUCAk CklEK LACtiOk ElfLULkl HSU
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ri^ui-ur Lk sie Liiiukkt.
rtkTOk LACOUb K»»LUtkl
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kOkTH ftL STP IkllUHT
kLOl klfCk STP bLuL k MAIN III
PAULA kl!
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10
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10
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lu
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10
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10
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10
10
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10
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10
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10
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10
10
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TABLE A-10. (Continued)
Obi
Ib'J
170
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112
111
111
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177
170
174
100
161.
id*'
Ib7
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190 '
191
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194
19b
196
1
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CUkknuUtkt :.j|kt. ifc. hfLO« tlLk* D
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ALLII.MIM H. AT lliAMkLIH Mill ILL
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. . KAkAkHA kl»Eb AT HT. bO UH10I.E
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OHIO tlftb IT DAkklBAL DAH
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lu
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lu
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iu
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10
10
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10
lu
-------
TABLE A-ll.
FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF FLUORENE
CONCENTRATIONS ARE IN Mg/kg.
l_ t » NAIUR iTI IT ntnUIIh Til TO III Si
2 nu.imi.Ton SIP AT MLLIR(.TI.» Tk TO
J TOklk IHtfllCAL 10 AHIA MAZAIIIOUS kA
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* "HlHIli TtkM AT HOILIilJOU H> AhtA S
6 fUBPMlS TIN! IT MULLIKOOD kD IkEI S
1 .. HOOktk HABIIL kOAD CULVKHT
8 SUISUk htl S. OF BJDDLt UkGURU
9.. RE» IOHK, SLUUGB
IU S.f. AlkPUkT JRDUSTklAL PLAkT
U_ U*U;fUf"" " AkM BA.ZAHPOUS »A
U nthfcm:, Tiki «T fkllSLk PUkU ANLA S
N __ BLBPB|!» TtkB 11 rkAisiN PU»I> met s
1* TBlMITIfcl TO CRATTAROU;! CkECK O.J
IS._.t»PM. rt «T sipkn nmi! HIXIIUOII:. H
16 TtDPt fl IT Stum Hint HlllkUOOb H
U SOIBOi SEII1CKS CO IT LOkDUR LI TO
16 bOklHJI SklllCtS CO IT COHIIUI LI TO '
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20 COIDOI SEIIICCS CO IT COkUOl «.| TO
J\ 60lpQ|_$C(*|CfS CO IT COBDOI CI 1O
22 COIbOl SEktICIS CU »T CONOO* C« TO '
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2*1 MtLK Llll ttlk (ICISbUIC US
** tllktssie Eipgsvut list sukiei
26 PICEOR till!! BlpoSUkl lisa btUPI "~
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26 CIEHTROI1CS IIC kkSl IT ISHBIILU •"
22 iciutni DkiiH HM-. 41 cinkLuiTc ,c
J. JO ICIbtHI DIUH HRS IT CHIkLOTTl HC
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3e ikoubikiii cat a co FLIRT SITE RR Mo *
oo - -J!'"5"111 c"«" «* MPorui *k IPCI
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5U Mentals TEkH AT IkAISIR POkll AREA S
•;l — B£"*«»s IM» ii iNirstB PVHD AHEL s
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« atntnis TtiR IT rtiistt rokp AHIA &
4* BEBPBJS TEAR AT fkAISEk PUkD AkEA S
S""
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6100
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-------
TABLE A-11. (Continued)
BCkk
Wl" »V» — •
b) . denim:* iti-i AT misih I-OHO ABCA s
b8 TKkktbSIL llhUbUK* Hl^k bUfcftl AT •
b» TtH»C»ir tUOSVHl bllt SUhILT IT 8
60 TCHkLbStC LIVOSUMt klbfc SUMtf AT J
bl HeiUHi!. IMA HAZAMUUUb NAS1K Slit 1
bJ IUBCH1S ARt4 BAZAhDOUb kASlt SITt 1
bl . BtBHIlS AhEA mUikfiOUSJIliiU Slit 1
64 BAlLkOAII bklvGt
bb ... BAItlLL KOAU BklMfc
66 HEBIHI^ IktA BAZAkOOOb NASlt SITt I
hi kIklLlMIll htl
6B (AST 1ST». iTBtfT BBIUCC
b« KOCA SLUUbH AT DELTA BO BBlOCt
10 S»k JOAtUlB B AT ABT10CB kAMF
11 ACL «1«CI AI Mill Ifttl. DAI IS SlktLT
12 LAS ttCAS HASB AT BOfcTB SBUkC BOkD
!• LAS (A.CAS «>»l LABC HEAD
IS SAB JUAUU1B Bltik.AT blAAi&LAUS CO.
76 LAflt BIBDOCIBO At BBI 10 BNlbbL
11 BUSS1AB BlttB AI UtlAB.IABAIBA.II SL
It BUSS1AB BIflk - HOI It BIO
SO SAB1A CBDZ BBLOB BOCBB BOAII MAST! V
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B2 B1LO BAT
BJ StOBABC •.«.&. BJ. Ja JSratABfc STP
B« SrOBABB B AT SPOBABt STP OUTFAL1
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Bb SPOBABK • l.b Bl BL SPOBABC STP
tl SVOtABK B.AI VUf FAILS ID
BB SVOBAHl B .S HI AD* CUBUk L'ALtBt S
b» SPUIABC J < BB SI .J Bl All C D'AUI
90 SPOAAMB HltCB J.» al. btLOfc CULUk 0
92 BACBKS B * IABIBA all*. NTH IkTAIl (
Si BACHES. B 4.BOUIB • IK IB bklDGbb Bk
9» COLUHII1A B • PASCU *TP IHTJIt (Hall
Si PQBTBtUI 1 l/».Bi Attt ffiCAULLO blf
Sb POkTkCUf B l/« Bl BtibN PUttTELLU !»
9B fclTlSL SPB1BCS J/U Ml BltOK PUHPlkC
99 B1LBLABD BUT 1IIAU UilLUBtrlA Bl.
100 sibkomsn kiveB AT STATE BicakAi 10
101 BIG UIIUCtftE kllKB At HIM TOUSiBB
102 aAktHCSTEI. MA. MATBB SUPPL1
Iflj BOkfr^ CitEB AT U.i. 101 HHlBCt'
I0« CLEAk LABI • HCCtTA. OMICO* MATEfc I
lOb Cllkl LAIt * HtEOSfOHT. OBIIOB NATE
IV!.. _BtB« LB. BIStBfOlk « k.UUttllLI- kAILB
1011 nOBBIliVILLt ABKA BAZAkUOUS kAbTK M
|jyj ALABU LAKE
110 HUntiOLT kl«lk • IkLM
III IIIDA hlftk DI.AH BAblbllLLe
112 AHtbl«.AI B. AT LLHAkTU ST.
Itkkt^SIC
TtkkESSIt
ttkktsstc.
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DtkAll
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CALirUBBIA
CALirONBlA
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kt»AD*
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CALIfOkBIA
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111 ADA
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kASBAICtUB
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bOOO
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2600
2*110
a 500
2SOO
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2SOO
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2500
2500
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21 Jb
2000.
2000
2000
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2000
2000
20UO.
2000
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2000
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lit JO
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-------
TABLE A-11. (Continued)
iu
114
11*
lib
111
118
M*..-
120
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122
12)
124
12b~
120
129
MUIMLO LM At IHLIiKlk Him
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bOULOEk CktEl AT flOUIb .
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COP'PEH ChLlA AD HOULUEl) Cilll
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PEAkL BIBBUN B. UllTB
110 A LI BAI CAkAL
.PI It rOkJ. OemiLfclllB 4 QNIhCI!
132 CABSOB • * BCD IflPlkK
_NJ S..PQiB.Jplf AT. SI ATT tE O.k, IBTAKK ...
114 CliDAB B. Bfl LABOSkOBC (SEA1TLL O.H.
IJi DUtAMSH B. kClOM BtBTQB SIP (RH 9.
136
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140
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141
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TOVEB CBEB1CAL CO AkIA IlktABOOUS MA
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PEISACOLA BAZABDUUb MAS1I blTl BtUL
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kOOSCIELT LAKB SALT B. ABB
LIB1 LAKE
BOI1LUHRE B AT HIMII>Bh|DCB.
•ilCti.il! CAkAL • LI1CBI1BLD
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1-90 rBEEMAl DBAIM lilt MASBIBC
BHTBVt Kill (SOB) . . .
BKLSO MATtk IMTAAl (LOll|.lT^ k)
BAlAkA BATIM IkT'lt (HAIIHA k|
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ANIlUkA
Cll||UHN|t_
ARIZOkA
AkIZOkA
AklZUMA
BAbAll
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1C 110 A
itIAVA
kASBIBbTOB
MASBIBGTOB
MASB1BU10B
BfVAD* ~
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riUBlDA
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lk|tOkA
1OUIS1ABA
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ltd Ut\K
kAShlkCTOk
kASHlkCTUk
k«Mllk(.T'IB
klbllBCTUB
\ lf»i,UO
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IbbM.OO
ii.4a.oo
16)1. UO
lfel?OO.
1591.00
li^Q.uo.
IMO.OO
tsn.oo
14B1.00
1J99.00 _
1240.00
UbO.OO
uov^oo'
I2odtoo~
1200.00
1200.00
I114!so"
.1000, 00 _
1000.00
1000.00
1000.00
JOOO.OO
1000.00
1000,00..
1000.00
BJ4.b4
7B6.IO
.?3)..10.
124.00
109.00.
bSlIoil
639.10
436.90
400.00
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400.00
soo.oo
469.00
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400. UO
400.00
4>'0,00
4UO.OO
-------
TABLE A-ll. (Continued)
ll>«
17U
171
172
I7J
'l76~
176
161 .
162
umm k * hNtntkTik nuk wiiku jkiAi
CHIMALIS k kli ItklklLII
BP kikiuiun k it ctkTkiLii ikTUB
IT GAGING STATlOk
klLSOk kOAb kBIDLt
POBD kEIB TBkBbSStE-GtURCIA 2>TITE L
I81£«riil TO CBITTlkObCI CfcklM «-«>
DUUI.UCI Ck»EI BEtOk HULMOLLlkU BISB
7.4RI EIST OP Slkljf MfJOB ^i DM
BOIkUkE STkEBT CSO
10*1 IKEB IT BIBSNILLIOHB VTP "
LiTTH SIPUJ j IIP;,! or ^Pt.ki_t.h
166 iiTTir S10UI B II llkk CHOIR
111 JOB A BJtEB pkkST Of DIHSBILLTOIIB
166 DBS IIOIBIS B IT IUCUI) I*E Bk " *
'"• ft-**1* *»ST. Of SlkpT BOOB SI PI
1*0 SBBlLkOCI k. UP!,! OF kOkTHkOOO " "
m — cm mm «T mtim 101
194 ~
I96~~
HI
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200
202 ~
J91
206
207
206
•••••SIS h BCIB DEBBI BIBSIS
_ iti»ii»is umi.Ait
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—BO M«TCB COBPIBI Hill* SUPfLt
PBIkfETOk DISPOSIL - SOOTH BBUBSklC '
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T E HllOk STP IT BEBPHIS Tk TO Bl'ss"
BISTE DISPOSAL l«c. kCIPuBT IJ
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klk JBJI&E.I
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CALIfUkllA
BIBSIS
kAkSIS
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kASMlHCTOk
lAkSAS
fljssguai
kEk JLkStl
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Itk JLkSEf
hlSUIBCTOB
T ._ w* '•••• WHn 51 PR pen JEBbEl
SLBtBCL-TIUI CBBH1CIL COkPOklTIO* BO ktk TOBB
SIOBB DftUB 7 «- 1MI NtSKl|l,TO» MSKlfCTO*
ELLIOT Bll kfclB CCkTEB klSMIkttOB
IISI B,llfB ,.B ei.I C«« .,.„ ,,. ."«"!",.
i HtAk
•JU.OOO
MOO. QUO
•100.000
•100.000
200.000
200.000
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200.000
J MO. iPuo.
190. 800
lt!>.opg
Ml. 060.
111.000
J I2>.OUC
I2&.000
in. boo"
llbtOOO
100. &00
1 100.000
100.000
100.000.
100.000
.97.000.
61.000
76.000
.76.000
71.400
Jil.2?0_
60.000
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.J7.000_
JO. 000
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21.640
20.000
-------
TABLE A-12. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF PHENANTHRENE.
CONCENTRATIONS ARE IN Mg/kg.
Ullj
LUf
4
3
M
b
t>
1
b
V
to
11
M
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14
Jb
Ib
II
la
l»
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it
it
it
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26
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24
10
J!
J2
SJ
jn
J5
3b
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J*
HO
H'
a/
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14 a
4«
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M
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54
bb
bb
T [ nAiim bTi- 11 luiipbj-, n. TII nibb
DJ LLJNbTllH bTP II nlLL.INl.rCN Ik 1U
HutiKbh HAniLL tiOAb LULIthf
TUktk L limit Al to AMI.* MiMIUUUS 4*
TUktk LMM1ILAL LU thtt UAlAhlU/US dA
ni-riHl!> THik *T HUlLIMC.fi I.U til If* b
KrnflltS TH>« AT MULtlhuUb lib »H»» S
THll'UTAhl TO ClUTTtklJOUl Ct.tL» (1.1
HtnlLL NU«I> bhlbbt.
HIILhUAI. blllOCt
TO* 11. CHtniCftL V.H »hi» HkZknbUUb hi
KiniMlS TtHN AT tl<«t!>tli PUhlJ AlitA b
flErKlib TEkk AT rbAliat. I'OkD AHtA b
HtflFMlS TIN! AT HOLLIMOOU I.I) ANCA b
ARTHUR MtL (*>OI)
CA^T JUTH. STKtLT HHJI/(.t
GOM.UH blH«ll.eS IU Al 1.0H»(>N LA TO
bUbDU* SLK1LKS CU Al (.ONUIN (.A TO
GUKI'U* btR«l«-ES CO AT t.OHDuH VA TO
CUktUN btkVlCES CU AT GOHUUI i>A TO
CUhU.ll bLRVlCBS III AT UOnUOM I.A TO
COhbUH SIBfKES LO Al CUhUUN (.A 1O
5H11HS liUflf SITt *T DhUOkS HI TO KL
TCmtSStt tAtObUHE hlbR SUIiVII
i- ic ton tivti UPOSUKI his* STUDI
i:«»nTiio»i«.s me MUSI AT AbueniLLie *
. .{mrMuoNJLS i*c ti»si AT AShhiiLkt N
OLD HHI 21 Olinr AT NT HOLtl DC
OLD HHI ^7 DUHP AT HI MOLLf HC
JAI>ru UUCHKS VNCPtHTI AT HtLHOHT Ht
IMDUSTHIAI. cftfp LU PIAHT SITC *M HJ
IMDUSTIIlAL CMKH CO AktA MCAH kOCft H
JNVUSTDIAI. LHtP LU PLAIT SITE »M hU
lirilbTblAL CHtll LU LAKUriLl Kb HOC*
HLnhltlS TtkN AT IhAISth PCJkD AHtA 5
fltrPNlS Ttkk AT rHAIbtN 1•O^D AHtA S
BtpfrHIS Tlfk AT FhAlbtk PUkD AHtA b
HtrU-HlS TtkM AT »HATbtk COHU AhUA b
HtM-HIS Ten* 11 »b4Iblll POkli AhKA L
n^hPMIS Tt»k AT FhAfbKH POtU ANtA b
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ntm-HIS TLfN Al IHA»blh PUkD ANEA b
HfKI-HIb TtkN AT thAlbtN PilKll AHtA r
ntni'nib TIKI AT tiiAibth PU».D »hK» s
nKM'HJf. TtNM AT ttiAIMN POkb *Ht* S
Tc»»»bb£t tlPObUkk MlMi SUK»t» AT k
TtfkbSSt-E f«_H»5flli> H(-k iUMIH Al h
TtkklSSLt 1 APuSUke Hlb* bUhVLI 11 J
. _ fltnmii Atti HiZikDLt/:; »isih birt .1
HEfll-Hli AM LA HAlAallUUS MASlfc ilTl J
MHIHIS «ktA HAiAhllUUb «A>U Sttl 1
TDICUTAHr TO CHATTAMOUCA Cl.tl.K 1.2
JlERlHlb A^EA MtZAhbOUl, MAyil hlTL 1
•tklLlvltl h»l
A HI HUH KILL (bUb)
kUCK SLtiUGH AT ULL1A hli llnlUoh.
lli»r ••'.,» t
nmif'Sft
TLkKI bbit
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rLoni>*
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kOKTH CAKOllMA
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MOUTH LAIiOLlhi
NCJhTH CARULIMA
kOPTH LAhOLIk4
ROH1H CAhOLlkA
1UUTH CAhOLlKA
;OUTM (.AEOLIkA
iuUTM (.AhOLlkl
hQUlH CAhULIkA
ItMNE^SfL
It>»FlS»E
TlHlltbSit
l»ME>b»L
1INNtbj»t
l^kkESbl-l
TtkHtb-ste
itmtisti;
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trkktssre
IfcNNkbStL
llllMt.S!>l>k
ItVHEbSCL
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itkNesste
liotcsrt
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lhrNll>5lE
CIMAI1
kill lUcK
lALltUkHlA
JBOUUU
HOUOL
JJOCO
tuouo
JOOOC
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70UUO
17000
17000
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IUOOC
loono
IOUUO
7MUO
6MOO
03SO
soou
bOOO
SOOb
bOOO
bOOO
bOOO
SOOO
sooo
bOOO
SUOO
bOOO
bOOO
SUOD
buoo
>000
bOOO
. bUOO
sooo
bOUO
bOUU
buuu
bOOO
5(JWt
bOOO
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bOUC
5000
buoo
booo
bOOO
iUUU.
sooo
bUUO
M60U
JOOt
^117
4100
ibflO
-------
TABLE A-12. (Continued)
oo
— itlU_
i./
bu
bO
DM
bb
b_L_
bd
-b9.
70
71
72
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74
7b
76
_77_
78
IM
III
Hi..
B«
as
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67.
68
89 .
95
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100
101 .
102
101
IDS
lOb
I"'
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III
ll/
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SAH JIUI.U1I. h AT 4klllX.ll H»nr
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l«& vktAi kA^n M M.kju inont HUAU
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SAB JuAiiUlk N1VLH AT bT AN 1 M.AIIS ».O.
LAM ntVUOAlRO AT II M| 40 UMIH.I
ROSSlAk kl»»b Al URIAH THkATHIRT PL
._ RUiiiAK Mllta - BVRTt HID
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TOPAZ LAKE
HI 10 liAl
.. HUUiTOR. itUI- ClIARktL.AI TIM TUhRLHb
SPOkADI! k 0.5 m Ab SI'UKANI iTP
SI»OK*k< h AT 1H,m«. IA
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kin ADA
lALIPUkkIA
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kAbhlRklUR
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211'U.OO
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2100.00
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2SUO.OO
2130.00
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20bO.OO
2000. UO
20CO.OO
2000.00
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2000.00
2000.00
2000.00
2000.00
2000.00
2000. UO
1 JOQO.OD
2000.00
2000.00
2000. Ob
2000.00
2000.00
2000. UO
2000. CO
2000. UO
2000. UO
2000.00
1971. Ub
1900.00
IHS7.UO
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| t,ya .00
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II. Jl.bb
ISSM.CU
IS'lO.Uu
-------
TABLE A-12. (Continued)
II J
111
IIS
lib
II'
MM
11V
120
121
122
I2J
I2b
12B
130
141
IJ2
MJ
IJ4
IJb
137
IJB
IJW
mo
141
142
14J
145
I4B
IbO
Ibl
152
IbH
Ibb
IbO
Ib/
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IbO
102
|bl
Ibb
Ibb
Ibl
lou
LUPIiH I hi IK Ah Itilll.lah CitlLK
OIL* HMI.h AT ulLLLblll UAF
AhlHUh HILL (b^U)
LAhbkMN UAH
CUIOpAUO hJVth HiLO. lAHKtl. UAH
. CUlOhAUO K. ff |UnA
MHIILU1 HAIillON
PLAhL HAhhl-k L. U.IK
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CAk&0« H » km IrHHt
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UltkAfllbN hlVLN NtAH HtkT (fc« IB. JO)
TbULKLL MlVEH AT lAhAb
LA hi TAHOt AT SAkb HAhl.OH
M.bHl EAS1 OP SAkOl HOUR bl PK
7.4HI LAST 6r SAUDI HCOK ST PR
_. lOAkORE STREET CbO
SEblttEkf kH ADAlk HATLH INliKL
TUHfcH CHLK1CJL LO A*»A HAZAkDUUb UA
TOkfB CHLRICAL CO ANLA HAZAHOOUb HA
yOHIR CHEHJLAL CO ARIA HAZAHUOOS 4A
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1-9H THtLMAI BHAlk — LAK1 kAbHlkb
HOObEtELT LAKL SALT H . AHH
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LIHI LAKE
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THII'OTAbl 10 CUATTAkDOlA thtm l|.4b
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kCkk-UAH kATLR bUII'LI HO N
no kATCk COHPAkl kAltri SUflLI
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HAtk'b bAklTAkl LAkUPILL - KtPiruND
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kti III||K
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2 I242.0U
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2 1200. UO
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2 1200.00
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1100.00
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1000.00
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400. UO
400.00
-------
TABLE A-12. (Continued)
on:.
LUC
170
1/1
\n
\n
MM
lib
1"
IBU
|H|
\0l
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lib
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Ui 201 .
202
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206
201
PUIAIL4II MIVIN kl lUIAlLJI'
VAShllN JjLANO : mill II (l.t)
VAbMlk ISLAND : HtLL 14 {'.!)
UNIOk h • HKHMUnm fUH BA'tlli IklAK
LHIkALII h Ik ClnTbALIA
HF kFHAUKUn h « lINlhALI* INTAKfc
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ADJAltNT SOUTH MDt Ok' HOhk
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310.000
170.000
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jnj.soo
29
-------
TABLE A-13.
1
2
J
b
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10
II
M
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14
20
21
26
2tt
JJ
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j*
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TABLE A-13. (Continued)
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TABLE A-13. (Continued)
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TAbLE A-13. (Continued)
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TABLE A-14.
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TABLE" A-14. (Continued)
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TABLE A-14. (Continued)
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170
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TABLE A-14. (Continued)
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TABLE A-15. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF ALDRIN.
CONCENTRATIONS ARE IN yg/Kg.
1
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TABLE A-15. (Continued)
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119.900
I2b.000
lib. 000 .
lbb.900
101.00(1
lOb.bOO
IbO.OUO
. .100.000
100.000
lub.ocb
1 HO. 000
lOb.OOb
100. OOL
100.000
-------
TABLE A-15. (Continued)
Ul'b
11 1
114
lib
lib
III
lib
IJU
HI
122
12J
124
12b
12b
129
1J1
134
JW-
IJb
Ub
137
IJd
IJM
140
141
3> 142
1 14J
S \n
140
147
I4B
149
lit)
Ibl
IbJ
Ibb
Ibb
Iba
lb*
loo
ItJ
Ik4
Ub
Itb
it;
Ua
CAblVILlt iiAhnOk.hlthlbAB
ClKVlLAkD kABuUB
ILLVLLANb HAftbOk
btLL L1TI OHAUACt LAVAL
HAHRlbVILLt HARbUk
1RDIANA HAhUUB
IBIiJANA HAftMOH
INDIANA MAkbUfc
JRUNDruOOll bAT
IkOBOLUUOlr BAI
Ltb LBAiMkl IblAkUb ClilkNILS
Lib CHAkEAbl ISLAkUb CnANNlLS
LIT1LK bALftOB HlVkH
ROBhOL HA MUM
HUBI.UI! HAdbOH
OGULBSBUBb
PEBblUKLL BABbOH
POlkT LOOkOUT HABbOR
PCiRl NISHlkCTOB
IRVlkt AVekUE bklDLL
CAHPUS liBlKB BBlUCt
SA1BT LOUIS hMtH
bAlkl LOUli HIILi.
SAlkT LOOIb BlVtB
_ . SAlkT LUUlb Bllth
SA1BT LCU1S HIVtM
SAlkT LCUlb hlttb
Clt»lLAkU hABbOk
CLLVkLABI) BAUhOtt
HERPBIb Tthk AT HUILT.COU H> AHhA b
P. «Ahg. Lk-B Ctkl PukTION; l>. HAku
P. HAbu. LK« OLD tBTP BISCh; P. HAH
Ptkt HAkgUI.TTL LK-CfcNTtH; 1. BAHy.
P. HAku. LK BKAM UOM CnKH; P. NABL.
P. BAKO. Lh IB SK POH11UB; P. HAKU.
P. flAm;. Lk 111 SV POHT10B; P. HAhU.
IIULUTN BAkhON
DULUTH BAkKOB
VU1UTH BAkhUri
DULOTB HA hi OK
DULOTH bABbuh
DULUTH hAHhOB
DULUTH HAkl'OB
LAkt HACHLlKle. Mk_T 1URB 1 hO«
LABAblAk klVLR AT LALtlN
kALIHl bThlAH AT kALlbl. O/HU. hi
AT h»Lk bAI UhlVt bhlUGL
LLIVrLAkD HAhhbh
tltHUhP hA|.bUI.
t-LcVCLAkU HAknuB
CLMkLAkU hAkaOk
CLLttLANI> UAhbUN
CL»t»LAkll HAnilOk
CLI «> LAkll nAnituh
CL»V»LAkU HAhUOk
LLkttLAkll iiAriUiik
- •• • -
CB10
IHlli
lOUlbl ABA
MlH!(.Ak
JublABA
IBblABA
IBblAbA
NKV TObK
riLlilLAk
MICBlbAk
ktk lUlik
Btk lOAll
kISLUkSIB
HKHICAk
klbCOBSIB
CALltUkBIA
CALlFOkklA
blSCONSU
klbLUk^JN
klM'ORSlB
BlbLOBSIB
NIbCUkSIB
klSCOkSlk
CHIO
LIIJO
TtBkEbSfE
BAbON CO. Hi
DAbOB CO.. 41
BASCB CC., ill
KASUB CC.. HJ
nlLHICAN
HAbUB I.O., HI
MBkkSOTA
kISCOfcbIN
HISlOkSlk
Blf.LOfcSlB
HlbCOkblB
BI.COBblk
klbLOBblN
OLAdCAA
IIAkAII
(.ALICOkklA
Okie
kbiU
LIllL
CHJO
L.IIO
LHlC
OB JO i
CNIO i
s em
lilO.OOO
luo.ouo
100.000
luo.oco
loo.oot
100.000
100.000
100. (100
100.000
loo.ooo
UG.UOO
1UO.OOO
100.000
100.000
loo. oiio
100.000
100.000
100.000
100.0(10
100.000
100.000
100.000
1 100.000 ^^
100.000
100.001)
luo.ouo
100.000
100.000
1UO.UOO
100.000
100.000
ioo.ooo
100.000
100.000
100.000
100.000
luo.uoo
10U.UUU
luo.uoo
100.000
100.000
luu.ooo
100. DUO
v^jsa
76.000
IH.HhO
70.000
/li.UUO
7«_l,000__
rn.ooo
70.000
70.000
/u.UOl
Jo. 000
7O.UIiU
70.000
-------
TABLE A-15. (Continued)
en
•vj
Iby
170
171
172
1 /4
1/6
117
176
161)
Ittl
Ib2
It 3
164
Ibb
Ib7
Ib8
189
ISO
IU)
IVt.
200
202
3t"
204
206
20 /
20e
—ft-
211
412
21 J
214
*!•-._
210
21V
22'J
7 » j
22j
• tll.| CHMK Nh HIMLAkl), FLA.
JAbCO HUC.MI*, PhOUhl. AT bl LHOkT I1L
t-?l LAKAL AT CllkT HUOtt Ib kh bOC
LAM »l!hhtT. kOM'IH tkb : 1C B|.
Clttl.lANU bAbHOK
CL<»I LAkb HANBO!
CLMLIAkb HAHbOli
. CLt«»LAMb HAMHOh
CLMltLANO IIANbOh
CLLHILAkb rlAfcbOk
GklthD fOHTAGh • Hi Nfc t jOl A
ChAMD POhlAGtfjiilbM LbO FA
GHAhCi POkTACfr F«lfcfctbOT*
. EEl'Im""1 ">T """ "UTL"B T°
CULI INT. CO«ST. klTLkHAI Al hIC
GOhbOk bthtlCCS CO AT GOhbU* GA TO
fLt»FLAkD HAtabOh
— UJtkAS llli uAlkh THLAlnKm n».
niiioum kl«Lh MEAb |4bU blJDCe
niS&OUbl K1VM, Al blOUI Clll
fccnk-«Ay KATtn SUI-PLI no H
no WATEH LONI>tll| bA)fc)i SUHIJ
ClHAhhUN bl«th ktAh COIHNII
—JUILU S1GOK. S at |> AH ISM «i . f h,f
01IUU OtSCAIKtS. AT bNI 97 CKOSS
biiou r 1*1/0 in jut AT H«> ij chois
IPO PtET SOUTH 0) UAK
II kl«LN AT HtlD>Lb»Kb LOCk 114
_J^rl BKLOy •. h»|ikik(.iuk AI ^uboii w
MOhTb Of L«itl LAUI ISLAMb »T PnJ**
bE.HI«D KktAKIiATtM 4000 FT :OUTh Of
riAlth 01STMCT IklAKL ULTVIfck f/lkb
..POkth tint cao!.5i>r. i.b HI A....WF p.
1000 IT bLLoy 111 j bHUCL Ik ST JOH
OLb HT 11 I.BC Abut I GOULb^ BILL i O
LITTLL AHgA.bAS a AT HI (IS 'T
THlklTI h A| HLIT I1IL KU
HtnlhlS TIM AT HULLIbUOU Ib AhhA S
ntninia Ti MI AT notmono n, AKLA b
PuJtAU MVtk bfcAh »UHT SnilH.Ahl
SHCLLUULh h. Ut^l Ot kulllilkObl/
STAOKILn IHLHICAL — IMLINlD ALUr I
STUMIEuk hlviii b,ill,»An O.^S rj.'
HILLi.»llAkM nAlUb 1/4 »h HiAunkl
HOLLAkb HAkiiUk. r^LUIGAN
HOLLANb HAhluK. PlLHICAk
bOLLANb hAnnOa. RlCMK.Ak
11ATL
lLOhlbA
ILLfclbA
lUUIbl ANA
CII1O
CHIU
CHIO
CHIO
tlllfl
OHIO
GH10
THIO
CblO
niVktsoiA
IlkMLSOTA
h I HHLliOTA
»tkBOkT
«l Vlbl
TtlAS
CtOMCJA
CblO
ILbA
KAISAS
OHLAHOnA
IOU1S| AhA
LOUISIANA
lOUlSIAkA
CALlfOhblA
RfckTOCkf
tfhnOMT '
• fkflOIT
VtHHOkT
VfkhODT
KANSAS
T»XAS
TKLAHOnA
ILkJ
LHIGUk
BKhK.AI.
TH»5
M.. Ji •: I j
Ml hll.AM
HKHIGAk
-J Ht AM
1)0.0000
SJ.OOUb
bo. oooo
so. oooo
SO .0000
su.ooou
so. oooo
SO.OOOb
so. oooo
so. oooo
so. oooo
so.oouo
so. oooo
so. oooo
so. oooo
so. oooo
SO. OOOO
so.oouo
so. oooo
SO.bObO
1 4S.OOOO
4S.OOOO "
4S.OOOC
IS. 0000
4S.OOOO
«2.79bO
. 40.0000
40.0000
40.0000
00.0000
40.0000
40.0000
1 10.0000
40.0000
40.0000
40.0000
40,0000
40.0000
40.0009
40.0000
4O.OOOO
40.0000
40.0000
40.00LC
90,0000
.*7.00b(j
->u. UOIO
JS.OOOO
JJ.OOOb
jo. oooo
ju.oouo
JU.OOUO
-------
TABLE A-16. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF CHLORDANE.
CONCENTRATIONS ARE IN ug/kg.
LUC
i.ATl
fit**
1
1
J
n
i
t
1
II
?
10
u
14
in
n
16
17
18
19
20
21
22
VJ
2«
«
26
21
JO
2V
T ™
t!n 32
00 JJ
J«
31
J6
i?
JB
*»
40
41
• 4
Hi
HI
Kb
Mb
« 1
KM
iy
ii)
bl
b*
3 J
bU
bb
bb
LIH1T IIILl CHtt* -..IP AT PkllLltAMl) *
Slflb BATUU AT bH J'j
nOahlSTOHN iTP Al HURklSTOhH Ti
(.UlfllWmCb INC tti.il IT iSIHlLLE k
LAUAtiA fcl»tB btl- HI IllimUI.MAIt »L I
WALLtl CM STP 4T LkSbtnEk *L 1(1 VAL
ALbtMTVlllt «tb1 blDt bTt> »T »LBLHT
STRtMUHlDCt Llkt/L(>kLn L»*f COHPbl>l
LalULLLlTL bTV M liFULLLTll 1* 1U
tltOSfOht bll> AT MkOSfOhr Tk TU b
Ol, CutKK kl kUHlH HCH7 ST. Ik BUT
bktftt aiVEh ftT KlbSA. 1>H
MO LtUUtHt»Lfc bTV AT Ku LAUD»kCALk
" WEST bTf IT UAH hlDGE Tk TU t«SI fO
...POTATO r« STI> AT I.HHHH o* TU POTA
EAil Hll(l>£ bTP AT UST hlbLt IN bO
10 LAUUkKOALE SIP AT AU LAUUtliDALI
yESlblOL STP AT HIGH HUNT kC TU III
hAST STf 11 UAH HIUGt TK TU CUMIN
TUSCUIbli iTP AT TUbLUAblA IL TU bf
HtKDI Ck STP *b IHUHASIILLt kt Tc H
lUb k rOkA kLM H11 KB AT fT LAUUAhbA
CALLATI* bTf AT CALLATIk Tk TO CUflb
HfiHANE bllUCe STt> AT ll>l* kC It IIAk
HlUbU CB Sl*> AT JUHMSOk CJTI TH TO
"~ BfcLflOMT STP-- CiUASe PIT, llbptb
CtCAHTUDII bTI* II ClDAIITOlIk GA TU h]
DktCNIUCe STP AT bAkOklDCC T* TU PR
BBAlMLBb bTP AT CHATTAiOOUA Tk TO S
•0 LAUDtHDALL STP AT iO LAUUfcbDALK
PATTUN CH bTP AT B I fin 1 HCHiB Al TO P
HOlLtUOOU bTP AT HOLLIMOOU FLA TO A
roilkTH I'H !!»• AT »»OJtIli.t Til TO Tt
FT fcbLKtB ^TP AT M hUCKKh IL TO CL
bMILTUATkh STP Al btfttlMATtk TI TO
HtikUtHbuli STP AT HtklltHbOH (1 To Uh
CflfcEkKIILLr fir AT CkLfektKIILL fk T
MILU HAI
HOOIH Alb lUbCC LAbt AT VAlllUbTA i.A
HEHPHIS TtN» AT HblLlkUOU >D AMtA S
pHfcHH C1T> STP Al Phtkll HT« AL
MAtirOBTCk LAKK/LimtN AhtA tOrfObllE
SILALAUtA M*e Pbillb STP AT bILALA
lUhlHblbl bTP Al UbMHAR 1C TU E 1.1 to
LAtAI^TTt ^Tf AT LAH»tTTt CA TO fb
THll>M SIP AT TNIOk CA 1U CliATTOUbA
T HC1« FISTS 1 DC. STP AT 1HU( AL TO k)LL
•EUSt hit LH STP AT bALtlbH kL TU It
. MAHUivlLl bAI
CtNMA blP A1 (.IftLVA AL TO PtA kl«t
ilLH STt AT LktU'. Al 1C LITTLt CAM
TALLtlltcA STP «LI 1 Al TALLIDtLA AL
bilf 1 III* ILLI JTI- Al ^rtl LhY» 1 LLi- fl. T
HAhkltlAk SIP Al Jl»l.nIrlK T» l(> CAdl.
bhAII^ VALlLt ->1H AT Mlitlll>.(,IIAn Al.
U1LA Klkl.h AT LlLLtbPlL UAr
ALAbAKt
TtlAS
ItkMCSblb
bOhTtt LAHULikA
ALAHAftA
ALABAMA
ALAbAHA
Nth JEMbtl
TtNMKbSri!
nimtsstE
KlLHICAk
CklCUl
»LUhll)A
TtkKtbSlt
CkUkCIA
TtkkfcSStE
FLOhlUA
kllbTII LtHULINA
IhkNESStE
ALAbAHA
kUkTV CAHUllkA
PLOIIlUA
TFHNKbStr
kOkTH CANULlkA
TUlHtSbB?
INDIANA
CfUkCl A
UNREbSLt
UkMtbSie
ILUhlDA
ALABAMA
fLOklDA
TLNNtbSEt
ALAbAHA
ILNkLbStt
ItMTUCtI
ILkkfcLStt
HAkAlI
ftCjhCIA
TLkkkbStt!
ALAbAHA
lib Jkkbkf
ALAHABA
bUhTB CAkOLikA
LLUfctlA
CEUkUl A
AIAHAHA
(OhTH tAHULIkA
DAkAll
ALAbAMA
ALAIiAllA
JILAhAflA
TtM.t-bH
ILkkt^SL^
»l AiiAH A
JlillUkA
1'jliOOO
iibtoO
jOOUt
^UUOO
IttbUO
UUbO
ItOOU
llb'IU
llbMU
11 l«tl
IbJ'.U
•*!».»
700U
60bC
bOUO
SBbU
bl^C
•<2IU
bCOII
bOOO
bOOU
M99S
4iy&o
«bbO
«!>9U
4«JO
«ObO
MOOO
JS<*i
J400
JKJO
JtflO
Jbkl
3500
jiyt
jouo
JJ-,0
J3JJ
3Vb(l
3^110
J19b
3103
30f<0
jUi,b
JCOU
31)00
^SOO
JSUO
.^V|7.
U 6(1
^'jJO
^b/U
^UbO
;jio
Jji 0
^2j2
-------
TABLE A_16. (Continued)
Uob
!>7
bb
bO
o(
b« AT kASMIILLE Tk TO I'h
. ALAHU LAKt
JACkSOkVILLI! STF AT J ACftSOk 11 LLE AL
_ . lfOM.OLT klVEn • InlAI
TObA RlVtfc HEAD HA bib V J LLe
iAJlOLOl HAhUUM
inehllAh N. AT tLHANTO ST.
miFlAI.ll ik AT AMhK'AJI h|*Jk
CkhSON k (t »t» tnnht
_ SALlkAS hl«Ek AT C.OkZALlib
bbULDLH LHltK AT nUUTH
CAhbON h. f. fHlt^mn
OKfckb k bL TlNtHAUA Hkb.
. SAkTA AkA k|«tR (ILLON PNAOu UAH
bOULOJ.il CHIEK AbOlt HUOkH LRtEl
«BJ.hJCAk «, AhOlt bOkhJSl bd
AntTHICAN H. AT kAITS Att.
COPPfeh CkK>.K AH HQULUkk LhtEK
*-»Kt TAbOE AT bAMU HAHbOl
... »0 UUOtliOALf! SIP AT «0 iAUPthPitt
LAHOITAk DAB
- MH17I-S CH iTP IT »li«»ilLt T" TO CO
COlOhAUO kllEtt DhLCH PAHKtl, I»AH
TOkk CbEtk blH AT JAbtLh AL TO TUkk
tULonipp M. a TUNA
SANL CMtEk AT TlMklTOklAL IU; HEkTO
Ftfhl. HikhuR I, LbLh
ALA kAl CAfcAL
b. KUIIK O.IHkK klVtH „ UdlHM
ST JOK K Uk^T dILLbUALK HN1 »•; HI LLili
.. HAUSbOtlO blP AT kAUtbbOHo kC TO bh
. TAktiOhO bT^ AT lAnhOhO kC 1O TAk ril
CAMYtfc LK IN N. bAblk. MASTINIS 1 X f
1-OHC Lk Ik C^«T ..»•.!• hol>, ,kt ..t
ri»r. in IN ||. l,Abl». f kAl HI LV ILLt T
BJC PUnTAGL LAKf-SOUTM bAblM; Ottlt
{••Cl!>fKCT L AT H«A LA kll ^AkAlOGA CA
_ HOO-KILT L»*t bALI (,, AHtl
UAVlb tK AT BILLlk iThltT; ContfOCK
HAJLl- Ch Al OLIIb|IA|. MfiiKl- COB- ill
TO«mik.'»llLL bit AT TOnmiHiVJLLL
J£fl tfiLlm LllI ili- AI JlMiHLOn til
SUUIN hlVth - ^kAI-flNT bHUALS
LAKI CITI TTI- Al LAilt Lin ii. TO LI
PLA!.l»n Ch AT HAhljr A»f; in» ot G
— t'**' f«> h ,T MOhTit :ni,.i ^i; hum,.
KALlhl :.THIAn AT II A 1 1 N 1 . uAIIU. HI
OkAKtlUUKC •.!»• Al CBAkl-tl.uH, ^ ,L
L hh AkTlMAH If KtAh bAllltLhOhO
•TAll
HOIiv I A .
DIChloAk , 0.00
"••-• : S:5J
bOOTM CAMQLlkA ' ^OHO.OO
TtkNtbSfK ' " '" '"
AU|Z,0!IA
ALAbAIIA
dAkAH
CALUOhllA
k>VAOA
CALlfOhkJA
AHIZOkA
kLIAUA
CALirOhMIA
AhJZOkA
CALirOhkIA
AlilZONA
•tKADA
ItVAUt
AtlZOMA
ALAbAIIA
ILAhAflA
HlCMlbAk
HAkAII
klVAUA
rlLHlCAl
kCJ,TH CAROLINA
kOaTH CAHULlk*
DILMJbAk
CRHICAN
PILHIbAt
CALItOhllA
AhJZCHA
kALAKAZOO LU..ni
MICHIbAk
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SUUTb CAkOL|»A
MC II 11. AN
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LC01M CAhOl INA
MkNbTLVANlA
2000.00 "
IWkO.OO
IBJoloO
17tO.OO
172t.OO
111 t. 00
IbSH.OO
itsn.oo
IbfcH.UG
ItQO.OO
I6JNOO
1'JVO.OO
__ Ibbl.dO
isooloo
IMbJ.LO
1170.00
IMbl.OO
laoo.oo
IJ«9,00
uoo.oo
I2i0.'o0
1110.00 '
1090.00
IOOS.OO
toco. oo
1000.00
1000.00
999.90
9io.uo
VtH.Ob
9bO.UO_
0<0. Ob
H30.00
ui't. .IS
O.'J.LO
010.00
-------
TABLE A-16. (Continued)
UK
VIATL
MIU
Ill
lib
111
lid
IIM
140
124
lib
IJO
1 Jl
1J4
IJ3
MM
Ub
U7
IJd
HO
Ul
112
cr> i*s
0 146
U/
Utf
1 bO
1*1
112
1'jJ
IbM
Ibb
HI
IbJ
Ibb
Ub
UH
Pitt Mil k-k ..!<• >T tilhhlRt HIU. IL
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NOktLUnkt h A r >tHiblii IUI.K
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HtLftOkT blt-HAi H, ilUhl '-.Lt.tCt , it,
bkMb h A loo AT iiuUMOK, ret.
faObLIHC GHIKk bll Al liLULlliO bfaLtU
PAlAt.OKlA LAHt
ALtitXTVlLLL LAbl Jlllt !iTP Al AltLM
ffcr.lA Fl AT bTU»M nlKI H«ZAil4.UU:> *
AL'AKU « Nil LAlll-AljilA
SAB iHANtmu U. ATCLUIOk
PAbbAlL hJ'Lli JirAil LliAIHAIt «J
iAhl nUK^Uk htAh '. AtL*U«Sj 11, Il-Aill
t>ASS«!C N AT HANlilbUU NJ
GOkbOll HUm II IAVLt!i,FLA
MHKKHuUbt GULLI Al CObTA ML* bl . ,
"aOUbTQK ShlH CKtfiNI-L Al HkO tbN
t'OMillU Tl AT PoUlAKU tLACIi I'll
ilUMTJIIU bAIUU AT 1-h CIU Hl'UiTU*. T
SIB! HAIOU AT NOU^TOk. 1 11 .
bT Joe k UfSr hlLLbUALfc nHI f ;!• 1 LLbb
LOkL-R GlthCLLH lAKt/bUHFACI CUHPbbl
OTh»h KATIBS 11 IJdHLLIl
_b«AbAn STI1 AT GkAhAII kC TO TOkM hhA
StfUUHAl* k AT bUAkta nlObl ho iILK
UAlALLt bTkKAH AT HAJFAHU. UAUU. UJ
HACkEKSACA ll AT JlAtlll kbACft MJ
TNIklTI H Al dllT LIki. MO
• OCA SLLULB AT LtLjA hi) bMJII(,t
SAM JUAlUlk H Al AATIULM Hifll-
BEL NlttN IT N10 DILL. DMJS STHttT
LAS *rCAb »HbH Al kOfcTM ilK.Kt HUAU
C1LDILLK f»( LAM HEAD
LAS (tUlb hAf LAM H»AU
* LAAt FILLSIiBR! kiAk 5LLTT ( I>«H
bA» JOAIUIN HltLI. AT MA«1bLAl>b CO.
L*Kt HikKILJHU AT n«I 40 hklVLK
BULSlAk HJVEII AT UhJAri TkEATHLkT fL
flUbSIAN hIVfh - HukTt hIC
HAl> hlVi.ll »T t ,1L1 LAI t
Thill Kit hlVLh AT 1 4hAL
TdUlAkt! hllLk Al LUCA.tllJIi
SAkTA ChUZ MtLO« hOLKIi HO At MA.bTL U
AUhAll1. Ch. bILu. ill'
L. hLACt CH hUANbTON Ml; HUbkL(.Ok
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ill). QUO
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-------
TABLE A-16. (Continued)
171
I'J
1 / bAIUU AT hUAhll gOAD HkAh HI)
— PAJ! — ^»H H AT kill Cit (.liAHAH SI. Ik h
SIBS bllOU AT HlkAfl ClAhllE bT.. HUU
b*Ak Cfclt« AT ST. PtTthSbOkl.. H.A.
NlVAkMA B1»KB
. SICAnOHf Ck ImbTb HAbUk «Hlp; Vt«AI
lIAkASUUAk KlUtH 41 bljUAkkUli kJ
HKl LAklLh »T ImVLUm Of FIAT ,t.vr
HUU ihlr mikltL-COHr k !>I«s bAI
— iinr
HC.hlU LlhUMkA
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ktb JthAtl
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-------
TABLE A-17.
ELEVATED SEDIMENT
OF DDT.
fV)
uhb
1
2
i
U
b
b
7
a
10
12
U
In
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21
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27
2B
29
.*!
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3«
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M
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LOl
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tbLAkAHA hlKtd UHbl'ktAK U.I HI.
FLU bTATlUk LUK o ON LlIU titttCHUbr
FUP .TATJOk LOU J ON LJIKt OkMCHUtit
bELrONT Sir-- t!b»ASt I'lT. JkUPLS
FCI) iTATIOk LOl 1 ON LAME OttlLMOUE
bTM.HhlDf.t LAkt/LOtfth LAKr COHPOS1
•ILL CK .T HANAbAiklb NJ
SNAKt hIVth AT NlbbA, OH
ANTUTAF. L AT UAGtRbTLmN. Ill)
RLACKHATtk. HI Dtl,
LITTLf HHITtUAk bAlOU AT HLUbTUN.Tt
. . bTUhCtOk fcJVtH UPSTREAM U..S HI.
ULAHtri POkl bRoOA
_ CON AhtA NO 1 HttUN S-bA Kb LOlAhA
BFJ1TER POku bKUO»
NtCHFb h AT ALTU M HNI bS II hi 01,
EAST bhANCb bAbb hlVEN NLAh NtN bfct
SULPHUR HIKER kh TALCO. IEI.
SHlkLOb HfcUOK
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B bk ANTIETAH Ct kEAk HtlNiESbUHO
LEON Ch AT PkMATt kD OFF LU1NTA
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. E-2E CANAL Al CLINT HCOHt RU NR HOC.
TRIfclTT II AT HeLT LINt kL
__COLOKAbO H-AHO»l TlllAL-TOHk LARK 4
FLINT H. .bHl DHk FHH bTATt DUCK
CHATTAHUUCHEE blttk OOKNbtki.AB or U
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TOMS k AT TOHb R »J
bl.'Ck bAIUU NEAR bbbbt^. AM.
bHAtb bAIUU A/ bt(-TT bTBEBl . Al RUU
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lul- k »0kk Nt.k k hhWb ULVU Al »T LA
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VILMITTt '. IMt»1
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HAf.rokT(,i, i4,t/Lu.i. *..tA n.nius.it
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hOHr.tSl.Ui lAKc k>Ai. HUulltb. 1 nl .
HlllSltJhO LANAL A~ Ub Ml Al IrtkM
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KA1NE
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klk JEHSi'I
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MICHIGAN
LOUISIANA
btk jeNStl
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N
1
1
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1
1
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1
1
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1
2
1
2
1
1
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1 IliUUO
1 /100
IMJUb
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I1S9
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060
HIS
677
fcOb
bOO
500
HiO
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21U
200
lay
H.5
1HU
171
110
IV U
I/O
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IbU
1ST
1SU
IMS
lib
-------
TABLE A-17. (Continued)
il
bo
bO
LI
bJ
65
bb
btt
70
71
72
1J
7q
7i
76
77
7d
BO
bl
82
bj
B«
rib
S •;
90
9b
100
ivl
102
104
lOb
lOo
lo*
lud
llu
1 II
112
SMITH HkUUk
Off LAPtlAk VI AT IH. OUT KALI TUIIC
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bAblK 1
N fOkft UP TK1M1TI H AT DALlAb. A
lOb H khk k CA Ab bOL LAC kB »T LAO
LlkCULk PAHK/CKlTIk LAUP COBFObllt
CHUSSilCKb C AT (.hUVPVlLLE kJ
DKLAVAHt MVfck AT CHLbTLh IA
1Mb M1LLSOLHO L*_iT .kblllir kL k. Ilk
LAM TObCALOOSA AT HILLTOP LblATf-
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CABIOS liklUC uklUGt
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CEIiAk HlVlk 0.2u MIL! UPSTnLAft
CHULULATi bAIUU Ml. MUHT LAV At A. 1 LI
L'AktUlLLt HMfcb kk LOLT. AkX.
PHOSPBCT L AT P8A (A kk bAbATUC» CA
ruukniLK bkuuk
II 01) hkbbK
taST P*l t AT T«nl-A. FLA HI
EL LAIIPO - Bk Ok ill 71
LlTTLt coDUAHii LIMCUK
LAAt PhO«ll>EkLE HbkTH OP LAKL PkU»
- »T b«CK bA| PRIHL DH1H.E
CkACALk JACK SLOObH IlkAINACt CtL
— LilTU kl»IR AT US kT 1111 kk H1LLLII
PElllEA CkLtft TklbUTAHI kKAk blhASBU
LMl fboVIDKktL «T LAKt fdb«| PtkCt.
OTTlh bkOOK
TOCHtKTOk CkttK »T TULMrtlOII kJ
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HUMTI«>: HAIUO Al 1-H blO lilillbTOk. 1
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b^Ut' i, kk tLAHUk kC
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bTATL
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kin jtasu
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1LIAS
kill JthSCI
TIIAS
DCklH CAkOLlkA
kOkTn ClhOLlkA
kCkTH CtkOLIkA
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kOkTH lAkOLIkl
ktalH CAKOLIkA
kllklH CAHOLINA
ktlkTH LAkOLlkA
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Until H LAnllLlkA
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IUi
-------
TABLE A-17. (Continued)
uhi
IU
114
113
lib
112
lib
II*
I2U
121
LAJ-
lii
I2b
130
131
M3
134
us
Ub
Ul
13d
us
140
142
143
144
146
1AL.
I4b
14V
ISO
m
1b4
lib
1b6
lib"
IbO
lb.1
-U3.
164
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Ibb
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TAk HlltR AT TAHOOHO KC
dill! CHI IF. 4 be. H.I *., nm. b,TM «c
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tAbftlb k AT lAUKIk COLLEGE
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bbAXUS k AT KASblbCTOb AT US 90
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bOKbF KlVth btAk fT. ktCEbilTV
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AT US ^71
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PAiSAlt HlteR bLAH IILLlHCTOk bj
SIHS bAIUU AT HlkAR LLAkKf LT . hOU
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—ilUMALO BA10U 11 bLULIOb. IC1.
lOh GOLUKb bATt ILJll LA bb bAI-LKS* »
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78.0000
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74.0000
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71.0000
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-------
TABLE A-17. (Continued)
l
Ot
in
uoa —
Ib*
170
i n
172
i n
I7b
177
1/B
__ n*
160
lol
IbJ
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IBb
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190
191
I9J
194
195
196
. til
198
199
200
201
202
. xii i
2OU
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ANT1ITAM C Nk •J|iAkiboLh(.. M,
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BAIOU COUhfAbLtAU AT kAMIIkOTOt. LA
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nlbLHAkHIL MOnTH 01 bAI JilE
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-------
TABLE A-18.
°F "PTACHU*.
2
J
M
>_
1
tt
1
10
U__
1^
13
In
li
16
11
!*
20
2t
21
21
24
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20
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31
12
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10
— — •_ 41
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AHEklCAk N. AT tLflAITO 51'.
bUMALO LH AT AfltHCAK Nl«tb
SALINAS Mllfi AT I>0*£ALES
UOIiLDKN CNLtA AT HCUTB
CAhiOM k. « HJVLHVltV
_0ltlki H bl TlkfcttAhA hH>.
SANTA AHA UKCH HLLUN PhADU DAH
. BOUJOtk LHtEft AbLVt . 1LULH (HkKK
AMEklCAl k. AeuVt bUkfclbt tab
AHthlLAk R. AT »A1TS AVtT.
COI'l-tN Chltfc Ah bUULUkh LH>tK
LAhUkTAH UAH
COLOhAOO HJVea bLLUk fAH«£h bAfl
CULOKAUO H. . IUHA
VliAhL'llAhbUN C.'lULI
ALA HAJ CAkAL
E. lOhK OMiafcK hlttN • UHlltL
GILA biVtfc AT LULKSUL 0»r
IKIllAIA HAMHUH
. IAUULU1 HAhbOH
CAbSU* h v NLW KH>JhL
LAKk TAhOt AT SAIIi MAhuOR
Llk* LAkfc
HORtkUHIlt H AT nCOUhHlLtK
IMDlAbA HAhL'UU
TUOLUHCL hl«ER AT TUULUHML C1TI
PATAbOfelA LAKE
ALAftO a hb CALII-AlhlA
SAM FkADLISClj h. AT LLIfTUI.
HUOSt»tll LARt iALT K. AJ.fi
HOCK SLOUGli AT UfcLlA hP MHJDoL
-All JOAlfUiH b Al AIT1UI.-H ktHf
EEL hl«tb AT RIO UbLL, OAHJb bThEEl
LAS »LO»S hA^H Al bOHTH bMtJHt HUAU
CALLVILLt LAT LAkL hFAU
LAb VrOb ..» LAKE BttU
LAKt VllLLoUhl ktAh ULUTT 1 bAH
SAfc JUAVUIH hlVLk Al '.TAI.lil.AUb tU.
LAKt HfckOOClba AT hh« ^0 ritJI>i.L
NUBIAN RIVth Al UllAh THLArntbl H
bUbSJAk klVLh - hl,klt Hlo
HAD hlVtli Af E-.S|.i (All
SAN1A CKU<. tULok libltn hOAI> >AST>. b
L, hlAtr v«,« tV»»;icn Hi,; nu:>6ln,4itl
L111LF. hlAk LH. Al hUlSEL Hj; bALlu
LITTLt KAr, Cht. hltth HI.; t.LTok T
LI11LL KkAil Lrt. Al I.HI.S. hL. HUbkH,
*A»H LH >.. AhC (.OKFIIIINlllkl «o «1 A
RbHtHlL AkIA HAZAhL^U: tfASlt ^ITt 1
IID1ANA hAlKUh
TKULftl t hl»th 11 t AtAU
tfAlt
bAkAJ]
HAkAU
AhJZOIA
IMIAUA
CALlrbhMlA
CtLirObkIA
lALIFOnllA
CALirOkblA
AklZONA
klVADA
CALirOHIIA
LALirtikklA
AMZUkA
LALirOkHIA
CALirtkiiA
AbltOkA
NEVADA
AHIZObA
AbJZOIA
NAkAlI
HikAIJ
ktHAUA
AhlZUIA
lUDlAkA
hAkAII
krVADA
ItVADA
AMZUNA
CALlPOabIA
IMDIAIA
CALIFOkMlA
Ahl/OkA
LALlfUdUlA
AHliOMA
A^Ji.tl»A
(.ALlrOklllA
CALIFOllklA
CA1 JfOhklA
II V ALA
III VAUA
CALIKUIfklA
t»l l»Oi.m«
LALIPOlilllA
LALJFUhNIA
CAI j KOI 111 A
(.ALllUi HA
Al liUKA
DILHlUAk
Ml HICAH
riLhICAN
r 11 hit. AN
(.rl Mbl*
ItkNt bStt
IklilANA
CALUOnllA 2
* ntAk
JjJj.UO
2m. oQ
ItTt.OC
IbiJ.GO
IHjO.OU
IVbO.OU ~
1 lib. 0(1
ibio.ua
UHb.UO
161. 1 .01'
1 hi! n .nil
1031.00 '
1SVM.OO
IbVO.UU
ISVU.UC
ISbl.UU
1461.00
UV9.dC
libu.oo"
liSO.OU
12bU^UO
1 1000.00
4 9tl.au
2 «m.oo
/ ao^.uo
766. 1C
1 - 7J3.IO
7CO.OO
fcsi.iir
bbl.OO
bJS. JO
bJb.SO
boO. 00
bou.ou
500.00
bCu.OO
buO.UO
iiFO.OO
bi.o.00
tuo.oo
bOO.uO
son. oo
bliU.OO
bl Q.bU
VUO.Ob
btU.jO
bOU.CO
•*tl°-U')
1UO.UI
J' tl.Ol
3JK.UC
-------
TABLE A-18. (Continued)
•
b7
•jO
i9
bO
bl
bj
b«
bb
bb
by
JO
7!
72
LL_
7b
7b
77
7d
24_
00
«l
62
Bl
b«
> - »S
CT> "*
•vj b7
aa
b9
90
VI
92
11
y«
*s
*b
97
«9
100
101
102
IP*
101
Ibl
lOb
It)/
lUu
10V
1 IU
III
112
bUliUH bAI b. Ul HlbULL (.MliUkb
•KM IOUK SLOUCH
S.». tlht-UHT JNuUSInlAL PLAbT
I r HAlUk STI- AT Htlll'HIb Tb 10 HISS
ThlllkeL klVih »T LGLHHUOO
PC«S*Ukt!L HtHbOh
POhT HiSPlMClOK
SilKT LOUIb HIVlH
Sllkl LOU 11. H|«FH
Si ll(l tOUJb HIItH
— et^ciLjajEhj^j..,,,^^ >ATtH ,.T
TUVtH LHEHIOL CO iH|!« HAZAHUUUS VI
. »I CAGlkt, bI»T40k
COOS* KlItN IT Lt/«L* bT Lint MEJIh
. -9U-.L1JU,TOJL._ST.P AT DlLtl^TOli TN TO
MILSOi hOAD tin Hut
BAST J8TB. iTBKLT »)RIUGL
BAlLHOAIi UN I DC L
. TVIBUTtbl TO CHATTAHUObA Chtlt. 2.2
THlbUTABI TO (.HAITAriOUbA CkfcKk O.J
POiD HfcAH TKMKSi.tE-CtOI.Cl* ST*n ,,
HOOltH HARILL bOAU CULVEJiT
. TWUUTAN1 TO CtumigOl,* ChttH I.Mi
bARJtl hOAD hriJUCt
BOUlOtS CHIEK btigN BULHgiLAlp HASH
II01AKA HAkbOH
•AbbAS C1TI MATLh TkKATHLIT PLT,
BIS&OUHI bltbl ULAb IDtfO UalOLt
BISSOUH1 fcMKII |T MUUI CITI
KCRN-HAV kATEk SllfPLI HO M
. PQ MATLH COHPAll UATkh SUCVLI
LARt RACKEkZlE. ribST lUHb fhon
OFF LAPHAk J.T »T ll't IUTKAIL TOI1C
rCD STATlOk LOK V UH LAKE UKEECHObt
BUtFALO SPklliGb LAHfc
SBtLLNOCK H. Ul'il OF NUHTbkUOb
rCt STATION 10 K 1 ON lAKfc (KEtLhUhl
ASblAoULA bAhblih. OHIO
ASbTAbULA Hihbuh. QrtlC
ASbTAHULA HAbHOk. OdlU
ISblAbULA bAhbub. Oll|0
AShTAbULA nAkHUb. OHIO
ASbTAbUlA HAhbOk. On 10
ASbTAbULA hAHHUh. tblL
«SHl«bUl* H.HbU.. Ul.ll.
AbHIAbULA hAbbJh. UHlu
BLACL HJ»U. BlLflJOAK
bLALt kj«t.a. ni«.HIL*K
CA^IHILlt hAhbUb.hlLHll.AN
CL»VtLAkU hANhOk
CtttfcLAkb BAkuUh
NARklS«I|L» HArtbUI
INUlAkA HinbOn
IHbUbA RAHbUh
bfAlt
CALIFORNIA
CALllUuklA
LAI IFObllA
TtkbtSbtt
btttDA
itl^LOkbll
kl^LOh^l*
klbLObSl*
HlbCOk^lK
HlSCObblb
LtLkCIA
»LOhIbA
LLOHGI A
btUkClA
ILkbEtStE
ItbbfcSbtE
TL^bLS^tE
IfekbEbSEE
ILkbKiSte
ItkbfcSSfcE
1»kbl!S^tfc
TFRbESStK
TeUkK^btK
TkBBESSCC
m*t:>sig
TlkbglilE
AklZQbA
IkUIAbA
r.jssouui
•EbbASKA
JCMA
KAb!>A!>
HlSSOUkl
TEXAS
• M.hOkT
riohioA
TtlAS
lOkA
ILOhlDA
fhlC
LblO
OHIO
Chic
CblO
CHID
CHJU
flklO
kIJLO»ii»
KlbCOlMN
RUHICAk
CHK;
LHIO
All.HII.AII
UI'lAKA
IkOIAbA
J30.000
JJU.UOO
JJU.UOU
joo.uoo
200.000
4UG.OOO
200.000
2UO.UOU
^00.000
J ^uu.non
2UO.OOO
200.000
200~.OOU
200.000
200.000
200.000
. 2QQ.OQO
200.000
.-..200.00V
200.000
1 200.000
200.000
200.000
200.000
190.800
IbO.OOO
ISO. 000
liO.OOO
IbO.OOO
ibo,qgu
1Mb. 000
uo.ooo
1^0. qOO
120.000
110.000
100.000
100.000
100.000
IbO.OOC
IUO.OOO
100.000
luQiPUl
uo.ooo
100. bOb
100. Ufal)
ivo.uuv
luO.OOO
100.000
100.000
100.000
IUO.OOO
-------
TABLE A-1S. (Continued)
ObS
11)
111
IIS
lib
ill
lib
119
120
Ul
122
Hi
144
12).
I2b
127
126
IV4
130
1)1
132
1J3
IJ4
us
IJb
137
IJb
in
140
IB)
> ""
1 143
CT. 144
00 ,,5
146
14}
14B
.14V.
Ibl)
1)1
Ib2
I*1
154
lii
Ibb
I*'..
1i8
ISM
160
Ibl
162
ItJ
164
i^s
Ibb
167
160
LOl
Jkp)ANA HANuOft
IkDIAkA HAkUCk
IkpJABA NAHhOH
llblABA HAkHUk
IkUlAkA hAhbUk
IkOlAkA BAKHOB
. -IkPim WA.HBUH
HOkOeuUOIT bAI
- KlOfeWLUUOIl b«I
1Kb CHtkttUl ISLtkOS CHt««ILS
US_tBAIlKtUl lbL*«LS L«*.miS
LITTLE SALMON kMLk
— BQIIIOI: ntkbok . .
BOlkOt HkhBOk
- -JWLllSBUhli
POJkT LOOtUUT HtkbUH
SA1HT LOUIS BKKh
SilIT LOUIS klVtll
- .-SHUT LOUIS fifth
CLlVlLtlll lUNbOh
- ClCVCLmp Mtfe00N
TOkER CHEBICIL CO *kE* H1AAHDOU!, hi
• EHPN1S fHU AT UULLIkuOU MD 1UKA •>
OULUTH HikbUk
fiVLUia bikbOM
OULUTH btkhUk
- fiOLUTH DlflbUk
DULUTk HtHbOH
DULUTH HAkMOk
OULUTH HAkUOK
DULUIU HAIIbUk
AT BtCM b«l VIJVL bklDCK
cimituD nttbOk .
CLLIELtkD UAkbOb
CLMfLlkD nltuuh
CLtlkLIkO HAkbOk
. -C1EVBUWO H«|ibUk
CLIIt.L*«D HlUbUb
. CUtELMP b4imOh
CLtttLlkD htkaUk
CLLIfLlkU UAhbUh
JlllLO HUbbES PhOftkll AT bl LHOkT kl
L«K» KLBHtT. kUhTH tkU i |U pi,
GBAkD fOulACIr.nikkt.bOTt
bk»|io.|>b«itcL.njkfc^*>(jiA
UktkO VOkTAbL.nikktbUTi
_6JiikU PokTic.t.in.kt.,caA
40UO FT HtLUk tAbT CktLR kUTLABO TO
..TUCiZ LUlj;. .
COkbOk StkVlCkb (.0 AT CUHOOk I, A 1O
B*5»» 1
CADPU!. UkJVk BklU(.»
UPSTkLAH O» lUH-tliS COktLUI^C):
100 »EET SOUTH or OAH
J HI bgLOk k. btkklkbTOk A1 i.OpOK «
1UOO IT. ttLOy k. VOkkAL DAH Ak 1Ak
bTATK
JkOlAkA
IkUIAkA
JIV1III4
IkDJAkA
JkUlANA
IkUIADA
IkOlAHA
ktk lOkl
kLV IOkK
HICHIbAk
BlLMIUAk
Ilk IOBI
Bit Hll Ik
HICBICAk
»ik IOBI.
BltHlbAk
klSLOkSlk
kl&CUkSlk
KlitOHilH
OHIO
11)10
FLOklbA
TtklEhSFK
B1BBESOTA
kiSlOISlk
MISCOkSIk
kl&COBSlk
kISCOkSlk
klSLOkSIH
kISCOb&IB
B1SCOBS1I.
CALirOkklA
CB1U
IMJO
LUICI
CBIO
ColO. .
DbJO
vbio
IHIO
LtflLl
fcOkTH CAhULlHA
LCUISlAkA
HlkkKbUTA
f^BtbQT*
hlkNKSOTA
nikkesoTA
ITIIkBOBT
- Bt«AUA__
CCOkCIA
ULlkOJS
CALirOhklA
CALlPOhHIA
lALIFUkklA
ItRPOBT
•tkBUkT
loo.gou
100.000
100. 000
100.000
100.000
100.000
100.000
100.000
100.000
100.000
1UO.VOO
100.000
too .uoo
100.000
100.000
IUO.OOD
100.000
IUO.OOO
100.000
100.000
100.000 .
100.000
IUO.OOO
100.000
100.000
100.000.
10.000
-JO. 000 .
70.000
70.000
70.000.
70.000
70.000
70.000
60.000
. iC.QOU
bO.UOO
*v.ooo
bO.COO
50.000
. bu.fiOi).
SO. 000
46.000
It. 667
40.000
40.000
40.000
-------
TABLE A-18. (Continued)
en
vo
IbU
1 10
111
1/2
m
l«
176
171
17H
179
161
182
Ib3
IbM
IBS
167
Ibb
lav
1VU
it»j
I'm
i«
1*6
197
1*4
2UO
201
202
203
20S
20t>
207
206
204
211
212
2IJ
211
2l!>
t\ 1
21e
2IS
22U
221
2000 IT. AI.UVI! ». HjykAL UAH Tollt
NOkTH o» LA2i LAUI ibLAko ft inn t
BKBlkD HkLAKtATIIi 20Gb PT ! OUTH |j|
kATlb OlSThlCT IkTAlt bETMLbN tflkt,
fOKth L1NL CHUbSIkG l.b HI ABUVt M
1000 FT bhlUW HT 2 BNlUCt IN S.T JOH ~
OLD KT 11 bHt. AbOVt CUULOb RILL i l>
L1TTLL AhkANbAb h AT kinb ST
TBlklTI h IT btLT LlkL NU
HtlH-HIS TikN »T BOLLINCOU hi) AKLA S
ntm-Hli TLNN IT HOlLfkuOU kD *ht* i
biiurreii cotrictL -- u«n«tu ILUH f
M f*Ln BCM C 2uU »T
INflkt. AVEkOt'BklCCt
HOLLAND BAkHbH. H1LBK.AN
HOLLANU HAhbOH. fllCNlbAk
HOLLAND htkbUk. KICBICAk
HOLLAND BANBOb. HlLHIbA*
bOLLAID BAHbOk, DlCNll.tk
bOLLAND BAkBUB. HJCblLAb
HOLLAND UAImUH, BICBlbAN
BOLLAND BAbbOk. HlLblUAB
HOLLAND BAHUuk. nlCblbAN
BOLLAND BAkbOB, flllblCAN
HOLLAND BAKbOB, BICBII.AN
BOLLAND BAkbuk. HJLB1GAI
DKS BOlktS k IT KULL1U A»t bk
Buckere CANAL • LiTCbriKLD
— k.l*. LK-N. CtiTHAL HAblN: l,tC 2B Ol
EDIT LK-tOkTBMKST BASIk; S»C ^1 , 01
kLLIN LK-5. LEkTkAL BA^IN; Stl 3t.
CHILI LAKL-CKkTkAL bAMN; bEC 24 01
ribl LK-S. C»NThAL bAblN; iEC 20 0»
•NDIAN IAk»-CtN1kAL hASIN; STAflUAUG
LONt LI Ik CtNT. bAbiklCHlLTAL FALL
B001 LI-N. CKTkAL DAMN; Mf ^9 O>
CULBANt LK-NOBllihAbT bASIN; ML jO
JKHkiE* LAkC IN tflST BASIN; BAbTIkl
LOkC LAKL-LtkTkAL I-A^IN; MC 1<« 01
L. kBlTUlbH LK-LkkT. bAl>lk; HKfciO
LK tlfTttk-CtkTkAL BAj.lt; i(.C IS G»
rui LANF Ik CENThAL b*bl»; UALTON T
bkAl»Ukb Lk-fc.ClklkAL HAS1I.; OTStOO
CUTHklL LIl-N. LtNlBAL bASIk; liTSLCO
BETTIt LAIl-S. EA^l LAS1N; Shi. 3^ 0
BIGGINS LAlb Ik NOklHkfSr l-k&lk; LI
MJ.htH!> L*llL-N. CLkThAL hAMkj P»ll
DOUl.t LARL Ik Vtbl nAblN; lilAniTIIA
HOQ1 LK-b.lhNTVAL b»S^. SIC Jti Uf
ISLANb LAIIC-S.beSl bA!>IN; hlAkATHA
kOUku LAKE IN b.tA^T tASJN; ktlLtk
bOSh LAK» Ik LLNlhAL LAblk. llAN^LN
bCf.n LAKI-S. IL..1H 1 ,,AS|NS »fcHkl.T
SHIHd l».-k.LLNIkAL OASlfc; LAkktfcLL
bl»Tt
VtkAONT
KEkBOkT
ViknONT
ItHMONT
viknuNT
«»kHONT
VlhHONT
KANSAS
1EIAS
TH>KKbbtt
Tlkktaskl!
LhtkUN ~ "
tLufclDA
LALlPUNklA
nlCHICtit
PICBICAN
niLHICAk
BKBICAN
BILB1CAN
niCBiCAk
MtHlGAN
flll.BIl.Ak
HUB1CAN
BICBlbAN
MICBIGlN
HICBICAB
lUkA
AHIZOBA
CkAbfOkU CO., HI
tltllkbOk CO. HI
1HUN CO.. HI
DICB1CAN
BJtBlCAB
ihCN co.. ai
RltBlCAN
lllCblCAN
HUB1CAN
KhCOSTA CO.. fll
DLkOHlNtf CO. AI
ruBTCALn co.. ni
BusietOk co., in
CTSltO CO.. nl
CTbECO CO.. HI
mibuut is cu hi
BlLBlCAk
El. JObtPH CO HI
I1UBILA»
scMcgiCMft to.
bCHOCLChlfT tu.
VAk blikl i. co. n)
(AN bUI-EN tU. nl
•Ak bUMIN tU. nl
• AN BOill'N CO. JTi
B KKAk
<4U.OOUO
10.000U
xu.uouu
10.0000
UO.OOOO
10.0000
UO.OOOO
111. 0000
UO.OOOO
Ji.OOUO
32.SOOO
3l.«2bt,
30.0000
30.0000
JO. 0000
30.UOOO
JO. 0000
30.0000
30.0000
30.0000
30.0000
JO. 0000
30.0000
29.0000
2b.OOOO
25.0000
2 b. 0000
2&.0000
2!>.0000
2S.OOOO
2S.OOOO
2S.UOOO
2S.UOOO
2b.OOOO
2S.OOOO
2S.OOOO
2S.OOOU
2S.COOO
2S.OOOO
iS.OOOt
2b.tOOC
^•j.OOOO
2S.OOOO
^b.L'OOO
2S.OOOO
-------
TABLE A-19. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF LINDANE
CONCENTRATIONS ARE IN Mg/kg
1
i
t
lo
II
\t
u.
u
li
U
n
Id
.!»
20
21
22
2J
2H
JS
ib
21
I*
11
M
> Jl
1 Ji
s a
JS
36
J7
J8
J»
HO
11
«^
<|J
11
n't
Hit
«/
II tt
«••*
bU
bl
b2
b.1
tt
bb
•jh
T*UlTr k AT hi LI LIkt PU
BLACK HlVtK. BlLHH,kt.
bLK* illVtM. nlCHH.iH
C1S».«ILLC hinbU«.flH.Ml(>tII
Hthh)!>VliL» Htbbuh
INOkD£UUOI1 DAI
IMUkUfcbUUiT felt
LKS CUAIitAUl lil.»*US CriANNlLb
L£b LUAkMUI ISHkU.S LrttNHtLb
LITTLE iALnOd HI Hill
flPMiOb MAbhUh
HUkhUt HAkbUtt
. OLOIfcbhUhl.
" VLkbAUM'E MAhfaUh
VU1KT LUOIUU1 HAhljOh . .
PUhl UA^HINCTUII
DULUTH HAhbOh
DULUTH HAfcbOb
DULUTH HlfchOH
DULUTH nAfcbON
DULU1H UAitbOM
DULUTH HAhtoOK
DULUTH MAhbUM
GHAUT PAkl HISCOMblll
bhAl«thl> STf AT ChATlA»OOGA Tk Tt -
•tILACAUC.1 I1«C mj«ti STP AT bILACA
ASHTkbULA ttAttbbH. UU1U
ASHTAbULA hAhbUh. UHIU
ASHIAbULA HAHbOtl. t>HiO
ASHTABULA HAhbOb. OHIO
ASblAbULA HAkllUH. UHIU
ASHTAbULA MAHbUb, OHIO
AbhlluULA HAKbUH. UbIU
ISHTAbULA HAkBLH. OHIO
AShlAbUlA HAHhUk. CJJIIL
CLIIfeLAVb HAHHUh
CLKHKLAIID MAhBUi
HOLLA 111 HAHBOB. nlCHILAk
HOLLAIU HAHbbD, hlCHICAN
HOILAHU hiJifcOh, AJCH1CAH
HOILANLl HAhbllH. hlLHll.Ah
HUlLAkI) HAKbUb. fllCHITAk
HOLLAHU HAHbJH. MCHIbAH
HULLAHO HANbuH. HICH1I.AH
HOLLAKU HAknCH, HlCHIi.A«
HUILAHU HAIoUM, Hl(.nll.A«
HOLLAND HlkhOh. hlCIHl-iK
HOLLAND HtKbUK, MLHIOAI
nOLLAHD MJHibUli, M^Ulvtt
HDlAkA HAkbUh
IklilAIA HAhbuH
111 DIANA h»kh(rh
IKL-lAHk KtnDCh
IfcblAHA bAhhUH
IHlilAIIA Htlinl/h
IMblAKA HAIBUh
llIAb
klbCOkbll
MlbCOH j|H
rlCHIbAH
fllLHlCAA
ktk rOh«
KM lUfcK
riLHICAk
MLHJCAH.
ktk tOk*
rKhlLA*
HICHIOAk
»»H lun*
hlbCOkSlN
HILHJCAb
klSCOkSIn
MANfcbtlTA
biblOkSl*
klbLUkblM
klStGHSII
kJ^CQU^IH
HiCOkSI*
VlbCUkMM
HlkkLSOTA
TKklLbSEt
AlAbABI
CH10
CHID
4.H1D
fit 10
LrilO
rhio
(JtilO
CHIC
(HJC
UliO
CHlu
HJCBl^Ak
rlCHlCAN
rjlHK.AA'
klCHIGAk
MLHILAM
KICKlbAk
nilHlUAk
f ILHIGAk
M(-blt.>«
fKHlbAk
f 11 HlbAk
rinuiiAo
IbDIANA
INI<1 AHA
IklilAIA
:M>IA*A
1M>1ANA
INDIANA
UblAHA
ll< V
boo
suo
bUO
\00
'jJU
b(J(J
bOU
SuO
bOO
'ibO
M<0
•nit
MiO
bOU
bUU
bOO
bUO
bUU
SOO
bUO
bOO
bOO
2UO
tto
11u
ICO
luo
too
luo
IOU
100
_ 100
100
Ub
1110
luo
too
100
IOU
11)0
luo
lUO
1 ItlO
1 11.0
j luO
1 1JO
lUO
ino
luo
Ub
luO
1 '0
1.10
irO
tub
-------
TABLE A-19. (Continued)
UbS
LOC
b«
60
61
62
CJ
61
bb
66
b7
ttt
69
70
72
7J
7U
7i
76
77
78
7.1
80
82
BJ
81
bb
66
87
88
90
91
92
~9«
96
9J
98
99
100
101
102
101
1014
In!)
106
lOb
109
110
111
112
INDIANA HAnnUh
1NLIANA HAhnOH
1NLIAMA HAftbUH
INDIANA bAbbOH
INDIANA HAhHUK
INDIANA HAhHUB
SAlkT LOUIS MlDth
bAlkT LUUli BIKE*
SAlkT LLOIS MlVi.H
SAUT LOU 11, Ml If tii
SAlfcl. tOUli, HlVrJ.
VALLEI Ck bTP AT LtbStHEH AL Tu «AL
CLLVLLANU HAkbUN
CLMtLANO HAHbOk
CLLMbOl STP AT CLI flbOk SC :O I«KI h
flAPLt IfcfctH STP AT GHlth bC TO HAIL
OBT caEIK STP AT NASMMLLt Tk lu bH
UNITES Ch STP AT MAbHVILLE IN TU CO
•ASbVlLLE CENTkAL bTP AT HASHKlLLt
.MITE NpCfc LAIt ktAlt UAH
NAIAhBO RILLS htbLH« NtAI LAM
AT HACK bAI liKlVt bhlOLE
PILh IN COUPER k*fc AT tNU or bICh n
CHArtvikL HESCHV »CAH PAH
CAHPOS DHIVE bhlUtE
UPSTNEAH Or r06-PLb CONrLOtNCt
100 »EET bOUTH CF DAh
BAhDUELL hlbUHl KtAB UAH
AT OLP UUHCH hAMf
AT JABbOHtl.NOHTM Of MAIN
CLEVELAND HAhPOM
CLtVfLAkD MAHbOh
_£1UU:U» dArihOH
CLLVLLANO HAkHOH
CieVtlAkL HAkriUb
LLLVrlLANU HAknUb
Ck>*ELANO HAabUh
CLLViLANO HAHbUh
CLLILLAND HAtibOk
CLLVtLAki) HAHBUk
CLEVKLAfcU bAhhOh
AT ILOATIkb POCK
tASl U» LAUHLH h»rf - MDLIiAkkLL
100 lAHbb bllOTH Ut LLII PJKh
riKSl bASlk. HIOLHAKkia. nllbASIM
AT COLUtk >Lbl LThLi.1 UhlULL
tNTfcANCI LI HOL:.A (.MICA L'HAMUL
CHhlbTiANA bAf. nluhA^IM
SUkLfT HI AT kAKI nOCIS
1"° '*»'•'-- »"»-TH u» UAnkLh AKtkUL
HlliLHtkkLI NLNTb U» IIAI IbLr
DIDtllANNtL. tAbl u» ^hTH 1>1 HUT
NlbbASlk t Ot kHrOol lihllKt
INUIAkA
IHblAkA
JkUlAkA
IkOIAkA
IkblANA
INUIANA
klSLONSlN
NlSCUIblk
HI SCON blN
klSCOkSIN
klbLUNSIk
HISIUNSIN
ALABAMA
IHiO
UhlO
SCOld CAaOLIkA
SLUTH CAHOLlkA
TtNNEbStt
TEMIIESSEE
1MAS
TEIAb
CALirOHklA
SOOTH CANOLINA
TKlAb
tALirOMNIA
LALlrOMNIA
CALirOfcNIA
TALltUKklA
TlIAb
CALUOkklA
OHJO
LblU
CHIU
UH1O
rhio
IH1C
ocig
CblO
CHIO
CH10
CN10
thlO
CALliObllA
CALIIUiiNIA
tALlFOhk.A
(.ALIFbkNIA
CALlfUiiklA
LALirObNlA
CALUQKN1A
CALIFUhNIA
(nLltOhklA
CALIIUhNIA
( ALltObNIA
CALirUNkIA
1
2
1
1
1
1
2
1
2
2
1
2
1
1
.2
1
1
1
1
1
1
b
1
1
B
9
a
II
1
2
1
1
1
1
1
1
1
1
1
2
1
1
4
2
It
b
2
1
fc
7
t
ni m
luc.ooo
100.000
100.000
100.000
1OO. 000
100.000
100.000
100.000
100.000
100.000
IOC. 000
100.000
100.000
100.000
100. OOC
100.000
100.000
100,000
100.000
66.470
iio.ooo
26.667
2b.OOO
2S.COO
20.000
20.000
20.000
40.000
20.000
20.000
20.000
20.000
20.000
2b.OOO
20.000
20.000
20. you
20.000
vO .000
20. COG
211. 000
*U •OilO
•JO • 000
20.000
2C.OOO
2o.ooo
20.000
-------
TABLE A-19. (Continued)
r— *" •*
in
UU
lib
117
lid
11V
121)
121
122
lil
Ul
126
130
131
IJM
1 ib
1 ib
137
».u».
lug IT », uf bOtdiOH CNttft JHLIT
100 ILET IUHTH U ILLtbL
N. LAkL LI) LtS ION e( tt|l^ MT|I
AT IbOO VALLkl UhKVAl HMJDLI
U/i. LAM AT bHlLi.*
PA11MC CUAbT Hll.Hi.AI
Btl OblbKJ ilhtfi tKUOL
100 >Ub MtiT Ul bib CAbluk «A-,H
lOb lAhUb fc o» NUkTH STAh hEACh
-iMUt_Ql..iijL£iitl. Lhk urkmti!
AT CkiUAH bThltl MHUCK
ikti/s iip AT ntfcb AI 10 Linn CAU
CLtAa cvetK-Abuve riUAL t m 2^1
BMUin Cii ilf AT JunN^Uk, CHI Tk VO
AT ^ULSA A¥tkUI! UTtkSIOM tMUbL
ill&u CHUB AT (t»i.i mim-it
U/l fALlflL LOAST UlLHUAI
KlirtB A • NKULb - Ukl 3Uk
SHAUK HlvrN AT hblbCb IDtrlu
COUth PALtkl! kl»»h A) kOf.t JAKt
PAItTTE fclktik AT IAIflTL-n.l SI,
KOOTIikAl HI VCR Al LOftlAlU JDAHU
-SP04A«£ KlVCk talk POST FALl* LAB
Sr lOUCh DALtlll! k AT KkAflLLl. I
11 ATI
ULirOhNU
(ALUUaklA
i4LI(U«Hll
CALltONblA
KLlllihlllA
l&LlfUbkli
CALirohdlA
CliJrONNlA
CALlfUfeklA
lALIKOHkIA
lALltUKklA
JlAfUHA
ItkltJSCL
lALirObNJA
ClLirUklllA
CALI»ObMIA
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1UAHU
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2 ^il.OOOO
3 20.00UO
1 20. 00(10
2 ^U.OOOO
•^"lUUOU
2 ^0.0000
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t> lO.OOUb
1 iU.UOOU
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l> 20.UOUL _^^
20.0000
20.0000
20.0001;
17.iOOO
i. I6.tihfc1
16.0000
10,0000
10.0000
10.0000
10.0000
10.0000
10.0000
10.0000
>
ro
-------
TABLE A-20.
SEDIMENT LEVELS OF TOXAPHENE
LO
— ^ MAI,
2
3
b
10
14
)j
11
Ib
1 7
40
41
42
4b
4b
28
2JL_
32
33
JU
3b
37
3b
39
10
12
MJ
11
b|
b4
bi
bb
HkW, UVtk ktt.)| LI. lilt .1C n> In
SALbbA f.Vk Al SI JH hit *C HJ. LK l.H
T t DAiok :if AI ntni-liib TI> TO «,Kb
kAkbAS C.1TI «Altn fhhAffltNl I-LT.
!LL5iO.Onl »|»r.h tllll ,,,,,, hk|uljE
nilMJUhl hlVtH AT ilOUl LIU
KCHk-HAh nATLk bOJ-PLI no H
HO kATIE* COHI-Akl kATtH SOPI-Lf
LITTII AkNAkSAS k AT kilts 'T
CASKS LktLk kLAk HL»!.bl«C. lhI.(OJb
9-feBJJijJLa— tJJI'A HAitAhntllls kAblt SJT( |
«uo B;,tou'ii( i""< " "» o> "" "
ItlLLlkGIOk jTp 1T nLLmtL» Ik TO
SHtLLkom k. UH-T b» kukTMkuoij
P"4> OkkL AT CUkT ncdHL i.b NH hui
1.1 LA kltKk AT bllLEbflE UAr
TBllilTI k AT bill lint HO
OGIHAK Cktt» IT n-7b lik; MLST bHAMC
.gckDAu cktm AT s niiiti n\. bk IN fc
ObkllAH it u»r bBOOkSIOt CUD; H. but
ALAnu LARt
lObA Hlttk kEAH IIAkrbVlLtE
BAHOLOJ HAHU08
LAk» PkuVlUKllCt. btPlk Lkb
AHtklLAk K. AT ^LHAkl^ bT.
BOMALO th AT AltkklCAk klflH
c«h»0k h t »L« inn HI
i>ALIkAb kl«Ek AT (.OkZALEb
DOULOtk Cklfk AT IIOUTH
CAkbOM k. • Hl»th»ll<
OMLkS M M T|)»f)*>-r *-i
j«-i« ••« HI ILK htlUk PkADC bAM
BOOLOLk Chl.it AUOVI MILbLk Chit 11
AHItlCAk k. AbOVL bUkhlSe hk
AHtklCAk k. AT liAllb AH.
COUIH CfcH. Ah nuULOlk CBttfc
LAfL TAfu> .1 »,,,!, HAhBllM
LAMOkTAk OAR
COLOkAUC fclVt,, ,,tLC- l-Al^ei, LAn
IMTLt FLl DtE k«» dL JtT kITh IIAI-L
COLloii.i/0 k. a niDA
UbS KUIktb k AT -be LIU AVI HK
Siti'i.'*!!!"'' *t*h i'"''ir. Ahi .
BilC'U bAkTMUlOntk III Ah flCblNtl. AHk
fCAfci. bAhblla b. LULL
ALA .Al CANAL
t. lUaR i.uikiK hjktu » uutiitL
CUUIHIk tkffk Ai ILUtth -,T •
hALI.AI bHI LK hi. HJ ..-.I t Of i,, ,.„
TUkfcll (k Af LA-I/U LkUbSlM.
MU1H CAkOLikA
tOUTH CAhOLlkA
ILkklibSIt
KlbbtlUal
OthkAbKA
ILKA '
KAkSAb
MbbOUkl
NAkbAS
ItAAb
bLOTB CAHULlkA
HAkAll
TEkkESSFE
HAWAII
111 HlUA
AHllOkA '
1MAS
"JIHIGAA " ~
PICHIGAk
HH.UK.A*
RICHfCAk
IhlZCkA
HIV ADA
CALirOHkiA
lOblSIAkA
CAL IFUH>I «
LALirOkllA
CALJ»UkklA
klVAUA
LALltUHNlA
CALlFC.klA • '
AhlZukA
CALIFChlllA
CALjrOnklA
AkIZUkA
Nl VAOA
fc* VAbA
SOUTH CAIIULIHA
ArtlZo»A
1IIUA
AllKAN.SAj
UiHil
kl ».UA
KAk'.Ab
hAhSAS
nA»,:>Aj '
-llll'n LonULJka
lUOlbliNA
Ibl4ti.0
10000. L
bbUO.C
bbOO.O
bbOO.t.
bbOO.O
. bdOO.b
bJ'00.0
3333. li
JOOO.O
27l)!(j
2700.0
2000.0
2000.0
2000.0
2000.0
L 2000.0
1971.0
1HS7.0
IH30.0
laoi.o
Iboj.o
1 I7bil.ll
1726.0 '
USb.O
lofcl.O
1C31.U
1S10.C
Ib^O.O
Ibbl.U
1«bJ.li
|Vli| .0
IMOO.O
Ijvs.n
1300.0
12Su!l
KbO.L
L^bO.P
i.Cu.o
II ••O.I
idnii.i,
-------
TABLE A-20. (Continued)
i /
bb
hi
bj
bb
JLL
(>*
70
71
li
In
74
76
.77
7tt
7«
"I
82
BJ
an
bb
BB"
0»
SJ_
'*
9b
»6
100
IU1
104
IOJ
lui
lOb
lu/
IOB
111
112
tLlih ChlliL-At-ult 1IUAL d »tl ; FAUTTE T«
bT Joitl'H 1 U.kbTh 01 CHICAGO ST Ik
ST JOJtHI if 4 kklP MhV tu hH;«Jtti|)
UkkAntO Tklba HJLLbbALr Mb DHJFAIIT
iT JOE k Ant JOKISVIUK yd It-; FA«M
Btjk CKHK A-J Wi-U7 fch; M1TS»0«I.
BfcAM Chim AT NLLbUk liOAU; HUI;SOk T
HLICK Ch AT LIUkb H. 1 ; 'FAUFI tLO\k
»«U CH»,A aT UMil B.I- IAII.HILP
BLACK CMEER AT flOhbE till; tAlhFIiLI)
- lAlSIl (HVtH AT AJU hOAtt; HAlMk T
bLAlK L'b AT bANk LLCEK BUI J(, C1TI
. »IAC|( CH AT Jl-it HfclDCt; FAlkFlbLO
BtAII CkKtK AT lltChANIC ST l.k. Ik HO
BtAfc LliHik Al IIL-12/ hi): .ILLSUM lul-
BBSTOII UhAlk AT MOUTH; lAIklltLU Ty
1 bh b(.At* i| yfbThii IOUTU A«L; ZIEL
• hh bLACK H AT lObTB *«c |,b; HOLLA
k tIK bLACK H «T D-41 bn; UbLLAkp Tk
BAlSlk H. AT AUbTlK kb.; BAKCHtSTLh
g tilSlB >1 JHUhrik. HIIPK hD: !:|,Ant
U*I>ii H AT UU*LAk ST bhIOCt Ik HAH
HAISlk kfl bB orr IOiJ1|( B0. BhlutEk
NObbtVLLT LAKE iALT k. Akn
BilOU BACOk J HJ t U» b A lit hi
TEkSAS hlttk AT TtkLAL. LODJblAkA
*»*>"" MUkkt ltik.t AT m.lhl«is LCI
UN. nOUTII OF OEkl. Cfl.. AbOtIT 10
HOklLUIIIIt b AT fci-GUbHlUCK
TUOLUHBb HltLk AT TbOkUANK CITI
fAIALOMlA LAkH
llftlA FL Af SIIikL¥ Mi.,. IIAZAHMIU-. j
• HBO H Nk CALIJ-A'ihlA
SAk Hi A liC 1. SCO k. Al LLIFTOk
HAV UATth JUlAAt .1 bA»tkPl,kT
. OCfltLttt kllTLII kLAk KAIOB kATt.i i.T
SAID) Ch kk ABC CUMUbflDtkl CC Al A
CUOiA HJIIh AT i,*/ALA !. T Likt k»Ak
ACAtt.ni bkUH U.L Al ri,AHL01Tt kC
kh HCiUlb HI LlihL^L BA10U. II Of
BAJCU HALOk J HI t LI ChO.VlLLL
kUtA bLUUl.it AT OitTA hit bKJUof
bAk JOA'.Ui. k AT .klltCH hAflr
— Ml- Ki*fh A j hlii bm . H»|3 sr«n7
LAb fl^Ab »ALH Al kihTil bMl.hl- KOAU
CAllHllLt 1 At I AM. niAf
LAS >toAl. liAT LAHI n»Au
briAlt
1 ." t Ab
MCblGAk
nit Hit,* a
MiCHlOAk
M( HJ1.1K
KltHILAk
HKH1GIN
ri«,Hll>Ak
HICHlbAk
KlCHlbAk '
DKHICill
DKHIOIk
KICHJGAk
HlLHlGAk
MKHIbAk
IfkAWLL LQ.. ni
MILHIbAN
rjC.HIl.AI
UK HlLAk
niLHir.AN
HKHlCAk
HUHK.AM
niLHlbAk
HlCBlbAI
kALHlKkAM CU. Ml
AHlZOkA
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KJIllMAkA
CALltOHfclA
CAHfOhkiA
AkJZUkA
A k J ZOk A
Ciiiffl.! A
NOhlb CAHOL1NA
ICimiAHi
LOL'lblAhA
CALItOhNI*
NtVADA
kLtAOA
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(')OO.(IO
luto.ou
1000. UO
111 li ii nr*
1000. 00
1000. 00
1000. VO
1000. DO
1000.00
100U.OO
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1UOO.OU
1 1000.00
1000.00 '
1000,00
1000.00
100Q.PO
luoo.oo
L 1000.00
1000.00
1000.00
1000.00
1000.00
1000.00
1000.00
1000.00
VbJ.JO
.010.00
8IU. MO
HUO.bO
7bb.10
7bO.OO
133.10
tbl.OO
LbO.OO
b3V.JO
6J6.>>0
600.00
bOO.UO
DOO.dO
btO.bu
too. uo
biJ.JO
bJU.Cb
bOO.Ct
SVO.uO
— bm.LO
bUti.OO
!>UU.UU
bl b.b(l
-------
TABLE A-20. (Continued)
113 LAKt FILLMlUkl ktAk SCUTT 1 I14H
Ha SAk JOAI>U1N hIVth AT SlANi: LAUS CO.
lib LAKL HtkDuClkO AT nil 20 bhll>i.t
1U HUSSIA* hlVKfc AT UklAH UKAIIItNT IL
"I HUS^IAk fcUKk - nukTh nlO
IIB MAI) filVth AT FSStl LAME
"» THUCUtE Blttl, AT tAkAU
120 TRULKLL KlVfch AT LOCftktOU
.'«.' - - **klA CkUi ittLOrf kLCUk kOAO kASTL U
122 OTbtH tfAltkS 111 llllibULK
!_2J SAkbl Cfc Nh AfcL LUHfUUkblNl. CO AT A
I2» LAbLL LARt HUH VlLRSbUHC US
!-2i CA_LA«A*Ab 1 Thlh Al HI fcUEk kOAU kk
126 TOktH ChkllJL-AL LI AkfcA HAZAHbOUS MA
'-^* - -T0«lh CMlhlCAL 10 AktA HAZANbOUS .A
128 ntnl-HJS AMtA HALAuUUUS MASle'slTt J
12" IIILIOM H AT S-2H-10J
1JO LAIK PHOIJDKNCe- UlLOK JCT LA -J S. U
Ml STAUtPth cheniCAi. -- ukiuip ALUH p
.?3J OOkk^THiAH ilOf DM I ^Hb bk
134 10HA BKLM AT HAfcSHAl L10MN hTP
• US LIT1LE 5IOU1 II Ulfi of SPEkCtH
JJ7 IIHlPHIb TtkN AT UO1I.IMOOD Hi khkA S
138 II EB PHIS Ttkk AT HbLLIMUOO kl) AhEA b ~
ljy HCMI-HIS TtkN AT IkAlSLH POkU ABKA b
mo Hem-ins TEIIN AT rhiii^LM POkii AHEA :
^ 1*2 NEAh HOUTH OP LAlIP BAIUU, 1 01 H
1 I1J _JTleAli tOkft Ot TnUITI H AT fOhT
JJ 1«« L1HO COULtt kA^TLMAT
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iHb CKAb ChktK LATtHAL MA.TKA1 k k.A B CO
. UH rht»LHIIAII lilLLS kASTLMAI HI- POTHOLL
l«» TKIklTI h ^o LOOP bHl^ b/DALLAS
IS!! - JIM.kSAb hinih AT SAHII spkim.!>
blATE
LALIPOI klA
tALlfOfcklA
CALlrOkNIA
CALIPOMklA
LAI JIOk«lA
KtDAUA
INIZOkA
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btONGI A
HISSISSIVPI
CALIIOHkIA
flOklOA
ILONIUA
SLUTh LANULIkA
LOUISIANA
LkLbOk
AkKANSAS
1UVA
IOMA
1L.A
IOMA
ItkNtSSte"
likktSStt
lOUISlAkl
IfckAb
kAMIJkCTuH J!
kASHlNbTOk 41,
in AS j-
0*LAHOIlA |
k nt Ak
—
SOU. 000
SOO. 000
b 0.0,. (JUG
too. ooo
SOO.OQU
SOO. 000
.SbO.OOO
sou. iioo
bOO. 000
bOO.OUO
IKIV.VOO
wOb.OOO
UOO.ubO
379.000
3bO.OOO
300.000
JOO.OOO
JOb .000
300.000
300.000
300.000'
300.000
300.000
2tiO.OOO
2bS.OOO
2 St. 000
SbO.OOO
i SC. 000
2SU.OQQ
-------
TABLE A-21.
3>
(7)
Obs Lot
1 OOkUOk S.m»lLlS 11. AT LOBDOK LA 10
2 HAIbLbHOHO TN bAZAkllOUJ MAilL SADPL
1 IBD1ABA BAkbOB
1 1IDIABA BABMOb
i IkUlAIA BAHBOk
6 1IU1ABA BAbBUB
/ TUbk CbttK AT CUUkJT NUAO ^J bklULt
« LAIL BAkTkELL 1* Bl C« AT SC Bbl ij
9 -SUPbOll k miSlllU bAI
10 SAMliI Ck Bk ABC CunpOUkDlBb «.O AT A
U HOJAkA MAK..III.
li ATUtkS iTP BO 2 Al AIHKBS LA TO f.ll)
14 SAfiiliAV H.lȣk._
11 SAC1BAH BIlEh"*
]» Hitesflj! .a _ rojuimi Mu
IJ— - *AB1TAH kJ»l!H l«!>TllfcA|| AT MfHUC L*
1« IBDIAkA HAkBOB
!»-.. J1J1E85 STJt.MQ J Al AT Jim si 10 bQh
20 IB01ABA BAkbOB ~
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t\ . ..nuu&Qg .1, C.AJLU i>gi.«T
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TABLE A-21. (Continued)
Obi
1,7
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bj
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64
66~
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09
"70 "
71
72
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75
76
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79
80
81
82
83
811
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91
92
91
94
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104
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TABLE A-21. (Continued)
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113
114
116
117
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119
120
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124
123
124
126
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132
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436.000
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320.000
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-------
•xi
to
TABLE A-21
UBS LOC
]b1 T*HI'» fl AT blpKtl nikt H»i»KtOUb V
17U II 111 l2HlJ.i CH AT CUUtTI HP l»b Hkl
171 |.1E1: TITO Illl* . _ AT MTLK*
112 SAlkT LOUIS H1«1!H
113 C LEV CLAM HAkbOh
17M fllDCHAMEL lOkTB Ot DAI 11. IE
US .. BiBltttlRtl.. eiil tif ma. ilhttl
iTo niDhasm r or ntki-obT uaiDGt
ill -.-VEBbAuitk HtkbiUL
I7B POKT NASHlfcGTOB
17* Ikllfle AVEkllt UI\lllCl
IBO CtafUS OHi«K bBIOCL
IU1 SAU1BAH Hill*
1B2 kABSAS C.ITI »AT»k TNtATftEkT KM.
_IBJ BlSSUUkl .blVtlt klAh 14BO fl Hil/ lit
IB4 IHSiOUm BIVK1 At SIOUX CIT1
IBS IC1N-HAV (fATKM SUI-PLI HO II
1b6 BO MATE* tOIH-AIII MATEH SUPPLI
.187 ttUURD STt AT iidlAIIL 1L 1O bOBitl
1H« UACt^OIVlLLt! SIP tl JtCISOkVlLLE AL
ua Bim.JQ.flrr uuhh ott RQAU; snoiisui
190 CO PB 30 it DATTtbOl LK «D; bhOkiUli
Itll Cfl DUB JO OW lUlUbTklAL Kb: HMOkSIJ
192 CO PB 30 BtLOH kHTP KbOOIS; fakOkSU
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194 At GAG I It STAtlOII
19S flUUfil ilk iOHCt ti4St.il lilBUiti Gfc
196 BKAI Cken AT US-127 BH; PlTTSIOhU
197 lOkthSIDE STP At DJVHAM |C to ILLtk
I9U TIRVOBO STl- At TAkSOkO 1C TO 1AB 11
.1S9. KiiMbBOkb L1V 11 fclDlSBGHO 1C IU bE
200 NAPlt CBttK STP AT GktCB be TO IIAPL
J01 BJAk LLUJl AT BU.SOB kOiD; UUUbOk T
20^ B. kAlSIB tl SimOM kU; HAlSlk Tkp,
3QJ Bf.Af.1 CH AT LIO»h HHI: IAlt.Flt.LD Tk
20 AHCA ^
210
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.219 etsi 3»Tb, >IHllT.thJWt
22U BAlLfcOAL BM1UC2
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222 TBlhBTAkl TU CBATTABOObA >.kkE( O.J
^J ppkp kgAH TtH»t.5>tt-(»»uK(,U ->T»H. L
2J(I ObCrAH CkLliK AT B-fb bk; "LiT bkiNC
. (Continued)
iTATB .
rMlBiPA
SbUTM (.AKOLlkA
..(IlkBtbOTf
mscoksik
IB10
CALirOkBlA
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BICBlGAk
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2111
207
200
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200
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200
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200
200
200
200
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200
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200
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200
200
200
200
200
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2UU
200
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200
200
-------
TABLE A-21. (Continued)
22b
]2fa
221
2*1
230
"2J2~
2JM
OCtHAU ChltH AT i VAlLtl hi/ Uh 111 k
OCIH*« CH 0»»' bfcOOKSlUI! CED; M. bhA
ObtKAV CR 1/2 HI UNSTH Ut r-V6j * b
• ~Bfc~feLACfc n'ofbThtl "lOHTB lit; Zlll
• bb bLACl H AT lObTH A»t bH; HULLA
• Bk BLACK 8 AT ft-21 bfc; ttOLLAVU TH
KAlbJN k. AT AUiTK Kb. J BAMLHtSTLb
I IAJS1I AT &HAkUM'v»Lie! hO; bttAHU
HAIMI It AT UUHLAN it BfclBOi: il DAI
•ICHJUAI
DICHlbAM
BILH1CAI
MthlClK
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VA!>HTI!litli CO..B1 ~
nicniGAi
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2UO
2UO
"200
200
200
200
"200
200
200
00
o
-------
TABLE A-22. FRESHWATER REGIONS CONTAINING ELEVATED SEDIMENT LEVELS OF CYANIDE.
CONCENTRATIONS ARE IN mg/kg.
00
1
2
J
U
»
b
1
d
? .
to
II
12
U_.
l«
!*_ .
16
17
10
J» -
20
.21 _
22
21
21
2i._
2b
2? .
26
29
10
Jl_
12
.«.._
34
3b
it
J1._
Jd
3»
no
41
42
.93
•a
.«*_
it 7
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49
SO
:>i
S2
!,J
sa
Si
bo
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COLlIb PhOCE!i!> kliTE SLUDi.1
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bOObtOUU A»E BHlbut ilS rt IS btjTbi
CUkTISS ST. HklDCl hfcHlkU iUnPHUUSK
JOHb littht SLUDGE
. fllOULfc ST BklllGL bU }T lib l-hlSTOL
L1ZI LkNL bHJDbt hliT BA»« ISO IT U
,«LB CKoiM iport UI-ST yuiti uibcim
•ECHKS R SH87 »O Of KUbT tklHUh
CtflUKtO ST bhlUtL .^ III OS SOUTH b«
r? IIOl)(.t DlCKSThD SLUDGC
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BMC«n»flkliT 81»Bfc k4TEfc »»Lltl
DBS nOlkES. STI> Ul(.k!>Tkli SLUOGt
CUfltlCIIE STf blCtSTKD StUUbfe
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PUT I«ITHUOO COkf OUtrtLL U02; LOU
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LOIG LAKe IK HESI BASIC; OktCAMS TV
_bABTU« U»e-«ESl t»5Hi; SCbOUt-CklkiT
LONG LAIL-LEITHAL UAblM; PAVlLIOk T
tJHCOl.il |.A»t-CkklhA|. bASI*. bftlLLD
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flUHhM kAAE Ik SV UAS1M: GhATTAH TV
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LAKL KACATAVA Ik HtbT UASIII; PAkK T
LOkC LARL ll CtHThAL hAbll; CULU* T
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UAIEBPOfil DU.ESILD SJ.UO(iL
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bASk Llkk LlAE-N.t. bA!.ll: HAHBUhG
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• ILLwHtMl H. AT KIN MIRSllil.TgA
fL»l H«ATHU00 CUbf OUlfALL U01; LOk
CUkltCTICUT
1UMA
CUNNbLTICUT
CUBHECTICUT
CCkklCTJCUT
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COBkECTICUT
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CUBBECT1CUT
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moni»c
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nicniuM
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Pili*SILI*PlA
H1LH1I.AI
saou.oo
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1HSO.OV
isuo.oo
770.00
770.00
TbO.OO
690.00
«22.UO
J77.J3
J2U.UO
100.00
'J.OO
S9.00
5H.UO
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Jb.V9
JO. 00
29.61
26.00
22.0.0.
20.00
17.69
15.00
litflfl.
IS. 00
l«tPO.
14.00
12.00
11.00
10.00
10.00
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10.00
10.00
10.00
10.00.
lu.uo
10.00
10.00
1U.OII
10.00
10, 00
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10.00
10.00
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10.00
9.10
B.OO
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7.60
7.bfc
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7.2U
-------
• TABLE A-22. (Continued)
I
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