o,/
c/EPA
United States
Environmental Protection
Agency
Great Lakes National Program Office
77 West Jackson Boulevard
Chicago, Illinois 60604
EPA 905-R96-008
September 1996
Assessment and
Remediation
of Contaminated Sediments
(ARCS) Program
CALCULATION AND EVALUATION OF
SEDIMENT EFFECT CONCENTRA-
TIONS FOR THE AMPHIPOD
HYALELLA AZTECA AND THE MIDGE
CHIRONOMUS RIPARIUS
(§) United States Areas of Concern
• ARCS Priority Areas of Concern
-------
EPA 905-R96-008
September 1996
CALCULATION AND EVALUATION OF SEDIMENT
EFFECT CONCENTRATIONS FOR THE AMPHIPOD
HYALELLA AZTECA AND THE MIDGE CHIRONOMUS RIPARIUS
National Biological Service Final Report for
the U.S. Environmental Protection Agency
Great Lakes National Program Office (GLNPO)
Assessment and Remediation of Contaminated
Sediment (ARCS) Project
Ingersoll, C.G., P.S. Haverland, E.L. Brunson, T.J. Canfield,
F.J. Dwyer, C.E. Henke, N.E. Kemble
Midwest Science Center
National Biological Service
4200 New Haven Road
Columbia, MO 65201
and
D.R. Mount
Mid-continent Ecology Division
U.S. Environmental Protection Agency
6201 Congdon Boulevard
Duluth,MN 55804
Project Officer: Richard G. Fox
Great Lakes National Program Office
U.S. Environmental Protection Agency
77 W. Jackson
Chicago, IL 60604
U.S. Environments' Protecttefl
Region S.Utwy iPi-ll';)
77 West Jacks™ Botttevatf, 12ft
Chicago, it C03CW-3&SO
-------
Disclaimer
Although the sediment effect concentrations (SECs) can be used as guidance for evaluating
contaminated sediment, there is no intent expressed or implied that these SECs represent USEPA
or National Biological Service (NBS) criteria. Mention of trade names or commercial products
does not constitute endorsement or recommendation for use. The information in this report has
been funded in part by the USEPA under Contract Number DW14933874 with the NBS Midwest
Science Center, Columbia, MO.
-------
Abstract
Procedures are described for calculating and evaluating sediment effect concentrations (SECs)
using laboratory data on the toxicity of contaminants associated with field-collected sediment to
the amphipod Hyalella azteca and the midge Chironomus riparius. SECs are defined as the
concentrations of individual contaminants in sediment below which toxicity is rarely observed
and above which toxicity is frequently observed. Only a limited number of SECs have been
published for freshwater sediments. The objective of the present study was to develop SECs to
classify toxicity data for Great Lake sediment samples tested with Hyalella azteca and
Chironomus riparius. This SEC database included samples from additional sites across the United
States in order to make the database as robust as possible. Three types of SECs were calculated
from these data: (1) Effect Range Low (ERL) and Effect Range Median (ERM), (2) Threshold
Effect Level (TEL) and Probable Effect Level (PEL), and (3) No Effect Concentration (NEC). The
SECs were calculated using: (1) dry-weight concentrations, (2) dry-weight concentrations
normalized to total organic carbon concentrations (for non-ionic organics), or (3) dry-weight
concentrations normalized to acid volatile sulfide concentrations (for divalent metals). We were
able to calculate SECs primarily for total metals, simultaneously extracted metals,
polychlorinated biphenyls (PCBs), and polycyclic aromatic hydrocarbons (PAHs). The ranges of
concentrations in sediment were too narrow in our database to adequately evaluate SECs for
butyltins, methyl mercury, polychlorinated dioxins and furans, or chlorinated pesticides.
About 60 to 80% of the sediment samples in the database are correctly classified as toxic or not
toxic depending on type of SEC evaluated. The SECs calculated for the entire database were
generally as reliable as SECs calculated for the Great Lakes database at classifying both toxic
and non-toxic Great Lakes samples in our database. ERMs and ERLs calculated using the entire
database are generally as reliable as paired PELs and TELs at classifying both toxic and non-toxic
samples in our database. Reliability of the SECs in terms of correctly classifying sediment samples
is similar between ERMs and NECs; however, ERMs minimize Type I error (false positives)
relative to ERLs and minimize Type II error (false negatives) relative to NECs. Correct
classification of samples can be improved by using only the most reliable individual SECs for
chemicals (i.e., those with a higher percentage of correct classification). When SECs are used to
conduct a preliminary screening to predict the potential for toxicity in the absence of actual
toxicity testing, a low number of SEC exceedances should be used to minimize the potential for
false negatives; however, the risk of accepting higher false positives is increased. Calculating
SECs using dry-weight concentrations vs SECs calculated using sediment concentrations
normalized to TOC concentrations for PAHs and total PCBs resulted in similar correct
classification of toxicity and similar Type I and Type II error. The range of TOC concentrations
in our database was relatively narrow compared to the ranges of contaminant concentrations.
Therefore, normalizing dry-weight concentrations to a relatively narrow range of TOC
concentrations had little influence on relative concentrations of contaminants among samples.
Our SECs were calculated from toxicity tests with field-collected samples. If a chemical
concentration exceeds an SEC generated using data from these tests with field-collected samples,
-------
it does not necessarily mean the chemical caused the observed effect. Rather, the SEC is the
concentration of a chemical that is associated with the effect. Field-collected sediments typically
contain complex mixtures of contaminants. Additional information is needed to identify the
specific contaminants that were actually responsible for the toxicity. Confirmation of sediment
toxicity due to individual or groups of contaminants can be determined by using Toxicity
Identification Evaluation (TIE) procedures or by conducting toxicity tests with spiked sediments.
Once the probable cause(s) of sediment toxicity has been identified, better decisions can be made
regarding remediation options.
IV
-------
Contents
Abstract iii
List of Tables v
List of Figures v
List of Appendices viii
List of Acronyms x
Acknowledgments xi
Introduction 1
Methods 4
Results and Discussion 10
Conclusions and Recommendations 22
References 24
Tables 29
Figures
Appendices
v
-------
List of Tables
Table 1 Percentage of whole-sediment samples identified as toxic in Chironomus riparius
14-d (CR14), Hyalella azteca 14-d (HAM), or H. azteca 28-d (HA28) tests.
Table 2 Percentage of paired tests or paired endpoints identifying samples as toxic in
Chironomus riparius 14-d (CR14), Hyalella azteca 14-d (HAH), or H. azteca 28-
d (HA28) tests.
List of Figures
Figure 1 Comparability and reliability of ERMs calculated using the Great Lakes database
(ERM-G) vs ERMs calculated using dry-weight concentrations and the entire
database (ERM).
Figure 2 Comparability and reliability of PELs calculated using the Great Lakes database
(PEL-G) vs PELs calculated using dry-weight concentrations and the entire
database (PEL).
Figure 3 Comparability and reliability of ERLs calculated using the Great Lakes database
(ERL-G) vs ERLs calculated using dry-weight concentrations and the entire
database (ERL).
Figure 4 Comparability and reliability of TELs calculated using the Great Lakes database
(TEL-G) vs TELs calculated using dry-weight concentrations and the entire
database (TEL).
Figure 5 Comparability and reliability of NECs calculated using the Great Lakes database
(NEC-G) vs NECs calculated using dry-weight concentrations and the entire
database (NEC).
Figure 6 Comparability and reliability of ERMs and PELs calculated using dry-weight
concentrations and the entire database.
Figure 7 Comparability and reliability of ERLs and TELs calculated using dry-weight
concentrations and the entire database.
Figure 8 Comparability and reliability of ERMs and ERLs calculated using dry-weight
concentrations and the entire database.
Figure 9 Comparability and reliability of PELs and TELs calculated using dry- weight
concentrations and the entire database.
vi
-------
igure 10 Comparability and reliability of NECs and ERMs calculated using dry-weight
concentrations and the entire database.
Figure 11 Comparability and reliability of NECs and ERLs calculated using dry-weight
concentrations and the entire database.
Figure 12 Reliability of ERMs calculated using dry-weight concentrations and using
sediment concentrations normalized to total organic carbon (TOC; ERM-T)
concentrations for the entire database.
Figure 13 Reliability of ERLs calculated using dry-weight concentrations and using
sediment concentrations normalized TOC (ERL-T) concentrations for the entire
database.
Figure 14 Reliability of NECs calculated using dry-weight concentrations and using
sediment concentrations normalized to TOC (NEC-T) concentrations for the
entire database.
Figure 15 Reliability of ERMs for metals calculated using dry-weight concentrations and
pore-water (ERM-PW) concentrations for the entire database.
Figure 16 Reliability of ERLs for metals calculated using dry-weight concentrations and
pore-water (ERL-PW) concentrations for the entire database.
Figure 17 Reliability of NECs for metals calculated using dry-weight concentrations and
pore-water (NEC-PW) concentrations for the entire database.
Figure 18 Reliability of ERMs calculated using total-metal (ERM-BT) concentrations and
simultaneously extracted metal (ERM-BS) concentrations for the entire database.
Figure 19 Reliability of ERLs calculated using total-metal (ERL-BT) concentrations and
simultaneously extracted metal (ERL-BS) concentrations for the entire database.
Figure 20 Reliability of NECs calculated using total-metal (NEC-BT) concentrations and
simultaneously extracted metal (NEC-BS) concentrations for the entire database.
Figure 21 Observed and expected toxicity of samples based on the minimum number of
ERM exceedances using dry-weight concentrations for the entire database.
Figure 22 Observed and expected toxicity of samples based on the minimum number of
ERL exceedances using dry-weight concentrations for the entire database.
VII
-------
Figure 23 Observed and expected toxicity of samples based on the minimum number of
NEC exceedances using dry-weight concentrations and using all individual NECs
regardless of the percent correct classification for the entire database.
Figure 24 Observed and expected toxicity of HA28 samples based on the minimum number
of NEC, ERM, and ERL exceedances for the entire database using dry-weight
concentrations regardless of percentage correct classification by these individual
ERMs.
Figure 25 Observed and expected toxicity of HA28 samples based on the minimum number
of ERM exceedances for the entire database using individual ERMs for PAHs or
PCBs calculated using dry-weight or using sediment concentrations normalized to
total organic carbon concentrations.
Figure 26 Observed and predicted toxicity of Clark Fork River samples based on the
minimum number of Great Lakes ERM exceedances using dry-weight
concentrations.
Figure 27 Comparability of our SECs for the entire database to published SECs for
benzo[a]pyrene (BaP) based on dry-weight concentrations.
Figure 28 Comparability of our SECs to published SECs for copper based on dry-weight
concentrations.
Figure 29 Observed and predicted toxicity of HA28 samples based on dry-weight
concentrations and the minimum number of exceedances of published freshwater
PELs, Hyalella azteca AETs, EQP, and SLCs.
Figure 30 Relationship between the frequency of ERM exceedances and the sum of the
ERM toxic quotient for toxic and non-toxic HA28 samples using dry-weight
concentrations.
List of Appendices
NOTE: The entire versions of Appendices 2a, 2b, 4a, 4b, and 5 are not printed in the
report. The computer disk that accompanies the report contains electronic
versions of these appendices. See the file named "read.me" for a further
description of these files.
Appendix 1 Summary of biological, chemical, and physical characterization performed on
sediment samples from each site.
VIII
-------
Appendix 2a Biology database.
Appendix 2b Chemistry database.
Appendix 2c Chemistry codes.
Appendix 2d Sample codes.
Appendix 3 a Summary of sediment effect concentrations (SECs) calculated using dry-weight
concentrations and listed by chemical, test type, and sample type for the entire
database.
Appendix 3b Summary of sediment effect concentrations (SECs) calculated using dry-weight
concentrations and listed by chemical, test type, and sample type for the Great
Lakes database.
Appendix 3c Summary of sediment effect concentrations (SECs) calculated using sediment
concentrations normalized to total organic carbon (TOC) concentrations and listed
by chemical, test type, and sample type for the entire database.
Appendix 3d Summary of sediment effect concentrations (SECs) calculated using sediment
concentrations normalized to total organic carbon (TOC) concentrations and listed
by chemical, test type, and sample type for the Great Lakes database.
Appendix 4a Data grouped by chemical, test type, sample type, toxicity response, and sediment
concentrations normalized to dry weight (in ascending order).
Appendix 4b PAH or PCB data grouped by chemical, test type, sample type, toxicity response,
and sediment concentrations normalized to TOC concentrations (in ascending
order).
Appendix 5 Other published toxicity data grouped by chemical, test type, sample type, toxicity
response, and sediment concentrations normalized to dry weight (in ascending
order).
Appendix 6 Other published sediment effect concentrations (SECs; dry-weight concentrations)
used to evaluate the comparability of our calculated SECs.
IX
-------
Acronyms
AET Apparent Effect Threshold
AOC Area of Concern
ARCS Assessment and Remediation of Contaminated Sediments
AVS Acid Volatile Sulfide
CR14 Chironomus riparius 14-dtest
EQP Equilibrium Partitioning
ERL Effect Range Low
ERM Effect Range Median
HA 10 Hyalella azteca 10-d test
HA 14 Hyalella azteca 14-d test
HA28 Hyalella azteca 28-d test
HS28 Hexagenia spp. 28-d test
LOEC Low Observable Effect Concentration
MATC Maximum Acceptable Toxicant Concentration
NEC No Effect Concentration
NERH No Effect Range High
NERM No effect Range Median
NOEC No Observable Effect Concentration
PAH Polycyclic Aromatic Hydrocarbon
PCB Polychlorinated Biphenyl
PEL Probable Effect Level
SEC Sediment Effect Concentration
SLC Screening Level Concentration
TEL Threshold Effect Level
TOC Total Organic Carbon
TT28 Tubifex tubifex 28-d test
-------
Acknowledgments
We would like to thank following members of the USEPA Great Lakes National Program Office
(GLNPO) Assessment and Remediation of Contaminated Sediments (ARCS) Toxicity-
Chemistry Work Group for assistance in designing the study and interpreting the results: G.A.
Burton, Jr., Wright State University, Dayton, OH; D.C. Cowgill, USEPA-GLNPO, Chicago, IL;
E.A. Crecelius, Battelle, Sequim, WA; J.C. Filkins, USEPA-LLRS, Grosse He, MI; R.G. Fox,
USEPA-GLNPO, Chicago, IL; J.P. Giesy, Jr., Michigan State University, East Lansing, MI; P.P.
Landrum, NOAA, Ann Arbor, MI; M.J. Mac, NBS, Washington, DC; T.J. Murphy, DePaul
University, Chicago, IL; J.E. Rathbun, AScI, Grosse He, MI; P.E. Ross, The Citadel, Charleston,
SC; V.E. Smith, AScI, Grosse He, MI; and H.E. Tatem, USCOE, Vicksburg, MS.
We would like to thank the following individuals for insight and guidance in developing
procedures to evaluate SECs: E.R. Long and J. Field, NOAA, Seattle, WA; D.D. MacDonald,
MacDonald Environmental Sciences, Ladysmith, BC; F.D. Calder and G. Sloane, Florida
Department of Environmental Protection, Tallahassee, FL; R.S. Carr, NBS, Corpus Christi, TX;
and S. Smith, Environment Canada, Hull, Quebec.
We thank the following individuals for providing helpful review comments on the report: G.T.
Ankley, USEPA, Duluth, MM; W.G. Brumbaugh, NBS, Columbia, MO; F.D. Calder and G.
Sloane, Florida Department of Environmental Protection, Tallahassee, FL; R. Fleming, WRc,
Marlow, Bucks, United Kingdom; P.P. Landrum, NOAA, Ann Arbor, MI; E.R. Long and J.
Field, NOAA, Seattle, WA; D.D. MacDonald, MacDonald Environmental Sciences, Ladysmith,
BC; M. Reiley:, USEPA, Washington, DC; and S. Smith, Environment Canada, Hull, Quebec.
XI
-------
Introduction
In support of the United States commitment to the Great Lakes Water Quality Agreement,
Section 118 (c)(3) of the Clean Water Act (CWA; added by the Water Quality Act of 1987)
authorized the USEPA GLNPO to carry out a 5-year study and demonstration project relating to
the control and removal of toxic pollutants in sediments of the Great Lakes. The Water Quality
Act of 1987 specified five Great Lakes Areas of Concern (AOC) as requiring priority
consideration in conducting demonstration protects: Saginaw Bay, MI; Sheboygan Harbor, WI;
Grand Calumet River, IN; Astabula River, OH; and Buffalo River, NY. Results from this
Assessment and Remediation of Contaminated Sediment (ARCS) project have been used to
develop: (1) methods for evaluating effects of contaminated sediments, (2) Remedial Action
Plans (RAPs) for AOCs, and (3) Lake-wide Management Plans (Ross et al., 1992; USEPA,
1994; Fox, 1996).
Over the past decade, a variety studies have reported toxicity associated with field-collected
sediments (USEPA, 1994; ASTM, 1995; Burton et al., 1996). However, it is often difficult to
evaluate relationships between levels of contamination and toxicity in these and other studies
because the sediments typically contain a variety of both organic and inorganic contaminants.
Procedures are described in this report for calculating and evaluating a variety of sediment effect
concentrations (SECs) using laboratory data on the toxicity of contaminants associated with
field-collected sediment to the amphipod Hyalella azteca and the midge Chironomus riparius.
We define SECs as the concentrations of individual contaminants in sediment below which
toxicity is rarely observed and above which toxicity is frequently observed.
Only a limited number of SECs have been published for freshwater sediments (Persaud et al.,
1992; Batts and Cubbage, 1995). The objective of the present study was to develop SECs to
classify toxicity data for Great Lake sediment samples tested with Hyalella azteca and
Chironomus riparius. This SEC database included samples from additional sites across the
United States in order to make the database as robust as possible. Three different approaches
were used to calculate SECs including: (1) Effect Ranges Low and Median (ERL and ERM;
Long and Morgan, 1991), (2) Threshold Effect and Probable Effect Levels (TEL and PEL;
MacDonald, 1994, MacDonald et al. 1995; Smith et al., 1996), and (3) No Effect Concentrations
(NEC; Kemble et al., 1994). The SECs were calculated using: (1) dry-weight concentrations, (2)
dry-weight concentrations normalized to total organic carbon concentrations (for non-ionic
organics) or (3) dry-weight concentrations normalized to acid volatile sulfide concentrations (for
divalent metals).
For the ARCS project, whole-sediment toxicity tests were conducted with the amphipod Hyalella
azteca (14- and 28-d tests) and the midges Chironomus riparius (14-d test) and Chironomus
tentans (10-d test; USEPA, 1993; Burton et al., 1996; Table 1 and Appendix 1). Only a limited
number of samples were successfully tested with C. tentans; therefore, we did not use these data
to calculate SECs. Chemistry, benthic community analysis, elutriate toxicity, and mutagenicity
of sediment samples were also evaluated as part of the ARCS project (USEPA, 1993; Burton et
-------
al. 1996). Sediments were collected from three Great Lakes Areas of Concern: Indiana Harbor,
IN; Buffalo River, NY; and Saginaw River, MI. In addition to the ARCS data, we evaluated
toxicity and chemistry data generated with sediments collected from the following sites: (1)
Waukegan Harbor, IL (Ingersoll and Nelson, 1990); (2) the upper Mississippi River, MN
(Appendix 2); (3) the upper Clark Fork River, MT (Kemble et al., 1994); (4) the Trinity River,
TX (Appendix 2); (5) Mobile Bay, AL (Appendix 2); and (6) Galveston Bay, TX (Roach et al.,
1993).
Ingersoll et al. (1996) described the major findings of this report as part of a series of papers
describing results from the ARCS project including: sediment chemistry, benthic community
analysis (Canfield et al., 1996a), toxicity (USEPA, 1993; Hall et al., 1996), mutagenicity
(Papoulias and Buckler, 1996; Papoulias et al., 1996), and toxicity ranking (Canfield et al.,
1996a; Wildhaber and Schmitt, 1996). Procedures in this series of papers are also described for
confirming the cause of sediment toxicity (e.g., Toxicity Identification Evaluations, TIE; Ankley
et al., 1996). Smith et al. (1996) also used our data and additional data from North America as
part of this series of papers to calculate and evaluate TELs and PELs for freshwater sediments.
Cause and Effect vs. Association and Effect
Our SECs were calculated from toxicity tests with field-collected samples. If a chemical
concentration exceeds an SEC generated using data from these tests with field-collected samples,
it does not necessarily mean the chemical caused the observed effect. Rather, the SEC is the
concentration of a chemical that is associated with the effect. Field-collected sediments typically
contain complex mixtures of contaminants. Additional information is needed to identify the
specific contaminants that were actually responsible for the toxicity. Confirmation of sediment
toxicity due to individual or groups of contaminants or the interactive effects of sediment
toxicants can be evaluated by using TIE procedures (Ankley and Thomas, 1992; Ankley et al.,
1996) or by conducting toxicity tests with chemicals spiked into sediments (Lamberson and
Swartz, 1992). Once the probable cause(s) of sediment toxicity has been identified, better
decisions can be made regarding remediation options.
Application of Sediment Effect Concentrations
Ideally, SECs could be used to: (1) interpret historical sediment chemistry data, (2) identify
chemicals or areas of concern, (3) identify the need for more detailed studies before an action is
taken, (4) identify a potential problem before discharging a chemical, (5) establish a link between
a contaminant source and sediment quality, (6) trigger regulatory action, or (7) establish target
remediation objectives. The strength of SECs generated using data from studies with individual
chemicals spiked into sediment or with an equilibrium partitioning (EQP) approach is that cause
and effect relationships can be established (Di Toro et al., 1991; USEPA, 1992). While, all
seven of the uses listed above for SECs could be satisfied with either of these approaches, both
the spiked-sediment and EQP approaches were developed primarily for evaluating the effects of
individual chemicals. However, contaminated sediments typically contain complex mixtures of
-------
chemicals which could act independently, additively, synergistically, or antagonistically.
Therefore, the application of SECs developed using these two approaches is often uncertain in
field-collected sediments (Swartz and Di Toro, 1996).
One of the main strengths of SECs generated using data from tests conducted with field-collected
samples is that the potential effects of mixtures of chemicals are explicitly addressed (Long and
Morgan, 1991; USEPA, 1992; MacDonald, 1994; Long et al., 1995; MacDonald et al., 1995).
However, there are a number of limitations associated with the co-occurrence-based approaches
that have been used to generate SECs including cause and effect is difficult to establish and use
of these SECs may be restricted to the geographical area where the sediments were collected.
Hence, the last four uses for SECs listed above are difficult to accommodate using co-
occurrence-based approaches such as a weight-of-evidence approach (Long and Morgan, 1991).
For example, these SECs should not be used independently to establish trigger levels for clean up
of sediment. One of the major strengths of SECs developed with data on field-collected
sediments is in their use for predicting the potential for toxicity in field-collected sediment
samples. A primary use of SECs developed with field-collected sediments should be to provide
guidance for determining sites which may require further investigation (Long and Morgan, 1991;
MacDonald, 1994). Moreover, the ability of any sediment toxicity test or SEC to predict benthic
community effects should be considered before any approach is used to routinely evaluate
sediment quality (Canfield et al., 1994; 1996a,b).
Regardless of the intended use, SECs should be evaluated relative to their potential to:
(1) correctly classify toxic samples as toxic (toxic sample that exceeds SEC [hit]),
(2) correctly classify non-toxic samples as not toxic (non-toxic sample that does not exceed
SEC [no hit]),
(3) incorrectly classify non-toxic samples as toxic (Type I error; false positive; non-toxic
sample that exceeds SEC [hit]), and
(4) incorrectly classify toxic samples as not toxic (Type II error; false negative; toxic sample
that does not exceed SEC [no hit]).
-------
Methods
The following steps were taken to develop the database: (1) chemistry and toxicity data were
generated, (2) samples were classified as "toxic" or "not toxic" based on statistical analyses of
the toxicity tests, (3) toxic samples were classified as "effects" or "no concordance" based on
chemistry, (4) minimum data requirements were established, and (5) SECs were calculated.
SECs were calculated for the following tests: (1) 14-d C. riparius [CR14], (2) 14-d H. azteca
[HAH], and (3) 28-d H. azteca [HA28] (Table 1). Chemical concentrations were used to
calculated SECs were normalized to: (1) dry weight, (2) total organic carbon (for non-ionic
organics; Di Toro et al., 1991), or (3) AVS (for divalent metals; Di Toro et al., 1990).
Calculations and graphics were performed using SAS version 6.08 (SAS, 1992).
Toxicity Testing
Toxicity tests with the amphipod Hyalella azteca were conducted for 10 to 32 d following
procedures outlined in Ingersoll and Nelson (1990), USEPA (1994), and ASTM (1995). Tests
were generally started within 3 weeks of sediment collection. The control sediment was a fine
silt- and clay-particle size soil obtained from an agricultural area. Twenty amphipods (less than
14-d old at the start of the tests) were exposed in 200 ml of sediment with 800 ml of overlying
water in 1-L beakers. Four replicate beakers were tested at 20°C on a 16L:8D photoperiod at a
light intensity of about 50 to 100 foot candles. Overlying water was renewed daily and the
amphipods were fed a suspension of Purina® Rabbit Chow three times a week. Endpoints
measured at the end of the amphipod tests were survival, growth (as length), or sexual
maturation. Toxicity tests with the midge Chironomus riparius were conducted for 13 to 14 d
using similar procedures to those used in the tests with amphipods except midges were <48-h old
at the start of the tests and midges were fed a mixture of algae, Cerophyl®, and Hartz Dog Treats®
daily. Endpoints measured at the end of the midge tests were survival and growth (as length).
Statistical analyses were conducted using one-way analysis of variance with mean separation.
For responses in which variance among treatments were heterogenous, rank analysis was
performed and differences between means were determine using a t-test on ranked means.
Percent survival and maturation data were arcsin transformed before analysis. A sample was
designated as "toxic" in a replicated treatment if there was a significant reduction in survival,
growth, or maturation relative to the response in the control sediment (p O.05). A sample was
designated as toxic in a non-replicated treatment if there was over a 50% reduction in the
response relative to the control sediment (10- to 13-d H. azteca or C. riparius tests with
sediments from Waukegan Harbor and the Trinity River).
SECs were calculated for the following tests: (1) 14-d C. riparius [CR14], (2) 14-d H. azteca
[HAH], and (3) 28-d H. azteca [HA28]. For calculation of SECs, the following data were
combined: (1) 10-d with 14-d H. azteca, (2) 29- to 32-d with 28-d H. azteca, and (3) 13-d with
14-d C. riparius.
-------
Appendices 1 and 2b lists the physical and chemical measurements made on each set of sediment
samples. Physical characterizations included organic carbon content, water content, and particle
size. Chemical characterizations included total metals (Ag, As, Cd, Cr, Cu, Fe, Hg, Mn, Ni, Pb,
Se, Zn), organometals (butyltins and methyl mercury), acid volatile sulfide (AVS) and
simultaneously extracted metals (SEM), chlorinated pesticides, total polychlorinated biphenyls
(PCBs), polychlorinated dioxins and furans, or polycyclic aromatic hydrocarbons (PAHs). Metal
concentrations in pore water were also measured in selected samples (USEPA, 1993).
Sediment toxicity data were obtained for the sites listed below (Table 1 and Appendices 1 and
2b). Suspected toxicants were mixtures of metals and organic compounds except for the samples
from the upper Clark Fork River where suspected toxicants were primarily As, Cd, Cu, Pb, and
Zn.
Great Lakes ARCS: Sediments were collected from three Great Lakes Areas of Concern: Indiana
Harbor (up to 8 samples tested in August 1989), Buffalo River (up to 11 samples tested in
October 1989), and Saginaw River (up to 8 samples tested during Survey 1 in December 1989
and up to 16 samples tested during Survey 3 in June 1990). Toxicity tests were conducted with
H. azteca (14- and 28-d tests) and C. riparius 14-d test). All of the Indiana Harbor samples were
extremely toxic to amphipods in the 14-d test. Therefore, a 28-d test with amphipods was not
conducted. We assumed for the calculation of SECs that Indiana Harbor samples toxic to
amphipods in a 14-d test would also be toxic in a 28-d test.
Waukegan Harbor: Toxicity tests were conducted with 4 sediment samples from Waukegan
Harbor, IL in November 1987 (H. azteca 10- and 29-d tests, C. riparius 13-d test).
Upper Mississippi River: Toxicity tests were conducted with 5 sediment samples from the upper
Mississippi River near Minneapolis, MN in September 1987 (H. azteca 32-d test).
Upper Clark Fork River: Sediment samples were collected from Milltown Reservoir (8 samples
tested in July 1991) and the Clark Fork River, MT (7 samples tested in September 1991).
Toxicity tests were conducted with H. azteca (28-d test) and C. riparius (14-d test).
Trinity River: Toxicity tests were conducted with 5 sediment samples from the Trinity River,
near Dallas, TX in June 1988 (H. azteca 10- and 32-d tests).
Mobile Bay: Toxicity tests were conducted with 6 sediment samples from Mobile Bay, AL in
March 1988 (H. azteca 28-d test). The test was conducted under static conditions with 10%o
salinity in the overlying water.
Galveston Bay: Toxicity tests were conducted with 5 sediment samples from Galveston Bay, TX
in July 1990 (H. azteca 28-d test). The test was conducted under static conditions with 10%o
salinity in the overlying water.
-------
Classification of Effects and Minimum Data Requirements for Reporting SECs
To increase the likelihood that associations between sediment chemistry and toxicity would be
observed, the data were screened to determine if at least a 10-fold difference in concentration for
at least one chemical among the samples was met from each site (Long and Morgan, 1991;
MacDonald, 1994). The chemicals measured in each sample were classified in terms of their
association with the observed toxicity. Each of the chemicals in the toxic samples were
classified as an "effect" or "no concordance" depending on whether the ratio of the concentration
in the sample to the mean concentration in the non-toxic samples was >1 or <1. Concentrations
of chemicals in non-toxic samples were designated as "no effects". Samples designated with the
no concordance descriptor were also included with the no-effect samples for calculation of SECs.
Long and Morgan (1991), MacDonald (1994), Long et al. (1995), MacDonald et al. (1995), and
Smith et al. (1996) used a similar designation; however, they considered a chemical to be
associated with a toxic effect only if the mean concentration in toxic samples at a site was at least
two fold greater than the mean concentration in non-toxic samples at a site. We chose to use a
ratio of >1 instead of >2 to classify a sample as an "effect" in order to minimize Type II error
(toxic sample classified as not toxic). We reported an SEC of a chemical in Appendices 3 and 4
only if: (1) five or more of the samples were toxic for the chemical and (2) the number of toxic
samples with concentrations above the SEC was greater than the number of toxic samples with
concentrations below the SEC.
Calculation of Effect Range Low CERL') and Effect Ranee Median (ERM): We calculated ERLs
and ERMs using procedures described by Long and Morgan (1991) and Long et al. (1995). Our
ERLs and ERMs are calculated for individual tests (e.g., the H. azteca 28-d test) in order use
consistent endpoints for determining a toxic response. In contrast, Long and Morgan (1991)
merged data from about 75 sources. These sources included marine and freshwater field surveys,
spiked-sediment tests, and EQP. Effect ranges were calculated by Long et al. (1995) for 9
metals, 13 individual PAHs, 3 groups of PAHs, and 3 synthetic organic contaminants. Strengths
of the Long et al. (1995) approach include: (1) ranges instead of absolutes (e.g., AET) are
calculated, (2) a preponderance of evidence from diverse sources is used to generate the ranges
(e.g., weight of evidence), and (3) probability of observing effects can be estimated. Limitations
to the Long et al. (1995) approach include: (1) the quality of the data was variable, (2) different
types of data were merged (e.g., acute lethality and benthic community structure were combined
to calculate effect ranges), (3) concentrations were calculated on a dry-weight basis (data on
sediment organic carbon and AVS concentrations were not available for all data sets), and (4) no-
effect data are not used in the calculation of ERLs or ERMs.
Long et al. (1995) calculated ERLs and ERMs using the following procedure. Concentrations
observed or predicted by different methods to be associated with effects were sorted in ascending
order, and the lower 10 percentile (ERL) and 50 percentile (ERM) effect concentrations were
calculated. An ERL was defined by Long and Morgan (1991) and Long et al. (1995) as the
concentration of a chemical in sediment below which adverse effects were rarely observed or
predicted among sensitive species. An ERM was defined as the concentration of a chemical in
-------
sediment above which effects are frequently or always observed or predicted among most
species. Use of percentiles minimized the influence of single data points (e.g., potential outliers
associated with AETs) on SECs. No-effect data were used to evaluate the reliability of ERLs
and ERMs calculated using only effect data (Long et al., 1995). We chose to calculate ERLs
using the 15 percentile rather than using the 10 percentile of effects to reduce the potential for
Type II error (false negatives; MacDonald et al. (1995; see below)).
Calculation of Threshold Effect Level (TEL) and Probable Effect Level TPEL^: We calculated
TELs and PELs using procedures described by MacDonald (1994) and MacDonald et al. (1995).
Our TELs and PELs are calculated for individual tests (e.g., a H. azteca 28-d test) in order use
consistent endpoints for determining a toxic response. MacDonald (1994) and MacDonald et al.
(1995) calculated TELs and PELs by expanding two to three fold the database originally
developed by Long and Morgan (1991) and by excluding freshwater data. Effect ranges were
calculated by MacDonald et al. (1995) for 9 metals, 7 pesticides, 13 individual PAHs, 3 groups
of PAHs, total PCBs, and one phthalate ester. A similar procedure was used to calculate
freshwater TELs and PELs for 8 metals, 6 individual PAHs, total PCBs, and 8 pesticides (Smith
et al., 1996). Strengths and limitations to this approach are similar to the ERL/ERM approach.
However, calculation of TELs and PELs take both effect and no-effect data into consideration.
MacDonald et al. (1995) and Smith et al. (1996) calculated TELs and PELs using the following
procedure. Concentrations observed or predicted by different methods to be associated with
effects were sorted and the lower 15 percentile (ERL) and 50 percentile (ERM) concentrations of
the effects data set were calculated. In addition, the 50 percentile (No Effect Range Median;
NERM) and 85 percentile (No Effect Range High; NERH) concentrations of the no effects data
set were calculated. The TEL was calculated as the geometric mean of the ERL and NERM,
whereas the PEL was calculated the geometric mean of the ERM and NERH. The geometric
mean was used rather than the arithmetic mean because the two data sets are typically not
normally distributed. An analogous procedure has been used to calculate Maximum Acceptable
Toxicant Concentrations (MATCs) from the geometric mean of the no-observable- and low-
observable-effect concentrations (LOEC and NOEC; MacDonald, 1994). For each of the values
(ERL, ERM, NERM, and NERH), a series of percentiles was evaluated to optimize correct
classification of toxicity using the TELs and PELs (MacDonald, 1994).
A TEL (or ERL) is assumed to represent a concentration below which toxic effects are rarely
observed. A PEL (or ERM) is assume to represent a concentration above which toxic effects are
frequently observed. The range between the TEL and PEL (or between the ERL and ERM) is
assume to represent the range in which effects are occasionally observed (MacDonald, 1994).
Probability of toxic effects can be calculated within each range. For example, only 6% of the
cadmium (Cd) concentrations reported by MacDonald (1994) below the TEL of 0.68 ug/g were
associated with adverse effects, whereas over 71% of the Cd concentrations above the PEL of
4.21 ug/g were associated with toxic effects. These Cd data indicate that exceeding the PEL may
be associated with unacceptable effects. In contrast, 3% of the nickel (Ni) concentrations below
the TEL of 15.9 ug/g and 9% of the Ni concentrations above the PEL of 42.8 ug/g were
-------
associated with toxic effects. These Ni data indicate that it may be more difficult to adequately
determine unacceptable levels of Ni using this approach (e.g., toxic concentrations of Ni were not
observed the MacDonald (1994) database).
The approaches described by Long et al. (1995) and MacDonald et al. (1995) have been used by
NOAA (Long and Morgan, 1991), Environment Canada (CCME, 1995), and the state of Florida
(MacDonald, 1994) to derive sediment quality guidelines. Additional organizations that are
considering the use of these approaches to derive sediment quality guidelines include the state of
California (Lorenzato et al., 1991), the International Council for Exploring the Sea, and the
National Rivers Authority in the United Kingdom (R. Fleming, WRc, Marlow, Bucks, United
Kingdom, personal communication).
Calculation of No Effect Concentration fNEQ: We also calculated No Effect Concentrations
(NECs) which are analogous to Apparent Effect Thresholds (AETs). An AET is defined as the
sediment concentration of a given chemical above which statistically significant effects (e.g.,
sediment toxicity) are always observed (Barrick et al., 1988). If any chemical exceeds its AET
for a particular response, an adverse effect is expected for that response. If all concentrations of
chemicals are below their AET for a particular response, then no adverse effect is expected. The
AET approach has been applied to contaminated sediment in marine environments (e.g., in the
Puget Sound, Barrick et al. (1988) and in California, Becker et al. (1989)); however, the AET
approach has rarely been used to evaluate freshwater sediments (Kemble et al., 1994).
A NEC is calculated as the maximum concentration of a chemical in a sediment that did not
significantly adversely affect the particular response (e.g., survival, growth, or maturation)
compared to the control. We chose to use the term NEC instead of AET because: (1) we
calculated NECs for whole-sediment or pore-water concentrations, while AETs are typically
calculated for just whole-sediment concentrations; (2) a minimum of 25 to 50 samples is
recommended for calculating an AET and we used <25 samples to calculate some of our NECs;
and (3) we calculated effects relative to a control sediment, whereas AETs are typically
calculated relative to reference sediments.
Evaluation of Sediment Effect Concentrations
If the concentration of a chemical measured in a toxic sample exceeded an SEC, the chemical in
that sample was classified as a "hit" for that SEC. Our SECs were then evaluated relative to their
potential to: (1) correctly classify toxic samples as toxic (toxic sample that exceeds SEC [hit]),
(2) correctly classify non-toxic samples as not toxic (non-toxic sample that does not exceed SEC
[no hit]), (3) incorrectly classify non-toxic samples as toxic (Type I error; false positive; non-
toxic sample that exceeds SEC [hit]), or (3) incorrectly classify toxic samples as not toxic (Type
II error; false negative; toxic sample that does not exceed SEC [no hit]). The SECs were
evaluated relative to their: (1) reliability in terms of correctly classifying the toxicity of sediment
samples within the data set, (2) predictive ability for correctly classifying the toxicity of sediment
8
-------
samples from independent data sets, and (3) comparability within the data set or to other
published SECs such as AET, ERM, PEL, or EQP values.
-------
Results and Discussion
Toxicity of Sediment Samples
The percentage of sediment samples identified as toxic (e.g., significant reduction in survival,
growth, or maturation relative to the control) in each sediment test are listed in Table 1. Survival
or growth of C. riparius in 14-d tests (CR14) were significantly reduced in 26% of the 42
samples tested. In the CR14 tests when both survival and growth were measured, survival (24%)
was reduced more frequently than growth (9%). Sediments from the Clark Fork River (7%) were
less toxic in the CR14 test than sediments from the Great Lakes (37%). Survival, growth, or
maturation of H. azteca in 14-d tests (HAM) were reduced in 41% of the 32 samples tested. In
the HAH test, survival (25%), growth (20%), and maturation (24%) were reduced in a similar
percentage of samples. None of the Trinity River samples were toxic; however, 48% of the
Great Lakes samples were toxic in the HAM test. Survival, growth, or maturation of H. azteca
in the 28-d tests (HA28) were reduced in 39% of the 62 samples tested. In the HA28 test,
survival (26%) and growth (34%) were reduced in a higher percentage of samples compared to
maturation (11%). None of the upper Mississippi River, Trinity River, or Mobile Bay samples
were toxic; however, 48 to 60% of the Great Lakes, Clark Fork River, or Galveston Bay samples
were toxic in the HA28 test.
The percentage of paired tests or paired endpoints identifying samples as toxic are listed in Table
2. The CR14 test seldom identified toxic samples that were not identified as toxic in the HAH
or HA28 tests. When CRH and HA28 tests were conducted concurrently, both tests identified
24% of the samples as toxic and 48% of the samples as not toxic (N=42). An additional 26% of
the samples were toxic only in the HA28 test and only an additional 2% of the samples were
toxic in the CRH test. Survival (N=42) or growth (N=34) endpoints identified a higher
percentage of samples as toxic in the HA28 test compared to the CRH test.
When HAH and CRH tests were conducted concurrently, both tests identified 37% of the
samples as toxic and 52% of the samples as not toxic (N=27). An additional 10% of the samples
were toxic only in the HAH test and no additional samples were toxic in the CRH test. The
survival endpoint (N=27) identified a similar percentage of samples as toxic in both tests. The
growth endpoint (N=19) identified a higher percentage of samples toxic in the HAH test (21%)
compared to the CRH test (5%).
The HA28 test seldom identified toxic samples that were not identified as toxic in the HAH test.
When HAH and HA28 tests were conducted concurrently, both tests identified 34% of the
samples as toxic and 53% of the samples as not toxic (N =32). Both tests identified an additional
6% of the samples as toxic. Survival or growth endpoints identified a similar percentage of
samples as toxic in both tests. However, the majority of the samples used to make these
comparisons were highly contaminated. We have not compared responses in HAH vs HA28
tests using moderately contaminated samples. Additional exposures conducted with moderately
10
-------
contaminated sediment may exhibit a higher percentage of sublethal effects in the HA28 test
compared to HAH test (Kemble et al. 1994).
When both survival and growth were measured in the CR14 test (N=34), 6% of the samples
reduced both survival and growth, 6% reduced survival only, 3% reduced growth only, and 85%
did not reduce survival or growth. When both survival and growth were measured in the HAH
test (N=25), only 6% of the samples reduced both survival and growth; however, 20% reduced
survival only, 16% reduced growth only, and 60% did not reduce survival or growth. Hence, if
survival was the only endpoint measured in a HAH test, 16% of the toxic samples would be
missed. Similar percentages are also evident for the HA28 tests. When both survival and growth
were measured in the HA28 test (N=44), 16% of the samples reduced both survival and growth,
14% reduced survival only, 18% reduced growth only, and 52% did not reduce survival or
growth.
The endpoint comparisons in Table 2 represent only samples where both survival and growth
could be measured. If a sample was extremely toxic, it would not be included in this comparison
since growth could not be measured. Moderately contaminated sediments that did not severely
reduce survival or maturation could have reduced growth. For example, in the HA28 test with
sediments from the Clark Fork River, growth was a more sensitive endpoint compared to
survival or maturation. Only 13% of the samples reduced survival and 20% of the samples
reduced maturation; however, growth was reduced in 53% of the samples.
In summary, both survival and growth endpoints can provide unique information for assessing
sediment toxicity and should be measured in either HAH or HA28 tests. Using CR14 test, only
one additional sample was identified as toxic compared to responses in the HAH or HA28 tests.
A primary consideration in selecting an organism for toxicity testing should be its ability to
identify toxic samples (Burton et al., 1996). In future evaluations, it may be a more efficient use
of resources to test additional samples with H. azteca alone rather than testing fewer sediments
using both H. azteca and C. riparius.
Calculation and Evaluation of SECs
The SECs calculated from our database are listed by chemical, test type, and sample type based
on dry-weight concentrations (Appendix 3a for the entire database or Appendix 3b for the Great
Lakes database) or based on sediment concentrations normalized to total organic carbon
concentrations (TOC; Appendix 3c for the entire database or Appendix 3d for the Great Lakes
database). Data are grouped by chemical, test type, sample type, toxicity response, and
concentration (in ascending order) calculated using dry-weight concentrations (Appendix 4a) or
to sediment concentrations normalized to TOC concentrations (PAHs or PCBs; Appendix 4b).
We were able to calculate SECs primarily for total metals, simultaneously extracted metals (SEM
metals), total PCBs (for the HA28 test), and PAHs. The ranges of concentrations in the samples
were too narrow or there were too few measured concentrations in our database to adequately
11
-------
evaluate SECs for butyltins, methyl mercury, polychlorinated dioxins and furans, PCBs (for the
CR14 or HAH tests), or chlorinated pesticides (i.e., not reported (NR) in Appendix 3a to 3d).
An unreliable SEC for individual chemicals listed in Appendices 3 and 4 is denoted with an "@"
(e.g., less than five of the samples were designated as toxic for the chemical or the number of
toxic samples with concentrations below the SEC was greater than the number of toxic samples
with concentrations above the SEC). See for example the unreliable NEC for total copper
denoted with an @ for the CR14 test in Appendix 3a. The SECs for a particular chemical listed
in Appendix 3 vary considerably in ability to make correct or incorrect classifications of toxic or
non-toxic samples. For example, correct classification of samples with individual SECs
typically clustered at 60 to 80% correct. Type I (false positives) and Type II (false negatives)
error for individual SECs ranged from 0 to 50% depending on the type SEC (i.e., Figure 1 to 5).
The following section discusses some applications of the database for deriving SECS for
classifying the toxicity of samples: (1) Great Lakes vs the entire database, (2) ERMs and ERLs
vs PELs and TELs, (3) NECs vs other SECs, (4) dry-weight vs TOC normalization for PAHs and
total PCBs, (5) whole-sediment vs pore-water metal concentrations, (6) total metal vs SEM metal
concentrations, and (7) calculation of observed and predicted toxicity based on the minimum
number of exceedances of SECs. Additional sections of the report evaluate: (1) predictive
ability of our SECs, (2) comparability of our SECs to published SECs, and (3) confirming
causality of SECs. Additional applications of the database may be of interest to the reader. A
copy of the SAS (1992) programs used to manipulate the database can be obtained from the
authors.
Great Lakes vs the Entire Database: Initially, the objective of this report was to develop SECs
to classify toxicity data for Great Lake sediment samples tested with Hyalella azteca and
Chironomus riparius (Appendix 3b and 3d). However, the database was expanded to include
samples from additional locations (Appendix 3a and 3c). This section of the report evaluates the
comparability and reliability of SECs calculated using just the Great Lakes database vs SECs
calculated using the entire database (Figure 1 to 5). Comparability was evaluated by plotting the
ratio of concentrations for two similar types of paired SECs (e.g., Figure la to 5a). Reliability
was evaluated by plotting the ability of two similar types of paired SECs to: (1) correctly classify
samples (e.g., Figure Ib to 5b), (2) incorrect classify non-toxic samples as toxic (hit; Type I
error; false positive; Figure Ic to 5c), and (3) incorrectly classify toxic samples as not toxic (no
hit; Type II error; false negative; Figure Id to 5d).
The ERM-Gs, PEL-Gs, ERL-Gs, and TEL-Gs calculated using just the Great Lakes database (GL
SECs in Appendix 3b) tended to be higher than the paired ERMs, PELs, ERLs, and TELs
calculated using the entire database (all-data SECs; Appendix 3a; Figure la to 4a). However,
these GL SECs were within 2X of the paired all-data SECs. This indicates that the toxicity
observed in the additional samples (i.e., outside the Great Lakes) occurred at lower sediment
concentrations. An exception to the trend of higher GL SECs was the HAH ERMs and ERLs
which were identical using the two databases (Figure la and 3a). This was expected since the
additional HAH data were non-toxic samples from the Trinity River (Table 1) and ERLs and
12
-------
ERMs are calculated using only toxic samples. For the HA28 test, the all-data NECs were often
higher than the paired GL NECs (NEC-Gs; Figure 5a). This is not surprising since NECs by
definition can only increase with additional data.
Even though the concentrations of the paired SECs differed (Figure la to 5a), the percentage of
the Great Lakes samples correctly classified by paired GL SECs and all-data SECs were similar
(Figure Ib to 5b). A high percentage (>77%) of these paired comparisons of correct
classifications were within a range of +20% for all three toxicity tests. For the CR14 and HA14
tests, Type I error (Figure Ic to 5c) and Type II error (Figure Id to 5d) were generally consistent
between paired SECs. For the HA28 test, Type I error tended to be higher and Type II error
tended to be lower for all-data SECs compared to paired GL SECs. Exceptions to these trends in
the HA28 test were Type I error tended to be lower (Figure 5c) and Type II error tended to be
higher (Figure 5d) for all-data NECs compared to paired NEC-Gs. In summary, these analyses
indicate the all-data SECs are generally as reliable as the GL SECs at classifying both toxic and
non-toxic Great Lakes samples in our database. Therefore, the remaining sections of the report
evaluate SECs calculated using the entire database.
ERMs and ERLs vs PELs and TELs: The ERMs or ERLs for the entire database tended to be
higher than the paired PELs (Figure 6a) or TELs (Figure 7a) for the entire database. This
resulted from a lower distribution of concentrations in non-toxic samples (e.g., low NERM or
NERH) relative to the ERM or ERL. An exception to this trend was uniform distribution of
ERMs and PELs for the HA28 test (Figure 6a). The SECs were typically +2X of their paired
SEC (Figure 6a and 7a). Although the concentrations of the paired ERMs and PELs differed, the
percentage of samples correctly classified by paired SECs was similar for all three tests (>96%;
Figure 6b). ERLs tended to correctly classify a higher percentage of samples compared to paired
TELs (Figure 7b). Type I error was generally lower and Type II error tended to be higher with
ERMs and ERLs compared to paired PELs (Figure 6c and 6d) or TELs (Figure 7c and 7d).
These analyses indicate the ERMs and ERLs are generally as reliable as the PELs and TELs at
classifying both toxic and non-toxic samples in our database.
The ERMs and PELs were higher than their respective paired ERL (Figure 8a) or TEL (Figure
9a). This was expected since ERMs and PELs by definition can only be higher than paired ERLs
or TELs. The percentage of samples correctly classified by ERMs and PELs (Figure 8b and 9b)
and the Type II error (Figure 8d and 9d) were higher compared to the paired ERLs and TELs. In
contrast, the Type I error was higher for ERLs and TELs compared to their respective paired
ERM (Figure 8c) or PEL (Figure 9c). These analyses indicate the ERMs and PELs are more
reliable than ERLs and TELs at correctly classifying samples, but ERLs and TELs minimize
Type II error (toxic sample classified as no hit).
NECs vs other SECs: The NECs were typically higher than their respective paired ERM (Figure
lOa) or ERL (Figure 1 la). Again, this was expected since NECs (the high no effect
concentration) would typically be greater than the 50- (e.g., ERM) or 15- (e.g., ERL) percentile
effect concentration. The percentage of samples correctly classified by NECs were similar to
13
-------
paired ERMs (Figure lOb) and higher than paired ERLs (Figure 1 Ib). Type I error associated
with NECs were typically lower compared to the paired ERMs (Figure lOc) or ERLs (Figure
1 Ic). However, Type II error (toxic sample classified as no hit) were typically higher with NECs
compared to either paired ERMs (Figure lOd) or ERLs (Figure 1 Id). These analyses indicate the
overall reliability of ERMs is similar to NECs; however, ERMs and ERLs both minimize Type II
error compared to NECs.
Dry-weight vs (TOC) Normalization for PAHs and Total PCBs: The SECs for PAHs and
total PCBs were calculated using dry-weight concentrations (Appendices 3a, 3b, 4a) or
calculated using sediment concentrations normalized to TOC concentrations (Appendices 3c, 3d,
4b). The percentage of samples correctly classified using SECs calculated using dry-weight
concentrations tended to be higher than the paired SECs calculated using sediment
concentrations normalized to TOC concentrations (Figure 12a to 14a). Type I error (Figure 12b
to 14b) and Type II error (Figure 12c to 14c) were generally consistent between paired SECs.
Exceptions to these trends were Type I error was generally lower for ERMs calculated using dry-
weight concentrations compared to paired ERMs calculated using sediment concentrations
normalized to TOC concentrations (Figure 12b) and Type II error was generally lower for NECs
calculated using dry-weight concentrations compared to paired NECs calculated using sediment
concentrations normalized to TOC concentrations for the HAH test (Figure 14c).
Whole-sediment vs Pore-water Metals: The percentage of the samples correctly classified by
ERMs, NECs, and ERLs calculated using pore-water concentrations of metals tended to be
slightly lower than paired SECs calculated using total metal concentrations (Figure 15a, 16a,
17a) or calculated using SEM metal concentrations (Appendix 3a). No consistent trends was
evident for Type I error between paired SECs among tests (Figure 15b, 16b, 17b). Type II error
was generally lower for total-metal SECs compare to paired pore-water metal SECs (Figure 15c,
16c, 17c). Exceptions to this trend were lower Type II error associated with pore-water NECs
for the CR14 test. In summary, these analyses indicate for metals, SECs calculated using pore-
water concentrations did not improve reliability compared to SECs calculated using total-metal
concentrations.
Total Metals vs SEM Metals: The percentage of the samples correctly classified by ERMs,
NECs, and ERLs calculated using total-metal concentrations tended to be higher than paired
SECs calculated using SEM-metal concentrations (Figure 18a, 19a, 20a). No consistent trends
were evident for Type I error associated with paired SECs among the tests (Figure 18b, 19b, or
20b); however, Type II error was generally lower for total-metal SECs compare to paired SEM-
metal SECs (Figure 18c, 19c, 20c). In summary, these analyses indicate for metals, SECs
calculated using SEM-metal concentrations did not improve reliability compared to SECs
calculated using total-metal concentrations.
Acid-volatile sulfide (AVS) has been demonstrated to control pore-water concentrations and
bioavailability of divalent metals in 10-d toxicity and bioaccumulation exposures. Divalent
metals in sediment with a molar SEM/AVS ratio <1.0 would not be predicted to be toxic or to be
14
-------
bioaccumulated by aquatic organisms (Di Toro, 1990). Concentrations of AVS were determined
for only 18 samples from the Great Lakes and 13 samples from the Clark Fork River (CFR;
Appendix 4a). Ratios of SEM/AVS were well below 1.0 for all Great Lakes samples and only 5
of 13 CFR samples exceeded SEM/AVS ratios of 1.0. Of the 5 CRF samples with SEM/AVS
ratios >1.0, only 1 sample was toxic in the CR14 test and 4 samples were toxic in the HA28 test.
Hence, there was an insufficient number of samples in the database to calculate SECs for
exceedances of SEM/AVS ratios. Samples were often toxic at SEM/AVS ratios <1.0 suggesting
contaminants other than metals may have caused the toxicity. SECs calculated using total-metal
concentrations often correctly classified >60% of the samples. These results indicate metals may
have been associated, but did not cause the toxicity observed in the Great Lakes samples with
SEM/AVS ratios <1.0.
Calculation of the Minimum Number of Exceedances of SECs: A second approach used to
evaluate reliability of SECs was to plot observed and expected toxicity of samples based on the
minimum number of exceedances of SECs. For example, Figure 21a is a plot of the percentage
of samples correctly classified as a function of the minimum number of individual ERMs
exceeded. In the CR14 test, if an exceedance of an ERM for only one chemical is used to
classify a sample as a hit, about 65% of the samples were correctly classified as toxic or not toxic
and about 30% of the non-toxic samples were classified as hits (Type I error; false positive).
However, the Type II error was only 5% (toxic samples classified as no hit; false negative). As
the criteria for a hit is increased to 2 or more ERM exceedances per sample in the CR14 test, the
percentage of samples correctly classified increased to about 80%, Type II error increased to
almost 20%, and Type I error decreased to <5%. In the HAH test, the highest correct
classification of about 75 to 85% occurs in the range of about 2 to 4 ERM exceedances (Figure
2la). In this range, Type I and Type II errors are equal (i.e., cross over of the not toxic/hit line
with the toxic/no hit line). In contrast, the highest correct classification of about 70% for the
HA28 test occurs across 3 to 10 exceedances with Type I equal to Type II error at about 7
exceedances.
Figure 21b plots correct classification of samples as a function of ERM exceedances using only
those chemicals for which individual ERMs correctly classify >60% of the samples (Figure 21 a
used all the individual ERMs listed in Appendix 3a regardless of percentage correct
classification). The number of ERMs used in the calculations remained the same for the CR14
and HAH tests (Figure 21a vs 21b); however, selecting a criterion of 60% reduced the number of
ERMs used in the calculations from 25 to 20 in the HA28 test. As a result, correct classification
increased by about 5 to 10% across 1 to 10 exceedances in the HA28 test (Figure 21a vs 21b).
This increased correct classification resulted from a reduction in Type I error (not toxic/hit).
Selecting a criterion of 70% correct classification for individual ERMs reduced the number of
ERMs used in the calculation from 22 to 21 in the CR14 and HAH tests, and from 25 to 9 in the
HA28 test (Figure 21 a vs 21c). At 1 exceedance, correct classifications increased in all three
tests by about 10 to 20% and both Type I and Type II error were only about 10% (Figure 21a vs
21c). However, increasing the minimum number of exceedances decreased correct
15
-------
classifications of samples in the HA28 test (Figure 21c). This drop in correct classification
results from increased Type II error (toxic/no hit) when fewer ERMs are used in the calculation
(Figure21avs21c).
In summary, correct classification of samples can be improved by using individual ERMs with a
higher percentage of correct classification. For example, using a 70% criterion for selection of
ERMs, only 1 ERM had to be exceeded in any of the three tests to achieve about 80 to 90%
correct classification of samples with only about 10% Type I and Type II errors. By lowering the
criterion to 60% for selection of ERMs, exceeding 2 to 5 ERMs still resulted in about 70 to 80%
correct classification of samples.
Figure 22a plots correct classification of samples as a function of ERL exceedances (regardless
of percentage correct classification by individual ERLs in Appendix 3a). Type II error (false
negatives) remains relatively low (<10%) across the range of 1 to 10 ERL exceedances. The
highest correct classification of about 60 to 70% occurs at >5 to 6 ERL exceedances. However,
Type I error (false positives) was always higher (>20 to >40%) compared to Type II error
resulting in lower percentage correct classification with ERLs compared to ERMs (Figure 2la vs
22a).
Selecting a criterion of 60% did not substantially improve classification by ERLs in the CR14 or
HAH tests, but correct classification increased about 10 to 30% in the HA28 test (Figure 22a vs
22b). Using a 70% criterion for selection of ERLs, 70 to 90% of the samples were correctly
classified with 8 to 10 exceedances in the CR14 and HAM tests and with 1 to 2 exceedances in
the HA28 test (Figure 22a vs 22c). However, in the HA28 test only non-toxic samples are
correctly classified at 3 or more ERL exceedances because of the high Type II error (toxic/no hit)
resulting from using just 2 ERLs (Figure 22c). In summary, correct classification of samples can
be improved by using multiple ERLs with a high percentage of correct classification. However,
samples which exceeded multiple ERLs were typically samples which also exceeded ERMs.
Hence, exceeding a few ERMs or multiple ERLs resulted in similar correct classification of
samples.
For NECs, about 70 to 90% of samples are correctly classified at 1 to 10 exceedances regardless
if all the NECs (Figure 23a), the 60% criterion (Figure 23b), or the 70% criterion (Figure 23c)
are used. Type I and Type II errors are generally equal at about 1 to 3 exceedances. However,
Type II error (false negatives) often starts at 5 to 10% with only 1 exceedance. Increasing the
minimum number of exceedances decreased correct classification of samples. This drop in
correct classification results from increased Type II error if multiple exceedances of NECs are
required to classify a sample as toxic.
Figure 24 directly compares correct classification, Type I error, and Type II error as a function of
the minimum number of ERL, ERM, or NEC exceedances for the HA28 test. ERLs only classify
about 40 to 60% of the samples correctly. The higher Type I error associated with ERLs
compared to either ERMs or NECs results in this lower correct classification by ERLs. ERMs
16
-------
and NECs correctly classify a similar percentage of samples; however, Type II error is
consistently higher with NECs compared to either ERMs or ERLs. In summary, these analyses
indicate the reliability of correct classifications is similar between ERMs and NECs; however,
ERMs minimize Type I error relative to ERLs and minimize Type II error relative to NECs. The
high Type I error typically associated with ERLs is the primary reason Long et al. (1995) and
MacDonald et al. (1995) recommend ERMs and PELs, but not ERLs or TELs should be used to
predict toxicity of samples. However, ERLs and TELs can be used to efficiently identify
concentrations below which toxicity is rarely observed.
Reliability of ERMs for PAHs and total PCBs calculated using dry-weight concentrations
(Appendix 3a) and calculated using sediment concentrations normalized to TOC concentrations
(Appendix 3c) are plotted in Figure 25. None of the individual ERMs calculated using sediment
concentrations normalized to TOC correctly classified >70% of the samples. Therefore, Figure
25 plots correct classification of samples as a function of ERM exceedances using only
individual ERMs which correctly classify >60% of the samples in the HA28 test (n = 11 SECs).
Correct classification of samples ranged between 60 to 70% and Type I and Type II errors were
similar based on exceedances of ERMs using either dry-weight concentrations or sediment
concentrations normalized to TOC concentrations. Correct classifications were also similar
using PELs and NECs calculated using dry-weight concentrations or calculated using sediment
concentrations normalized to TOC concentrations.
One would expect SECs calculated using sediment concentrations normalized to TOC
concentrations to be more reliable than SECs calculated using dry-weight concentrations since
TOC reportedly controls the bioavailability of non-ionic organic contaminants such as PAHs and
PCBs in sediment (Di Toro et al., 1991). The range of TOC concentrations in our database was
relatively narrow compared to the ranges of contaminant concentrations. The mean
concentration of TOC was 2.7% with a 95% confidence interval of only +0.65% (n=62). In
contrast, the concentration ranges of contaminants calculated using dry-weight concentrations
typically varied by several orders of magnitude. Therefore, normalizing dry-weight
concentrations to a relatively narrow range of TOC concentrations had little influence on relative
concentrations of contaminants among samples. Similar findings were reported by Barrick et al.
(1988) for AETs and Long et al. (1995) for ERMs calculated using sediment concentrations
normalized to TOC concentrations. However, it is surprising that there was not at least a trend of
increased reliability with SECs calculated using sediment concentrations normalized to TOC
concentrations. The lower reliability of SECs calculated using sediment concentrations
normalized to TOC concentrations may indicate PAHs and PCBs were not causing the toxicity,
but were only associated with the toxic chemicals. Use of sediment toxicity identification
evaluations (TIE) or studies using spiking of sediment are needed to establish these cause and
effect relationships (Ankley and Thomas, 1992; Lamberson and Swartz, 1992; Ankley et al.,
1996).
17
-------
Predictive Ability of SECs
The predictive ability of SECs (ability to estimate toxicity in an independent database) was
evaluated by first calculating SECs using just the Great Lakes (GL) portion of the database (n =
27 samples). We were able to calculate GL SECs primarily for total metals, simultaneously
extracted metals (SEM metals), and PAHs (Appendix 3b). These GL SECs were then used to
predict responses in independent HA28 and CR14 tests with Clark Fork River (CFR) sediments
(n = 15 samples). The CFR sediments contained elevated concentrations of As, Cd, Cu, Pb, and
Zn. Concentrations of PAHs, PCBs, and chlorinated pesticides were not elevated in these
samples (Kemble et al., 1994). In the CFR tests, 7% of the sediments were toxic in the CR14 test
and 53% of the samples were toxic in the HA28 test (Table 1).
Figure 26 plots correct classification of CFR samples as a function of the number of exceedances
of individual GL ERMs which correctly classified >70% of the GL samples. For the CR14 test,
about 80 to 90% of the CFR samples were correctly classified at 1 to 2 exceedances of GL
ERMs. The majority of the samples were not toxic and did not exceed GL ERMs for the CR14
test. Type II error (toxic/no hit) was always <10% and Type I error (not toxic/hit) was 20% at 1
exceedance dropping to <10% with >2 GL ERM exceedances. For the HA28 test, about 70% of
the CFR samples were correctly classified, Type II error was <10%, and Type I error was 20 to
30% at 1 to 2 GL ERM exceedances. Above 2 GL ERM exceedances in the HA28 test, Type II
error increases more than the decrease in Type I error, resulting in a substantial drop in correct
classification of samples. Evaluations using GL PELs and GL NECs resulted in similar
predictive ability compared to GL ERMs for the CR14 and HA28 tests with CFR sediments.
The CFR sediments primarily contained high concentrations of Cu and Zn resulting in
exceedances of GL ERMs for these two metals. Requiring more than 2 exceedances of GL
ERMs resulted in a high Type II error (toxic samples misclassified as not toxic). Hence,
classification based on multiple exceedances of SECs in a preliminary screening of sediments
which contain a limited number of contaminants may result in high Type II error. For example,
Type II error was <10% and Type I error was 10 to 30% at 1 to 2 GL ERM exceedances in both
the CR14 and HA28 tests with CFR sediments, but Type II error was high with multiple
exceedances in the HA28 test (Figure 26). Therefore, a low number of SEC exceedances should
be used to conduct a preliminary screening to predict the potential for toxicity in the absence of
actual toxicity testing. This would minimize the potential for false negatives (i.e., Type II error)
at the risk of accepting higher false positives (i.e., Type I error).
We have included this one example of how the predictive ability of SECs can be evaluated using
an independent data set. We are currently in the process of using our SECs calculated from the
entire database to predict the response ofHyalella azteca and Chironomus riparius in a variety of
independent data sets generated by other laboratories (Appendix 5: Field and Cairncross, 1994;
McGee et al., 1994; Schlekat et al., 1994; Day et al., 1995; Hoke et al., 1995; M.D. Sprenger,
USEPA, Edison, NJ, unpublished data). Data sets described by Pastorok et al. (1994) and Batts
and Cubbage (1995) are also being evaluated.
18
-------
Comparability to Published SECs
Example comparisons are plotted of our SECs relative to other published SECs for
benzo[a]pyrene (BaP; Figure 27 and Appendix 6) and copper (Figure 28 and Appendix 6). Our
SECs are typically lower than the AET (Figure 27 and 28) and EQP values (Figure 27) and are
relatively similar to paired marine ERMs, ERLs, PELs, or TELs and freshwater PELs or TELs
(Figure 27 and 28; Smith et al, 1996). The SECs based on EQP and AET approaches are
typically near the maximum concentration for the particular chemical in our database. This is not
surprising since EQP values represent concentrations of single chemicals predicted to be toxic
whereas the other SECs listed in Figure 27 and 28 represent concentrations of a chemical
associated with toxicity in mixtures of chemicals in field-collected sediments (Hoke et al., 1995).
Smith et al. (1996) reported 14 of their 23 TELs and 15 of their 23 PELs were within a factor of
3 for at least two other published SECs. These results indicate SECs developed using a variety
of approaches and data sets are often comparable. The SECs calculated by Smith et al. (1996)
were also comparable to our SECs listed in Appendix 3 for HA28 tests. However, reliability of
the SECs in Smith et al. (1996) was generally lower than the reliability of our SECs. The
database used by Smith et al. (1996) to calculate SECs included our data and a variety of
additional data sources from North America. This lower reliability of SECs reported by Smith et
al. (1996) resulted from including data for additional species from studies reporting no effects
without matching effect data (i.e., intolerant species or short exposure duration) or by including
data from benthic community surveys (i.e., difficult to compare sediment chemistry to
distributions of benthos). Additional comparisons are ongoing to further evaluate comparability
and predictive ability of published SECs to our SECs using additional independent data sets
(Appendix 5; Pastorok et al., 1994; Batts and Cubbage, 1995).
Ultimately, the best measure of comparability among SECs is not to compare similarity in
absolute concentrations, but to compare how different types of SECs correctly (or incorrectly)
predict toxicity in independent samples. For example, Figure 29 plots predictions of toxicity in
our HA28 tests as a function of exceedances of freshwater PELs (PELF; Smith et al., 1996);
Hyalella azteca AETs (AET5; Batts and Cubbage, 1995; assuming 2% TOC); EQP (USEPA,
1988; Hoke et al., 1995; assuming 2% TOC); and SLCs (SLC1; lowest effect level for Screening
Level Concentrations; Persaud et al., 1992). At 1 to 6 exceedances of these published PELs,
AETs, and EQP values, toxicity is correctly predicted in about 60 to 80% of the samples whereas
SLCs only correctly predict toxicity in about 40 to 60% of the samples. The higher Type I error
(false positives) associated with SLCs compared to the other values results in this lower correct
prediction by SLCs. The PEL, AET, and EQP values correctly predict toxicity in a similar
percentage of samples; however, Type II error (false negatives) is consistently higher with AET
and EQP values compared to either PELs or SLCs. In summary, these analyses indicate
predictive ability is similar between published PEL, AET, and EQP values; however, these PELs
minimize Type I error relative to SLCs and minimize Type II error relative to AET and EQP
values. In addition, the predictive ability of these published SECs is comparable to the reliability
of our SECs listed in Appendix 3.
19
-------
Confirming Causality and Development of Sediment Management Decisions with SECs
Exceeding an SEC for a particular chemical in a field-collect sample does not necessarily mean
the chemical caused the observed effect. Rather, the SEC is the concentration of a chemical that
is associated with the effect. Sediment samples typically contain complex mixtures of
contaminants. Additional information is needed to identify the specific contaminants that were
actually responsible for the toxicity. Confirmation of the cause of sediment toxicity can be
accomplished using sediment spiking or toxicity identification evaluation (TIE) procedures.
Once the probable cause(s) of sediment toxicity has been identified, better decisions can be made
regarding potential remediation options.
Spiking evaluations could be conducted by adding contaminants to a non-toxic sediment (e.g.,
BR-01) or control sediment (USEPA, 1994; ASTM, 1995). This information could be used to
establish dose-response and cause-effect relationships between individual chemicals and adverse
responses. Select metals or organic contaminants could be evaluated individually and in
combination to determine toxic concentrations in sediment. Sediments spiked with
concentrations bracketing various SECs could be used to generate LCSOs or a minimum
concentration at which effects are observed (e.g., low-observable-effect concentration, LOEC).
The LCSOs and LOECs could then be used to determine if the toxicity associated with exceeding
an SEC was caused by contaminants in sediment (Swartz and Di Toro, 1997).
Equilibration and mixing conditions vary widely in sediment spiking studies (ASTM, 1995).
The duration of contact between the chemical and sediment can affect partitioning and
bioavailability of contaminants. Therefore, spiked sediments should be aged long enough to
establish a steady state between contaminants and the various sediment phases. USEPA (1994)
recommends holding spiked samples for at least one month before testing. Furthermore, a range
in sediment TOC, DOC, and AVS could also be evaluated depending on the chemicals(s) under
consideration. Data from sediment spiking tests should be compared to field data on chemical
concentrations in natural sediments and observed effects. This information could be used to
better determine cause-effect relationships between contamination and toxicity. Approaches
such as TIE could also be used to evaluate the cause of acute toxicity of sediment pore-water
samples (Ankley and Thomas, 1992; Ankley et al., 1996). For example, sodium thiosulfate or
EDTA could be used to chelate toxic metals and pH adjustments could be used to evaluate
ammonia toxicity.
SECs generated with laboratory toxicity data should be confirmed relative to the responses
observed in benthic community assessments. Canfield et al. (1994, 1996a,b) used to sediment
quality triad (Triad) to evaluate benthic communities in the Great Lakes, in the Clark Fork River,
Montana and the upper Mississippi River. The Triad approach integrates data from: (1)
laboratory exposures (e.g., sediment toxicity), (2) benthic community structure (e.g., number of
genera), and (3) chemical and physical analyses (e.g., metals, grain size) to provide strong,
complementary evidence for the degree of pollution-induced degradation in aquatic
communities. Good concordance was evident between laboratory toxicity, sediment chemistry,
20
-------
and benthic invertebrate community structure in extremely contaminated samples in our database
(Canfield et al. 1994,1996a,b). However, less concordance was observed between benthos and
either laboratory toxicity or chemistry in the moderately contaminated samples. Laboratory
toxicity tests were better at discriminating chemical concentrations in sediments than the many
commonly used measures of benthic invertebrate community structure likely because benthic
organisms may be responding to factors such as habitat alteration as well as contaminants. We
are in the process of calculating SECs for a variety of benthic indices and plan to evaluate the
reliability, comparability, and predictive ability of these SECs for benthos compared to SECs for
laboratory toxicity tests.
Throughout this report we have evaluated the reliability using the frequency of exceeding
individual SECs. Canfield et al. (1996a,b) and Kemble et al. (1996) evaluated the reliability of
our ERMs using a toxic quotient approach. A toxic quotient was calculated for each sample by
first dividing the concentration of individual chemicals by their respective ERM and then
summing each of these individual values. Figure 30 plots the relationship between the frequency
of ERM exceedances and the sum of the ERM toxic quotient for HA28 samples using all ERMs
regardless of the percent correct classification. The frequency of observed toxicity in samples
increases at either a sum ERM toxic quotient of about 10 to 20 or at a frequency of ERM
exceedances of about 3 to 7. A similar relationship is evident if only individual ERMs are used
that correctly classify >60% or >70% of the samples; however, a lower number of ERM
exceedances or lower sum ERM toxic quotients are needed to consistently estimate observed
toxicity. In summary, either the sum toxic quotient approach or the frequency of SEC
exceedances are equally reliable at classifying samples as either toxic or not toxic in our database
((Canfield et al., 1996a,b; Kemble et al., 1996).
21
-------
Conclusions and Recommendations
ERMs and ERLs are generally as reliable as paired PELs and TELs at classifying samples as
either toxic and not toxic in our database. Reliability of the SECs in terms of correctly
classifying sediment samples is similar between ERMs and NECs; however, ERMs minimize
Type I error (false positives) relative to ERLs and minimize Type II error (false negatives)
relative to NECs. ERMs and NECs rather than ERLs should be used to predict toxicity of
samples due to the lower Type I error associated with them. However, ERLs can be used to
efficiently identify concentrations below which toxicity is rarely observed. Correct classification
of samples can be improved by using only the most reliable individual ERMs or NECs for
chemicals (i.e., those with a higher percentage of correct classification). When SECs are used to
conduct a preliminary screening to predict the potential for toxicity in the absence of actual
toxicity testing, a low number of SEC exceedances should be used to minimize the potential for
false negatives (i.e., Type II error); however, the risk of accepting higher false positives (i.e.,
Type I error) is increased.
Calculating SECs using dry-weight concentrations or using sediment concentrations normalized
to TOC concentrations for PAHs and total PCBs resulted in similar correct classification of
toxicity and similar Type I and Type II errors. The range of TOC concentrations in our database
was relatively narrow compared to the ranges of contaminant concentrations. Therefore,
normalizing dry-weight concentrations to a relatively narrow range of TOC concentrations had
little influence on relative concentrations of contaminants among samples.
SECs generated using data from field-collected samples should not be used independently to
establish trigger levels for clean up of sediments. The strength of SECs developed using data
from tests with field-collected sediments is in their use in predicting the potential for toxicity in
independent field-collected sediment samples. A primary use of SECs developed with field-
collected sediments should be to provide guidance for determining sites which may require
further investigation. The ability of any SEC or sediment toxicity test to predict benthic
community effects should be considered before either of these approaches are used to routinely
evaluate sediment quality.
Our SECs were calculated from toxicity tests with field-collected samples. If a chemical
concentration exceeds an SEC generated using data from these tests with field-collected samples,
it does not necessarily mean the chemical caused the observed effect. Rather, the SEC is the
concentration of a chemical that is associated with the effect. Field-collected sediments typically
contain complex mixtures of contaminants. Additional information is needed to identify the
specific contaminants that were actually responsible for the toxicity. Confirmation of sediment
toxicity due to individual or groups of contaminants or the interactive effects of sediment
toxicants can be evaluated by using TIE procedures or by conducting toxicity tests with
chemicals spiked into sediments. Once the probable cause(s) of sediment toxicity has been
identified, better decisions can be made regarding remediation options.
22
-------
Ideally, multiple approaches should be used to develop SECs and evaluate sediment quality. An
integration of methods using a weight of evidence is the most desirable approach for assessing or
confirming effects of contaminants associated with sediment. Sediment evaluations integrating
data from laboratory exposures, chemical analyses, and benthic community assessments (the
Sediment Quality Triad) provide strong complementary evidence of the degree of pollution-
induced degradation in aquatic communities.
23
-------
References
American Society for Testing and Materials. 1995. Standard test methods for measuring the
toxicity of sediment-associated contaminants with freshwater invertebrates. E1706-95b. In
Annual Book of Standards, Vol. 11.05, Philadelphia, PA.
Ankley, G. and Thomas, N. 1992. Interstitial water toxicity identification evaluation approach. In
Sediment classification methods compendium, pp. 5-1 to 5-14. EPA 823-R-92-006, Washington,
DC.
Ankley, G.T., Schubauer-Berigan, M.K., and Dierkes, J.R. 1996. Application of toxicity
identification evaluation techniques to pore water from Buffalo River sediments. J. Great Lakes
Research: In press.
Barrick, R., Becker, S., Brown, L., Seller, H., and Pastorok, R. 1988. Sediment quality values
refinement: 1988 Update and Evaluation of Puget Sound AET, Vol. I. PTI Contract C717-01,
PTI Environmental Services, Bellevue, WA.
Batts, D. and Cubbage, J. 1995. Summary guidelines for contaminated freshwater sediments.
Washington Department of Ecology, publication no. 95-308, Olympia, WA.
Becker, D.S., Barrick, R.C., and Read, L.B. 1989. Evaluation of the AET approach for assessing
contamination in sediments in California. PTI Contract C739-01, PTI Environmental Services,
Bellevue, WA.
Burton, G.A., Ingersoll, C.G., Burnett, L., Henry, H., Hinman, M., Klaine, S., Landrum, P., and
Ross, P. 1996. A comparison of sediment toxicity test methods at three Great Lakes Areas of
Concern. J. Great Lakes Research: In press.
Canadian Council of Ministers of the Environment. 1995. Protocol for the derivation of
Canadian sediment quality guidelines for the protection of aquatic life. Prepared by the CCME
Task Group on water quality guidelines, Ottawa, ON.
Canfield, T.J., Kemble, N.E., Brumbaugh, W.G., Dwyer, F.J., Ingersoll, C.G., and Fairchild, J.F.
1994. Use of benthic invertebrate community structure and the sediment quality triad to evaluate
metal-contaminated sediment in the upper Clark Fork River, Montana. Environ. Toxicol. Chem.
13:1999-2012.
Canfield, T.J., Dwyer, F.J., Fairchild, J.F., Ingersoll, C.G., Kemble, N.E., Mount, D.R., La Point,
T.W., Burton, G.A., and Swift, M.C. 1996a. Assessing contamination of Great Lakes sediment
using benthic invertebrates and the sediment quality triad approach. J. Great Lakes Research: In
press.
24
-------
Canfield, T.J., E.L. Brunson, F.J. Dwyer, C.G. Ingersoll, and N.E. Kemble. 1996b. Assessing
upper Mississippi river sediments using benthic invertebrates and the sediment quality triad.
Manuscript in review.
Day, K.E., Dutka, B.J., Kwan, K.K., Batista, N., Reynoldson, T.B., and Metcalfe-Smith, J.L.
1995. Correlations between solid-phase microbial screening assays, whole-sediment toxicity tests
with macroinvertebrates and in situ benthic community structure. J. Great Lakes Research:
21:192-206.
Di Toro, D.M., Mahony, J.H., Hansen, D.J., Scott, K.J., Hicks, M.B., Mayr, S.M., and Redmond,
M. 1990. Toxicity of cadmium in sediments: The role of acid volatile sulfides. Environ. Toxicol.
Chem. 9:1487-1502.
Di Toro, D.M., Zarba, C.S., Hansen, D.J., Berry, W.J., Swartz, R.C., Cowan, C.E., Pavlou, S.P.,
Allen, H.E., Thomas, N.A., and Paquin, P.R. 1991. Technical basis for establishing sediment
quality criteria for nonionic organic chemicals using equilibrium partitioning. Environ. Toxicol.
Chem. 10:1541-1583.
Field, L.J. and Cairncross, C.S. 1994. A sediment toxicity database for Superfund: EPA Region
III pilot project, for EPA/Office of Health and Environmental Assessment, Office of Research
and Development, Washington, DC, April 1994. 20 p. + appendices.
Fox, R.G. 1996. An overview of the Assessment and Remediation of Contaminated Sediments
(ARCS) project. J. Great Lakes Research: In press.
Hall, N.E., Fairchild, J.F., La Point, T.W., Heine, P.R., Ruessler, D.S., and Ingersoll, C.G. 1996.
Problems and recommendations in using algal toxicity testing to evaluate contaminated
sediments. J. Great Lakes Research: In press.
Hoke, R.A., Ankley, G.T., and Peters, J.F. 1995. Use of a freshwater sediment quality database
in an evaluation of sediment quality criteria based on equilibrium partitioning and screening-
level concentrations. Environ. Toxicol. Chem. 14:451-459.
Ingersoll, C.G. and Nelson, M.K. 1990. Testing sediment toxicity with Hyalella azteca
(Amphipoda) and Chironomus riparius (Diptera). In Aquatic Toxicology and Risk Assessment:
Thirteenth Volume, ASTM STP 1096, eds. W.G. Landis and W.H. van der Schalie, pp. 93-109.
American Society for Testing and Materials, Philadelphia, PA.
Ingersoll, C.G., Haverland, P.S., Brunson, E.L., Canfield, T.J., Dwyer, F.J., Henke, C.E.,
Kemble, N.E., Mount, D.R., and Fox, R.G. 1996. Calculation and evaluation of sediment effect
concentrations for the amphipod Hyalella azteca and the midge Chironomus riparius. J. Great
Lakes Research: In press.
25
-------
Kemble, N.E., Brumbaugh, W.G., Brunson, E.L., Dwyer, F.J., Ingersoll, C.G., Monda, D.P., and
Woodward, D.F. 1994. Toxicity of metal-contaminated sediments from the upper Clark Fork
River, Montana to aquatic invertebrates in laboratory exposures. Environ. Toxicol. Chem.
13:1985-1997.
Kemble, N.E., E.L. Brunson, T.J. Canfield, F.J. Dwyer, and C.G. Ingersoll. 1996. Laboratory
toxicity test with Hyalella azteca exposed to whole sediments from the Upper Mississippi River.
Manuscript in review.
Lamberson, J.O. and Swartz, R.C. 1992. Spiked-sediment toxicity test approach. In Sediment
classification methods compendium, pp. 4-1 to 4-10. EPA 823-R92-006, Washington, DC.
Long, E.R. and Morgan, L.G. 1991. The potential for biological effects of sediment-sorbed
contaminants tested in the National Status and Trends Program. NOAA Technical
Memorandum NOS OMA 52, Seattle, WA.
Long, E.R., MacDonald, D.D., Smith, S.L., and Calder, F.D. 1995. Incidence of adverse
biological effects within ranges of chemical concentrations in marine and estuarine sediments.
Environmental Management 19:81-97.
Lorenzato, S.G., Gunther, A.J., and O'Conner, J.M. 1991. Summary of a workshop concerning
sediment quality assessment and development of sediment quality objectives, 32 p. California
State Water Resources Control Board, Sacramento, CA.
MacDonald, D.D. 1994. Approach to the assessment of sediment quality of Florida coastal
waters. Volume 1 - Development and evaluation of sediment quality assessment guidelines, 126
p. Report prepared for the Florida Department of Environmental Protection, Tallahassee, FL.
November 1994.
MacDonald, D.D., Carr, R.S., Calder, F.D., Long, E.R., and Ingersoll, C.G. 1995. Development
and evaluation of sediment quality guidelines for Florida coastal waters. Ecotoxicology: In press.
McGee, B.L., Schlekat, C.E., Boward, D.M., and Wade, T.L. 1994. Sediment contamination and
biological effects in a Chesapeake Bay marina. Ecotoxicology 4: 39-59.
Papoulias, D.M. and Buckler, D.R. 1996. Mutagenicity of Great Lakes sediments. J. Great Lakes
Research: In press.
Papoulias, D.M., Buckler, D.R., and Tillitt, D.E. 1996. Optimization of the Ames/Salmonella
mutagenicity assay for use with extracts of aquatic sediments. J. Great Lakes Research: In press.
Pastorok, R.A., Peek, D.C., Sampson, J.R., and Jacobson, M.A. 1994. Ecological risk assessment
for river sediments contaminated by creosote. Environ. Toxicol. Chem. 13:1929-1941.
26
-------
Persaud, D., Jaagaumagi, R., and Hayton, A. 1992. Guidelines for the protection and
management of aquatic sediment quality in Ontario. ISBN 0-7729-9248-7. Ontario Ministry of
the Environment, Water Resources Branch, Toronto, ON.
Roach, R.W., Carr, R.S., Howard, C.L., and Cain, D.W. 1993. Assessment of produced water
impacts in Galveston Bay System. U.S. Fish and Wildlife Report, Clear Lake Ecological Services
Office, Houston, TX.
Ross, P.E., Burton, G.A. Jr., Crecelius, E.A., Filkins, J.C., Giesy, J.P. Jr., Ingersoll, C.G.,
Landrum, P.P., Mac, M.J., Murphy, T.J., Rathbun, J.E., Smith, V.E., Tatem, H., and Taylor,
R.W. 1992. Assessment of sediment contamination at Great Lakes areas of concern: The ARCS
program. J. Aquat. Ecosystem Health 1:193-200.
Schlekat, C.E., McGee, B.L., Boward, D.M., Reinharz, E., Velinsky, D.J., and Wade, T.L. 1994.
Tidal river sediments in the Washington, D.C. area. III. Biological effects associated with
sediment contamination. Estuaries 17:334-344.
Smith, S.L., MacDonald, D.D., Kennleyside, K.A., Ingersoll, C.G., and Field, J. 1996. A
preliminary evaluation of sediment quality assessment values for freshwater ecosystems. J.
Great Lakes Research: In press.
Statistical Analysis Systems. 1992. SAS Users Guide. Gary, SC: SAS Institute, Inc.
Swartz, R.C. and Di Toro, D.M. 1997. Sediments as completex mixtures: An overview of
methods to assess ecotoxicological significance. Chapter 16 in Ecological Risk Assessments of
Contaminated Sediments. G.R. Biddinger, T. Dillon, and C.G. Ingersoll (eds.). SETAC Press,
Pensacola, FL. In press.
U.S. Environmental Protection Agency. 1988. Interim sediment criteria values for nonpolar
hydrophobic organic contaminants. EPA, SDC #17, Criteria and Standards Division,
Washington, DC.
U.S. Environmental Protection Agency. 1992. Sediment classification methods compendium.
EPA 823-R92-006, Washington, DC.
U.S. Environmental Protection Agency. 1993. Assessment and remediation of contaminated
sediments (ARCS) program. Biological and chemical assessment of contaminated Great Lakes
sediment. EPA 905-R93-006, Chicago, IL.
U.S. Environmental Protection Agency. 1994. Methods for measuring the toxicity and
bioaccumulation of sediment-associated contaminants with freshwater invertebrates. EPA 600-
R24-024, Duluth, MN.
27
-------
Wildhaber, M.L. and Schmitt, C.J. 1996. Hazard ranking of contaminated sediments based on
chemical analysis, laboratory toxicity tests, and benthic community composition: Prioritizing
sites for remedial action. J. Great Lakes Research: In press.
28
-------
Table 1. Percentage of whole-sediment samples identified as toxic in Chironomus riparius
14-d (CR14), Hyalella azteca 14-d (HAH), or H. azteca 28-d (HA28) tests.
TOXIC1 TQXIC-S2 TOXIC-G3 TOXIC-M4
All samples
CR14 26(42) 24(42) 9(34) ND
HAH 41(32) 25(32) 20(25) 24(21)
HA28 39(62) 26(62) 34(44) 11(36)
Great Lakes
CR14 37(27) 33(27) 11(19) ND
HAH 48(27) 30(27) 20(25) 24(21)
HA28 48(27) 41(27) 24(25) 5(21)
Upper Mississippi River
HA28 0(5) 0(5) ND ND
Clark Fork River
CR14 7(15) 7(15) 7(15) ND
HA28 53(15) 13(15) 53(15) 20(15)
Trinity River
HAH 0(5) 0(5) ND ND
HA28 0(5) 0(5) ND ND
Mobile Bay
HA28 0(5) 0(5) ND ND
Galveston Bay
HA28 60(5) 60(4) 25(4) ND
'TOXIC: Significant reduction in survival, growth, or maturation
relative to the control (p<0.05, N in parentheses)
2TOXIC-S: Significant reduction in survival
3TOXIC-G: Significant reduction in growth
"TOXIC-M: Significant reduction hi maturation (H. azteca only)
5ND: Not determined
29
-------
Table 2. Percentage of paired tests or paired endpoints identifying samples as toxic in
Chironomus riparius 14-d (CR14), Hyalella azteca 14-d (HAH), or H. azteca 28-d
(HA28) tests. A designation of "-S" represents survival, "-G" represents growth, and a
row without an "-S" or a "-G" represents survival or growth endpoints for those tests.
TOX/TOX1 NOT/NOT2 TOX/NOT3 NOT/TOX4 N5
CR14/HA28
CR14-S/HA28-S
CR14-G/HA28-G
HA14/HA28
HA14-S/HA28-S
HA14-G/HA28-G
HA14/CR14
HA14-S/CR14-S
HA14-G/CR14-G
CR14-S/CR14-G
HA14-S/HA14-G
HA28-S/HA28-G
24
19
9
34
25
8
37
26
5
6
4
16
48
64
62
53
66
64
52
63
68
85
60
52
2
5
0
6
0
12
11
4
21
6
20
14
26
12
29
6
10
16
0
7
5
3
16
18
42
42
34
32
32
25
27
27
19
34
25
44
'TOX/TOX:
'NOT/NOT:
3TOX/NOT:
4NOT/TOX:
5N:
Samples toxic (significant reduction relative to the control p<0.05) with both
endpoints or tests
Samples not toxic with both endpoints or tests
Samples toxic to the first but not the second endpoint or test
Samples not toxic to the first but toxic to the second endpoint or test
Number of samples
30
-------
FIGURES
For Figures 1 through 20:
1. Comparability was evaluated by plotting the ratio of concentrations of paired SECs (for
example in Figure la: plots the ratio of paired ERM-Gs to ERMs; an asterisk indicates
one or more ratios greater 2.4).
2. Reliability was evaluated by plotting the ability of paired SECs to: (1) correctly
classify sediment samples (e.g., ERM-Gs to ERMs; Figure Ib), (2) incorrect classify
non-toxic samples as toxic (Type I error; e.g., Figure Ic), and (3) incorrectly classify
toxic samples as not toxic (Type II error; e.g., Figure Id).
3. The solid lines (e.g., Figure Ib to Id for ERM vs ERM-G) are lines of unity and the
dashed lines are ±20% of unity. In Figure Ib to d: (1) ERM=ERM-G if the paired
comparison is within +20% of unity; (2) ERM>ERM-G if the paired comparison is
>20% of unity; and (3) ERM
-------
ERM /ERM-G
FIGURE 1A: ENTIRE DATABASE VS GREAT LAKES DATABASE
BY
N- 25
ERM-Q
0(0%)
0.0 02 M 0.6 0.8 1.0 12 14 1.6 U 2.0 12
TEST-HAM
«- 2T
EflMERM-G
17 (KS)
4414441 4 44
3 3
1 1
• (22%)
4
3) 3
1 1
4(1«)
33 3
1
0.0 0.2 0.4 0.6 0.8 1.0
ERM /ERM-G
FIGURE IB: ENTIRE DATABASE VS GREAT LAKES DATABASE
100
90
M
70
60
50
40
30
20
10
0
N= 25
—r—i— i l • i
0 10 20 30 40 50 60 70 80 90 100
ERM
TEST-HAM
100
to
to
70
60
50
40
30
20
10
0-
N- 27
100
90
80
70
60
50
40
30
20
10
0
-r—'—r—'—r
—1 1 J • 1 r—, , , 1 f
0 1020304050607080M100
ERM
TEST=HA28
N= 27
0 1020304050M70MW
ERM
Figures 1a and 1b. Comparability and reliability of ERMs calculated using the Great Lakes database (ERM-G) vs ERMs calculated using dry-weight concentrations and the entire database (ERM). See the
page proceeding Figure 1 in the report for additional detail.
-------
ERM /ERM-G
FIGURE 1C: ENTIRE DATABASE VS GREAT LAKES DATABASE
ERM /ERM-G
FIGURE 1D: ENTIRE DATABASE VS GREAT LAKES DATABASE
0 10 20 30 40 50 60 70 80 90 100
ERM
TEST-HAM
0 10 20 30 40 50 M 70 N M 100
ERM
TEST-HAM
100
90
60
70
60
*°
40
30
20
10
0
100
90
M
70
60
»
40
30
20
10
0
N= 25
—i—•—i—'—i—'—i—•—i—•—i—•—i—•—i—'—i—•r
0 10 20 30 40 50 60 70 60 90 100
ERM
TEST-HAM
N-27
'i ' i '—[—•—i——i • i '—r"1—i ' i ' i '—r
0 10 20 30 40 50 60 70 N W 100
ERM
TEST-HA2«
I* I17 ' I ' I ' I ' I ' I
0 10203040M60708080100
ERM
100
M
60
70
60
»
40
30
20
10
0
N= 27
44
l l ' I ' I ' l i I ' I ' I
0 10JOM40506070M90WO
ERM
Figures 1c and 1d. Comparability and reliability of ERMs calculated using the Great Lakes database (ERM-G) vs ERMs calculated using dry-weight concentrations and the entire database (ERM). See the
page proceeding Figure 1 in the report for additional detail.
-------
PEL / PEL-G
FIGURE 2A: ENTIRE DATABASE VS GREAT LAKES DATABASE
PEL / PEL-G
FIGURE 2B: ENTIRE DATABASE VS GREAT LAKES DATABASE
N= 25
444444
•wr
4 4«
1 3 33
11
3 3
1
i . , i i i , . ,.,.11 i
0.0 02 04 0.6 0.« 1.0 U 1.4 1.6 U 2.0 22 2A
TEST-HA14
N= 27
.-Q
-0
3 31
1111
• • • i
0.0 oa M 0.8 fl.«
i •
M 1.6 U M 11 2-4
TEST-HA2S
N- 27
•W"
441 * 4414
3
^-i — i — i 't i T' t "T-r i "i i i"i ' i i "i — i~i
w-a
4
3 33 3
1 1 1
•war*
I 3 3
1 1
100
90
80
70
60
50
40
30
20
10
0
H=25
0 10 20 30 40 SO M 70 80 90 100
pa
TEST=HA14
100
90
eo
70
60
50
40
30
20
10
0
N= 27
0 102030406060708090
pa
TEST=HA2B
100
90
SO
70
60
(0
40
30
20
10
0
N- 27
0.0 0.2 0.4 0.6 0.6 1.0 U 1.4 1.6 U 2.0 22 U
'i i i i i i i i i i i i i i i ' i ' i i—r
0 10203040506070M90100
Figures 2a and 2b. Comparability and reliability of PELs calculated using the Great Lakes database (PEL-G) vs PELs calculated using dry-weight concentrations and the entire database (PEL). See the
page proceeding Figure 1 in the report for additional detail.
-------
PEL / PEL-G
FIGURE 2C: ENTIRE DATABASE VS GREAT LAKES DATABASE
TEST«CR14
PEL / PEL-G
FIGURE 2D: ENTIRE DATABASE VS GREAT LAKES DATABASE
ueu
100
90
80
70
60
50
40
30
20
10
0
N= 25
0 10 20 30 40 60 60 70 80 90 WO
PEL
TEST-HAM
100
90
BO
70
60
60
40
30
20
10
0
N«25
0 10 20 30 40 60 60 70
PEL
TEST=HAH
H WO
0 10 20 30 40 SO 60 70 10 H 100
i i i ' i i i ' I ' I ' i ' I
0 10 20 M 40 60 60 70 W 90 100
pa
100
90
W
70
60
50
40
30
20
10
0
N- 27
0 tt 20 30 40 50 60 70 80 90 100
PEL
TEST-HA28
100-j
90
80
70
60
50
40
30
20
10
0
N- 27
I'l'—T"1—I i I ' I ' I • I ' I • I ' I
0 10 20 30 40 50 60 70 80 90 100
PEL
Figures 2c and 2d. Comparability and reliability of PELs calculated using the Great Lakes database (PEL-G) vs PELs calculated using dry-weight concentrations and the entire database (PEL). See the
page proceeding Figure 1 in the report for additional detail.
-------
ERL / ERL-G
FIGURE 3A: ENTIRE DATABASE VS GREAT LAKES DATABASE
BY
mow
N= 25
,S«L-0
4 444 44M 4 4
333
3 3
1 111
' i . i c t i i . i ] i i i i | i i l i | . i i i | i ' ' ' I ' ' ' ' I ' ' ' ' I ' ' i ' I ' ' ' ' I
0.0 02 OA 0.6 O.B 1.0 U M 1.6 1.6 2.0 2.2 24
ERL / ERL-G
FIGURE 3B: ENTIRE DATABASE VS GREAT LAKES DATABASE
100
90
M
70
60
50
40
30
20
10
N= 25
1—'—l—'—i—•—l—•—i—'—i—'—i—'—i—>—i—•—i—•—r
0 10 20 30 40 60 60 70 80 M MO
ERL
TEST=HM«
N= 27
0 102030405060 70 MM 100
ERL
TEST=HA2«
100
M
80
70
60
SO
40
30
20
10
0
N-Z7
0 10203040S0607060M100
ERL
Figures 3a and 3b. Comparability and reliability of ERLs calculated using the Great Lakes database (ERL-G) vs ERLs calculated using dry-weight concentrations and the entire database (ERL). See the
page proceeding Figure 1 in the report for additional detail.
-------
ERL / ERL-G
FIGURE 3C: ENTIRE DATABASE VS GREAT LAKES DATABASE
I —i ' i ' i ' i ' i ' i ' r
0 10 JO 30 40 50 M 70 80 90 100
ERL
TEST-HA28
100
90
80
70
60
CO
40
30
20
10
0
N= 27
I I I I I I I ' I ' I ' I ' I ' I ' I
0 W203040SOW708090100
ERL
ERL / ERL-G
FIGURE 3D: ENTIRE DATABASE VS GREAT UKES DATABASE
0 10 20 30 40 50 60 70 80 90 tOO
ERL
TEST-HM4
0 10 20 30 40 50 N 70 N 90 100
Figures 3c and 3d. Comparability and reliability of ERLs calculated using the Great Lakes database (ERL-G) vs ERLs calculated using dry-weight concentrations and the entire database (ERL). See the
page proceeding Figure 1 in the report for additional detail.
-------
TEL / TEL-G
FIGURE 4A: ENTIRE DATABASE VS GREAT LAKES DATABASE
BY<
TEL / TEL-G
FIGURE 4B: ENTIRE DATABASE VS GREAT LAKES DATABASE
N= 25
.-0
444 4M64
TEL-TEL-Q TEL>TEL-G
I (24%) 4 (I6*T
3 33
1 t 1
33 3
1
• l i i i i i i i i i i • i •• i i • i i i i • i i i • i i i i • i ' i i i • i • i i • i • i
0.« 0.8 1.0 « 1.4 1.6 U 2.0 22 2.4
TEST-HA14
100
M
W
70
0 M
' M
g 40
30
20
10
0
N=2S
0 10 20 30 40
70 tO M 100
TEL
TEST=HA14
N= 27
TELTEL-fi
1(3%)
44*441444
33 3 33
H 1 1
i l 'l i i . . i i . . i i
M (L2 M O.B 0.» 1.0 « 1.4 1.6 U 2.0 23
100
90
60
70
60
50
40
30
20
10
0
N-27
I ' I ' I ' I ' I ' I ' I ' I ' I ' I
0 W 20 30 40 SO 60 70 60 90 100
TEL
Figures 4a and 4b. Comparability and reliability of TELs calculated using the Great Lakes database (TEL-G) vs TELs calculated using dry-weight concentrations and the entire database (TEL). See the
page proceeding Figure 1 in the report for additional detail.
-------
TEL / TEL-G
FIGURE 4C: ENTIRE DATABASE VS GREAT LAKES DATABASE
TE5T=CRM
IN
90
60
70
60
50
40
30
20
10
0
N-25
0 10 20 30 « 50 60 70 60 90 100
TEL
TEST-HAH
100
90
80
70
to
SO
40
30
20
10
0
N= 27
0 102030405060 70 6090 100
TO.
TEST=HA28
100
90
80
70
00
80
40
30
20
10
0
N- 27
i i i ' i ' i ' I ' I ' i ' I ' I ' I
0 10 20 30 40 60 00 70 80 90 100
TEL
TEL / TEL-G
FIGURE 4D: ENTIRE DATABASE VS GREAT LAKES DATABASE
100
90
60
70
60
50
40
30
20
10
0
N= 25
0 102030405060706090100
TEL
TEST=H*14
0 102030405060706090100
-i—>—i i i ' I '—I ' I ' I ' I ' I
0102030405060706090100
TEL
Figures 4c and 4d. Comparability and reliability of TELs calculated using the Great Lakes database (TEL-G) vs TELs calculated using dry-weight concentrations and the entire database (TEL). See the
page proceeding Figure 1 in the report for additional detail.
-------
NEC / NEC-G
FIGURE 5A: ENTIRE DATABASE VS GREAT LAKES DATABASE
BY CQNCBngATION
N= 25
NEC
-------
NEC / NEC-G
FIGURE SC: ENTIRE DATABASE VS GREAT LAKES DATABASE
100
90
80
70
60
50
40
30
20
10
0
100
90
80
70
60
50
40
30
20
10
0
N= 25
' i ' i ' i ' i ' i ' i '—r
0 10 20 30 40 M 60 70 80 90 100
NEC
TEST-HAU
N= 27
0 102030406060 70 8090 100
NEC
TEST-HA28
100
90
80
70
60
SO
40
30
20
10
0
N= 27
0 102030405080708090100
NEC
NEC / NEC-G
FIGURE 5D: ENTIRE DATABASE VS GREAT LAKES DATABASE
iw
90
80
70
CO
50
40
30
20
10
0
N= 25
0 102030405060708000100
NEC
TEST=HAH
100
90
80
70
60
50
40
30
20
10
0
N- 27
0 10 20 30 40 50 60 70 80 90 100
NEC
TEST=HA28
100
90
80
70
60
50
40
30
20
10
0
N- 27
i ' i '—t—'—i i i i—i ' i ' l ' l ' l ' l
0 10 20 30 40 50 60 70 80 90 WO
NEC
Figures 5c and 5d. Comparability and reliability of NECs calculated using the Great Lakes database (NEC-G) vs NECs calculated using dry-weight concentrations and the entire database (NEC). See the
page proceeding Figure 1 in the report for additional detail.
-------
ERL / TEL
FIGURE 7C: % TYPE I
TEST=CR14
ERL / TEL
FIGURE 7D: % TYPE II
100
90
M
TO
60
60
40
30
20
10
0
100
N= 26
i I i I • I ' I • I ' I ' I • ' • ' ' T
0 10MM4050M7080MWO
ERL
TEST=HA14
30406060 70 M90MO
TEST=CB1«
100
0 10 20 M 40 60 M 70 80 90 100
0 W20304060M70MW100
i i i i i i—r ' i ' I ' I ' I
0 » 20 30 40 50 60 70 «0 M 100
ERL
Figures 7c and 7d. Comparability and reliability of ERLs and TELs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
ERM / ERL
FIGURE 8A: BY CONCENTRATION
TCST-CR14
N— 2A
Wl
ERM-ERL
2(7%)
1
1
v»
t
33 3 3 '
1 1 1
i i • i i -t i r i i — i i T i i i — i I 11 — I — TT — r— I — I — I — I — i — " — " — T
0.0 02 M 0.1 0.1 1.0 « M 1.1 1.8 10 2.2 2.4
TEST=HA14
N- 27
EflMCT1.
0 (0%f 2 (7%) 25 (92*f
1
llll — l !• r- l — l—l —
4 444 4 4
3 •
1 •
1 — I 1 1 1 I 1 I — I"T I I"l 1111 r— 1 1 1—1 1 1 I I I r~< >' T
0.0 02 0.4 0.6 0.8 1.0 12 M 1.6 U 2.0 2.2 M
TEST-HA28
N- 33
ERMERL
0(W)
33(100%)
*
4 4
3 33 3 •
1 1
ERM / ERL
FIGURE 8B: % CORRECT
TEST-CRI4
100
90
80
70
N= 26
0 102030405060708090100
ERH
TE8T=HA14
100
90
80
70
60
50
40
30
20
10
0
N- 27
100
90
80
70
60
60
40
30
20
10
o
I I I—I—I ' I '—I ' I • I ' I ' I ' I ' I
0 102030405060708090100
ERM
TEST=HA28
N= 33
0.0 02 OA t* 0» 1.0 1.2 U 1.6 1.8 2.0 22 2.4
I i I i i i i ' i ' i ' I ' i ' I ' i ' i
0 102030406060708090100
ERM
Figures 8a and 8b. Comparability and reliability of ERMs and ERLs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
ERM / ERL
FIGURE 8C: % TYPE I
TE8T-CR14
0 10 20 30
70 80 W 100
ERM / ERL
FIGURE 80: % TYPE II
T£ST=CR14
100
90
M
70
60
50
30
20
10
0
N=26
0 M 20 30 40 50 60 70 90 90
ERM
TCST=HM4
100
90
to
70
60
50
40
30
20
10-
0
N-27
0 10 20 30 40 50 60 70 80 90 100
ERM
TEST-HA28
100
90
M
70
60
rf M
E «.
N= 33
ERM
0 10 20 30 40 50 M 70 80 90 100
ERM
Figures 8c and 8d. Comparability and reliability of ERMs and ERLs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
PEL / TEL
FIGURE 9A: BY CONCENTRATION
TEST-CR14
33
1 1
• i ' ' ' ' i ' ' ' ' i ' ' ' ' i ' ' ' ' i | i i i i i i . . . i i i i . i
0.2 04 0.6 0.6 1.0 1.2 1.4 1.6 1.1 2.0 12 2.4
TKT-HA14
N= 27
0.0 02 0.4 0.6 0.8 1.0 U 1.4 1.6 U 2.0 2.2 2.4
TEST-HA28
N- 33
3 3
3 3
11
1 i ' ' ' '
0.0 02 OA 0.6 0.8 1.0 « 1.4 tt M 2.0 13.
PEL / TEL
FIGURE 9B: % CORRECT
TEST=CR14
100
90
80
70
80
50
40
30
20
10
0
'I i I '—I I i I ' I ' I ' I ' T
0 W 20 30 40 50 60 70 80 90 100
pa
TEST-HA14
100
90
BO
70
M
50
40
30
20
10
0
N- 27
100
90
to
70
«
50
40
30
20
10
0
i i i ' i
0 102030405060708090100
PEL
TEST-HA28
N- 33
i ' i ' i i l ' I ' l ' I
0 10 20 30 40 50 N 70 80 90 100
PEL
Figures 9a and 9b. Comparability and reliability of PELs and TELs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
PEL / TEL
FIGURE 9C: % TYPE I
TEST-CRM
100
90
80
70
N» 26
0 10 20 30 40 50 60 70 80 00 100
PEL
TEST-HAW
— i
0 10203040S0607080MHO
pa
TEST=HA2»
I i I i I i I | I ' I ' I ' I ' I
0 1020304050607060W100
pa
PEL / TEL
FIGURE 9D: % TYPE II
TEST=CR14
0 102030405060 70 N90 100
PEL
TKT^HAU
102030405060701090100
Figures 9c and 9d. Comparability and reliability of PELs and TELs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
NEC / ERM
FIGURE 10A: BY CONCENTRATION
TEST=CR14
N- 26
444
4 4
3
i — 1111 — r-r-i-f r-
4 44
3 3
1 1
0.0 W 0.4 M 0* 1.0 « 1.4 1.« 1.1 2.0 U M
TEST-HAM
N' 27
NEC < ERM
12 (44%)
44 44
3333 i
1 1
NEC-EDU
8(29%)
441 4 4
1
w
4 4
3 3
1
0.0 02 M 0.8 0.8 1.0 U U
TEST=HA28
« "
N= 33
5
3
3W
3 3
1
28(84%)
4 •
33 » 3*
1 1 11
0.0 0.2 M
M a8 1.0 « M M « "
NEC / ERM
FIGURE 10B: % CORRECT
TEST=CH14
100
90
80
70
80
SO
40
30
20
10
0
N=28
0 10 20 30 40 50 60 70 80 90 100
NEC
TEST-HAM
100
90
80
70
N= 27
0 10 20 30 40 50 60 70 80 90 100
NEC
TEST=HA28
100
90
80
70
60
SO
40
30
20
10
N- 33
i ' i ' I i i ' i ' i
0 102030405060706090100
NEC
Figures 10aand 10b.
Comparability and reliability of NECs and ERMs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for
additional detail.
-------
NEC / ERM
FIGURE 10C: % TYPE
TEST=CRM
100
90
M
70
60
SO
40
30
20
10
0
N-26
102030405060706090100
NEC
TEST-HAH
V ' l ' I i I ' I ' I ' I ' I
0 102030405060706090100
NEC
NEC / ERM
FIGURE 10D: % TYPE II
TEST=CR14
100
M
10
70
60
50
40
30
20
10
0
N= 26
0 10 M 30 40 50 60 70 BO 90 100
NEC
TEST=HAI4
100
90
M
70
60
S 50
5 40
30
20
10
0
N- 27
'0 80 90 100
-I—i—| i | i i i i i i • i • i • i i i
0 10203040S06070MM100
NEC
Figures 10cand 10d.
Comparability and reliability of NECs and ERMs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for
additional detail.
-------
NEC / ERL
FIGURE 11A: BY CONCENTRATION
TESr-=CR14
NEC / ERL
FIGURE 11B: % CORRECT
TEST=CR14
N= 26
I ' ' ' i I ' ' i i i i i i i i i i i • i i i i i i •• I i i i i i ! i i i i ! i i i i i
0.0 05 0.4 0.6 0.1 1.0 U U 1.6 U 2.0 2.2 2.4
TEST-HAH
100
90
N
70
60
»
40
30
20
10
0
N=26
i ..... i ' i
i ' i ' — i ' i ' i ' i
0 10 20 30 40 50 60 70 60 90 100
NEC
TEST=HA14
N- 27
WL
Wl
3 3
I— i — i— i — r— I— i — i—i — i— i
TO
4 44'
33 3
11 1 •
0.0 0.2 04 0.6 0.1 10 U M W « 2.0 2* 2.4
TEST-HAM
100
90
60
70
60
50
40
30
20
10
0
N= 27
0 10 20 30 40 50 60 70 60 90 100
NEC
TEST-HA28
N- 33
NEC < ERL
0(0%)
ftr
• 1 1 1 1 1 1 1 1 1
TO
*
*
33 3 *
1 *
0.0 0.2 04 0.6 0.8 W U 14 « IB 2.0
24
100
90
60
70
N- 33
I i i '—i i i i i ' I ' I ' I ' I ' I ' I
0 102030+05060706090100
NEC
Figures 11aand 11b.
Comparability and reliability of NECs and ERLs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for
additional detail.
-------
NEC / ERL
FIGURE 11C: % TYPE I
TEST-CH14
0 10 20 30 40 50 60 70 90 90 100
NEC
TEST-HAM
•i '• i • i ' i • i ' i ' i
0 W203040SOM70UM100
NEC
TEST-HAM
100
90
90
70
60
N- 33
I '
0 W20304060M708090100
NEC
NEC / ERL
FIGURE 11D: % TYPE II
TEST-CR14
MO
90
K
70
4 »•
0 40
N- 26
0 10203040S0607090M
NEC
TEST=HAI4
100
90
N
70
CO
50
40
30
20
10-
0
N= 27
0 W 20 30 40 SO 60 70 90 M 100
NEC
TEST-HA29
0 10 M 30 40 60 M 70 90 90 100
Figures! 1c and 11d.
Comparability and reliability of NECs and ERLs calculated using dry-weight concentrations and the entire database. See the page proceeding Figure 1 in the report for
additional detail.
-------
100
90
80
70
60
SO
40
30
20
10
ERM / ERM-T
FIGURE 12A: % CORRECT
TEST=CR1«
N-M
i • i • i ' i ' i • i
0 10 20 30 40 60 60 70 M 90 100
ERM
TEST-HAM
100
90
M
70
60
50
40
30
20
10
0
N= 14
100
90
10
70
60
50
40
30
20
W
0
i ' i
0 102030405060708090100
ERM
TEST-HA28
N= 17
i . i . i ' i i I i I ' I ' I ' I ' I
0 102030405060708090MO
ERM
ERM / ERM-T
FIGURE 12B: % TYPE I
TEST*CR14
100
0 10 20 30 « 60 60 70 80 90 100
S—•—i—'—i—'—i—'r~
0 10 20 30 40 50 M 70 BO 90 100
ERM
TEST-HA28
1 I ' I ' I ' I ' I ' I ' I
0 102030405060708090100
ERM
Figures 12aand 12b,
Reliability of ERMs calculated using dry-weight concentrations and using sediment concentrations normalized to total organic carbon (TOC; ERM-T) concentrations for the
entire database. See the page proceeding Figure 1 in the report for additional detail.
-------
ERM / ERM-T
FIGURE 12C: % TYPE II
TEST=CRM
100
M
80
70
<0
JO
40
30
20
10
0
N= 14
0 102030405060706090100
ERM
TEST=HA14
100
90
80
70
t- M
3 50
5
-------
ERL / ERL-T
FIGURE 13A: % CORRECT
TEST-CR14
ERL / ERL-T
RGURE 13B: % TYPE I
TEST-CR14
100
90
80
70
60
SO
40
30
20
10
0
N-14
l • i > i ' l ' l ' i • l ' l ' l ' l ' l
0 10 20 30 40 50 60 70 60 90 100
ERL
TEST=HA14
100
90
80
70
N
SO
40
30
20
10
0
N= 14
r—'—i—1—i ' l • l ' I ' I ' l ' l ' l
0 10 20 30 40 50 60 70 80 90 WO
ERL
TEST=HAH
100
90
80
TO
60
50
40
30
20
10
0
N-14
0 10 20 30 40 50 60 70 N 90 100
ERL
TEST-HA28
100
90
SO
70
60
SO
40
30
20
10
0
N= 14
—•—l—•—i—•—i—'—i—•—i—•—i—'—i—•—i—'—r
0 102030405060706090100
ERL
TEST=HA28
100
90
80
70
60
50
40
30
20
M
N- 17
i ' l • l ' l ' I i i l ' I
0 10 20 30 40 50 60 70 80 90 100
ERL
100
90
80
70
60
50
40
30
20
10
0
N= 17
i i i i i ' i i l i I ' I ' I
0 102030405060708090100
ERL
Figures 13aand 13b.
Reliability of ERLs calculated using dry-weight concentrations and using sediment concentrations normalized to TOC (ERL-T) concentrations for the entire database. See the.
page proceeding Figure 1 in the report for additional detail.
-------
ERL / ERL-T
FIGURE 13C: % TYPE II
TEST=CR14
100
90
M
70
H «0
J, M
9 40
30
20
10
0
100
90
SO
70
(- M
J, 50
5 40
90
20
10
0
N= 14
i ' l '—r—•—i—•—i—i—i ' i ' i ' i • i ' i
0 10 20 30 40 50 60 70 M 90 100
ERL
TEST=HAM
—i—•—r—1—i ' i ' i ' i ' i • i ' i •—r
0 10 20 30 40 50 60 70 60 90 100
ERL
100
90
SO
70
h •»
I
ri M
5 40
0 10 20 30 40 SO 60 70 M 90 100
EHL
Figure 13c.
Reliability of ERLs calculated using dry-weight concentrations and using sediment concentrations normalized to TOG (ERL-T) concentrations for the entire database See the paae
proceeding Figure 1 in the report for additional detail. '
-------
NEC / NEC-T
FIGURE 14A: % CORRECT
TEST-CR14
100
90
80
70
60
50
40
30
20
10
0
N- 14
—T—'—I—'—I—'—I—'—I—'—I—'—1—•—I—'—I 'T
0 102030405060708090100
NEC
TEST-HAM
100
60
80
70
60
50
40
30
20
10
0
N- 14
l ' i ' l ' I ' l ' i
0 102030405060 70 80
NEC
TEST-HAM
100
80
80
70
60
50
40
10
20
10
0
N=T7
i • i i i ' l ' I ' l ' I
0 102030405060706090100
NEC
NEC / NEC-T
FIGURE 14B: % TYPE I
TCST=CR14
100
90
80
70
60
SO
40
30
20
10
0
N= 14
0 10 20 X n 50 (0 70 N 90 100
NEC
TEST=HA14
100
90
60
70
60
50
40
30
20
10
N= 14
i ' i '—i • i '—i—•—r—•—i ' l l
0 n 20 30 40 50 60 70 60 » 100
NEC
TEST-HA26
'l ' I '—i i l ' l
0 10 20 30 40 50 60 70 60 90 100
NEC
Figures 14aand 14b.
Reliability of NECs calculated using dry-weight concentrations and using sediment concentrations normalized to TOG (NEC-T) concentrations for the entire database. See the
page proceeding Figure 1 in the report for additional detail.
-------
NEC / NEC-T
FIGURE 14C: % TYPE II
TEST-CRM
100
90
M
70
60
50
40
30
20
10
0
N- 14
—i—-—i—'—i—•—i—•—]—'—i—•—i '—i—'i 'r
0 1020304050M70MM100
NEC
TKT-HA14
N=14
100
M
H
70
60
50
40
30
20
10
0
—1—>—I——I—1—I—I I ' I ' I ' I ' I ' I
0 10 M 30 40 50 60 70 80 90 100
NEC
TEST=HA21
N- 17
I ' I
0 1020W40506070MM100
NEC
Figure 14c. Reliability of NECs calculated using dry-weight concentrations and using sediment concentrations normalized to TOC (NEC-T) concentrations for the entire database. See the page
proceeding Figure 1 in the report for additional detail.
-------
ERM / ERM-PW
FIGURE 15A: % CORRECT
TEST-CRN
100
90
80
70
60
50
40
30
20
10
0
N- 6
0 10 20 30 40 50 M 70 »0 W 100
EMI
TEST-HAH
too
M
U
70
N
SO
40
30
20
10
0
100
M
M
70
N=7
—i ' i i i ' i
10 20 30 40 60 60 70 M 90 100
ERM
TEST-HAM
i I ' I ' I • I • I I ' I
W203040S06070NM100
ERM
ERM / ERM-PW
FIGURE 15B: % TYPE I
TEST=CR14
0 10 20 30 40 50 60 70 80 90 100
ERM
TEST=HAM
102030405060708090100
Figures 15a and 15t>.
Reliability of ERMs for metals calculated using dry-weight concentrations and pore-water (ERM-PW) concentrations for the entire database. See the page proceeding Figure
1 in the report for additional detail.
-------
ERM / ERM-PW
FIGURE 15C: % TYPE II
TEST=CRI4
100
90
80
70
60
50
W
30
20
10
N- 6
100
90
90
70
60
SO
40
30
20
10
0
i • i —i—1—r ' i ' i ' i ' i—' i ' i ' r
0 10 20 30 40 50 60 70 M 80 100
ERM
TEST=HA14
K- 7
T ' i '—r-1—i " i • i ' i ' i ' i ' i ' r
0 10 M M *) SO M 70 M 90 100
ERM
lEST'HJUB
100-
90
M
70
M
50
40
30
20
10
0
N= 7
i • i i i | i ' i ' i ' I ' i ' i ' ' '
0 10 20 30 40 M M 70 M 90 100
ERM
Figure 15c. Reliability of ERMs for metals calculated using dry-weight concentrations and pore-water (ERM-PW) concentrations for the entire database. See the page proceeding Figure 1 in the
report for additional detail.
-------
ERL / ERL-PW
FIGURE 16A: % CORRECT
TEST-CRN
100
M
80
70
60
60
40
30
20
10
0
100
M
80
70
60
50
40
30
20
to
0
100
90
80
70
60
50
40
30
20
10
0
i ' i ' i ' i
0 102030406080708090100
ERL
TEST-HA14
N= 7
'i i —i ' i ' i ' i ' i ' i ' i
0 102030405060708090100
ERL
TEST-HA28
H= 7
I i i I ' I i I i I ' I
0 10 20 30 40 50 60 70 90 90 100
ERL
ERL / ERL-PW
FIGURE 16B: % TYPE I
TEST=CRH
100
90
M
70
60
50
40
30
20
10
0
0 » 20 30 40 50 N 70 BO 90 100
ERL
TEST=HAH
I ' I
0 10 3f> 30 40 SO 60 70 N 90 100
ERL
TEBT-HA28
100
90
80
70
I «
i Z
30
20
10
o
N- 7
i i i i i ' i ' I i I ' I ' I ' I ' 1 ' I
0 102030405060706080100
EflL
Figures 16aand 16b.
Reliability of ERLs for metals calculated using dry-weight concentrations and pore-water (ERL-PW) concentrations for the entire database. See the page proceeding Figure
1 in the report for additional detail.
-------
ERL/ERL-PW
FIGURE 16C: % TYPE II
TEST=CR14
100
90
80
70
60
SO
40
30
20
10
0
N=6
0 10203040606070MM100
ERL
TEST=HA14
0 102030405060 70 M 90 WO
ERL
TEST-HAM
100
80
80
70
M
60
N- 7
0 10 20 30 40 60 60 70 80 M 100
ERL
Figure 16c. Reliability of ERLs for metals calculated using dry-weight concentrations and pore-water (ERL-PW) concentrations for the entire database. See the page proceeding Figure 1 in the
report for additional detail.
-------
100
90
80
70
60
CO
40
30
20
10
0
100
90
80
70
60
SO
40
30
20
10
0
NEC / NEC-PW
FIGURE 17A: % CORRECT
TBT-CRI4
N- 8
i • i * i ' — i ' i ' — i ' i • i ' — i ' i
10 20 30 40 60 60 70 80 80 100
NEC
TEST- HAH
N" 7
10 20 30 40 60 60 70 80 90 100
NEC
TEST-HA28
100-1
90
80
70
60
50
40
30
20
10
0
N- 7
0 10 20 30 40 BO 60 70 80 90 100
NEC
NEC / NEC-PW
FIGURE 17B: % TYPE I
TEST-CRM
100-j
90
80
70
60
50
40
30-
20
10
0
N- e
0 10 20 30 40 50 60 70 80 90 100
NEC
TEST-HA14
100-J
90
60
70-
M
»
40
30
20
10
N- 7
i ' i—•—i—' "i * i • i * i—•—i • i •—r
10 20 30 40 50 60 70 80 90 100
NEC
TEST-HA28
N- 7
0 10 20 30 40 60 60 70 80 90 100
NEC
Figures 17a and 17b. Reliability of NECs for metals calculated using dry-weight concentrations and pore-water (NEC-PW) concentrations for the entire database. See the
Figure 1 in the report for additional detail.
page proceeding
-------
NEC / NEC-PW
FIGURE 17C: % TYPE II
TEST-CW4
100
90
00
70
60
60
40
30
20
10-
0
I ' I ' I ' I ' I ' I • I ' I ' I ' I ' I
0 10 20 30 40 60 60 70 80 90 100
NEC
TEST-HAM
100
90
80
70
60
60
40
30
20-
10-
0
N- 7
0 10 20 30 40 60 60 70
NEC
TEST-HA28
90 100
100
go
to
70
60
50
40
30
20
10
0-
N= 7
0 10 20 30 40 SO 60 70 80 90 100
NEC
Figure 17c. Reliability of NECs for metals calculated using dry-weight concentrations and pore-water (NEC-PW) concentrations for the entire database. See the page proceeding
Figure 1 in the report for additional detail.
-------
ERM-BT / ERM-BS
FIGURE 18A: % CORRECT
TEST-CRH
100
M
to
70
60
GO
40
30
20
10
0
N- 5
I ' I ' I ' i
I ' I • I ' I ' i ' I
0 W 20 30 « SO 60 70 80 90 100
ERM-BT
TEST-HAM
70
N- 5
—T-I i •—i i p--—i—'—i—•—i—•—i—•—i—•—r
0 W 20 30 40 50 60 70 60 90 100
EflM-BT
TEST-HAM
100
W
M
70
GO
50
40
30:
20
10
0-
N« 8
0 10 » 30 W M 60 70 80 90 100
ERM-BT
ERM-BT/ERM-BS
FIGURE 18B: % TYPE I
TEST=CR14
l ' l • i -
0 10 20 30 40 SO 60 70 M 90 100
ERM-BT
TEST-HAM
0 W W 30 <0 60 60 70 SO M 100
0 10 20 M 40 SO 60 70 BO 90 100
ERM-BT
Figures 18aand 18b.
Reliability of ERMs calculated using total-metal (ERM-BT) concentrations and simultaneously extracted metal (ERM-BS) concentrations for the entire database. See the
page proceeding Figure 1 in the report for additional detail.
-------
ERM-BT /ERM-BS
FIGURE 18C: % TYPE II
TKT=CR14
100
90
80
70
N= 6
0 10 20 30 40 50 M 70 80 90 100
ERM-BT
TEST=HA14
100
00
80
70
to
M
40
30
20
10
0
N= 5
0 10 M 30 40 50 60 70 SO 90 100
ERM-BT
TEST=HA28
100
00
to
70
60
50
40
'30
M
10
0
I i I ' I ' I ' I ' I ' I ' I ' I ' I
0 WM304050W708090100
ERM-BT
Figure 18c. Reliability of ERMs calculated using total-metal (ERM-BT) concentrations and simultaneously extracted metal (ERM-BS) concentrations for the entire database. See the page
proceeding Figure 1 in the report for additional detail.
-------
ERL-BT / ERL-BS
FIGURE 19A: % CORRECT
TEST=CR14
ERL-BT/ERL-BS
FIGURE 19B: % TYPE I
TE8T=CR14
100
80
70
N= 5
*.'
i • i—' i ' i
0 10 20 30 40 SO N 70 N 90 100
ERL-BT
TEST=HA14
100
90
60
70
60
60
40
30
20
10
0
N= 6
0 10 20 30 40 SO 60 70 80 90 100
ERL-BT
TEST-HA14
100
90
00
70
60
60
40
30
20
10
0
N- 5
100
T—i— I ' I '
0 10M3040606070W9D100
ERL-BT
TEST=HA26
i—'—i—'—r~
0 10 20 30 40 M 60 70 80 90 100
ERL-BT
TEST=HAM
100
90
80
70
60
60
40
30
20
10
N- 8
l ' I I I ' I ' I
0 10 20 30 40 60 60 70 80 90 100
ERL-BT
V ' iJl—i ' ( ' i '—r
0 102030406060708090100
ERL-BT
Figures 19aand 19b.
Reliability of ERLs calculated using total-metal concentrations (ERL-BT) and simultaneously extracted metal (ERL-BS) concentrations for the entire database. See the page
proceeding Figure 1 in the report for additional detail.
-------
ERL-BT / ERL-BS
RGURE IOC: % TYPE II
TEST"CR14
0 102030405060708090100
ERL-BT
TEST-HUB
100
M
N
70
60
60
40
30
20
10
0
' I ' I i I i I i I ' I i I ' I ' I ' I
10 20 M M 60 60 70 80 90 100
ERL-BT
Figure 19c. Reliability of ERLs calculated using total-metal concentrations (ERL-BT) and simultaneously extracted metal (ERL-BS) concentrations for the entire database. See the page
proceeding Figure 1 in the report for additional detail.
-------
NEC-BT/NEC-BS
FIGURE 20A: % CORRECT
TEST=CRI4
100
90
80
70
60
SO
40
30
20
10
0
N=S
0 U 20 30 40 SO N 70 N 90 100
NEC-BT
TEST-HAM
100
90
80
70
60
SO
40
30
20
10
0
100
90
M
70
M
SO
40
30
20
10
0
N- 5
I—-—i—'—i—•—i—-—i—•—i—'—i—•—i—'—i—•—i—'—r
0 102030405060 70 BOW 100
NEC-BT
TEST-HAM
'i i i ' I ' i ' I i I ' I ' I ' I ' I ' I
0 102030405060 70 8090 100
NEC-BT
NEC-BT / NEC-BS
FIGURE 20B: % TYPE I
TEST-CRM
N=5
0 10 20 30 40 50 60 70 80 90 100
NEC-BT
TEST-HAM
100
90
80
78
60
SO
40
30
20
10
0
N= S
T—' i '—i ' i ' I ' i • i "•—r—i—i ' i '—r
0 1020304050M70MM1M
NEC-BT
TEST-HA28
8
i
V ' i * i i i ' i ' i
0 102030406060708090100
NEC-BT
Figures 20a and 20b.
Reliability of NECs calculated using total-metal (NEC-BT) concentrations and simultaneously extracted metal (NEC-BS) concentrations for the entire database. See the page
proceeding Figure 11n the report for additional detail.
-------
NEC-BT/NEC-BS
FIGURE 20C: % TYPE II
TEST=CflH
100
90
80
70
N= 5
i i i '—i ' i '—i ' i ' i ' i
0 102030405060708080100
NEC-BT
TEST-HAH
100
M
80
70
K= 5
Y • i ' i • i -•—i • i ' i ' i
0 10 20 30 40 50 60 70 N 90 100
NEC-BT
TEST-HAM
100
90
>0
70
60
60
40
30
20
10
0
N= g
t ' i i i i ' i • i ' i • i
0 10 SO 30 40 50 60 70 N 80 100
NEC-BT
Figure 20c. Reliability of NECs calculated using total-metal (NEC-BT) concentrations and simultaneously extracted metal (NEC-BS) concentrations for the entire database. See the page
proceeding Figure 1 in the report for additional detail.
-------
too
90
BO
70
60
SO
40
30
20
10
0
-ERM-
FIGURE 21A: ALL ERMs
SAMPTYP=BT TEST=CR14
NM2 / SEC-22
a
23456789
MINIMUM NUMBER OF EXCEEDANCES
CORRECT
NOT TOXIC/NO HIT
TOXKVNOHTT
TOXKVHir
NOTTOXKVHir
-ERM-
FIGURE 21B: 60% CRITERION
SAMP7YP=BT TEST=CR14
12345678
MINIMUM NUMBER OF EXCEEDANCES
CORRECT
NOT TOXIC/NO HIT
100
90
80
70
60
50
40
30
20
10
0
-ERM-
RGURE 21C: 70% CRITERION
SAMPTYP=BT TEST=CR14
N-42 / SEC-21
-D a a
n D a c
2 3 4 5 6 7 8
MINIMUM NUMBER OF EXCEEDANCES
NOT TOXIC/NO KIT
TOXIC/NO HIT
TOXKVHIT
NOT TOXIC/HIT
SAMPTYP=BT TEST=HA14
100
90
BO
70
60
50
40
30
20
10
0
N-32 / SEC-22
ja— ° a a
^-t-^-«-
12345
n—- R-
fl»-a
±P^3
-e~-f>
6 7
D
-«-
U
— 0-
8
D E
-ft — F
LJ L
-O — f
9 10
CORRECT
NOT TOXKVNO HIT
mm™
NOTTOXKVHrr
SAMPTYP=
100
90 • »-
80 i-""^
70
60 n— a — B
5,^0-™
30 • -^ III LJ U
20 5-
10 5-">@r — & — 6
BTTEST=HA14
N-32 / SEC-22
,-, n H R B E
B tt ^ !-><-'•-
— -9— -9 — P) — PI — o — T
CORRECT
NOT TOMC/NO HIT
NOTTOXKVHfT
SAMPTYP=BT TEST=HA14
MINIMUM NUMBER OF EXCEEDANCES
123456789
MINIMUM NUMBER OF EXCEEDANCES
CORRECT
NOT TOXKVNO HIT
a a a d a—a a
NOT TOXKVHIT
23456789
MINIMUM NUMBER OF EXCEEDANCES
SAMPTYP=BT TEST=HA28
SAMP1\P=BT TEST=HA28
SAMPTYP=BT TEST=HA28
NOTTOXPC/NOHIT
23458789
MINIMUM NUMBER OF EXCEEDANCES
CORRECT
NOT TOXKVNO HIT
12345678
MINIMUM NUMBER OF EXCEEDANCES
BOHRBNC/NO HIT
TOXIC/NO HIT
2345678
MINIMUM NUMBER OF EXCEEDANCES
Figure 21 Observed and expected toxiclty of samples based on the minimum number of ERM exceedances using dry-weight concentrations for the entire database. N = number of samples and
SEC = number of SECs used. Figure 21 a uses all Individual ERMs listed in Appendix 3a regardless of percentage correct classification by these Individual ERMs. Figure 21b uses only
those chemicals for which Individual ERMs correctly classify >60% of the samples. Figure 21 c uses only those chemicals for which Individual ERMs correctly classify >70% of the
samples.
-------
§»
ll
O Q.
3 a>
j> a
3 i 1
3 c{) I
: cjj i
3 I
3 1
1 ^ n
^
i
i
i
i
i i
• I
« &
II
23
-------
i»
la
== -
-j -
at -
o -
;
s -
UAiiiLJ L
C
1
3D C
ij i
i
05
I
1
d
I
fT'
3cb :
1
)cb d
3d) C
i
1 r-h (
3
3
3
]i
}i
31
]l
1
• -
i
i
r
i
i
z
ft
m
•
=:
m
°
-------
-NEC/ERM/ERL-
FIGURE 24
SAMPTYP=BTTEST=HA28
Co*
£
13
UJ
IT
£C
O
O
i
UJ
Q.
g
HI
CL
100
80
60
40-
20-
0-
100-
80-
60
40-
20-
0.
100-
80
60-
40-
20-
-S-;^-|^|^i-|
2 B Q--B--ET"'
• •• i •.. i ... i ...[... j ,,, i ,,,,,,,,.,,,
1 23456789 1C
MINIMUM NUMBER OF EXCEEDENCES
SAMPTYP=BT TEST=HA28
3— Q._B._&
N
3--^.^ ^^^^-^.^7
~e~~^---€}--o._~
I ' ' ' I ' ' ' I ' ' ' I ' ' ' I ' ' ' I ' ' ' I ' ' ' I ' ' ' I ' ' ' i
1 23456789 10
MINIMUM NUMBER OF EXCEEDENCES
SAMPTYP=BT TEST=HA28
V*— * — *^" ."...0— 0— G— £
^irgLCS.'liq—iq— B~&-B-B-€
-
:
: BED
'• ERL
•ERL
ERM
LKICf*
NcC
NEC
- ERM
ERL
345678
MINIMUM NUMBER OF EXCEEDENCES
9 10
Figure 24 Observed and expected toxicity of HA28 samples based on the minimum number of NEC, ERM, and ERL exceedances for the entire database
using dry-weight concentrations regardless of percentage correct classification by these individual ERMs. See legend of Figure 21 for a
description of Figure 24.
-------
B
EC
§
ERM
FIGURE 25: DRY-WEIGHT vs TOO NORMALIZATION
SAMPTYP=BTTEST=HA28
N=62 / SEC=11
3456789 10
MINIMUM NUMBER OF EXCEEDENCES
111
100-
80 \
60-i
40
20
01
1
SAMPTYP=BT TEST=HA28
I j < J i . T I| l l I j r r i- j r—1 i | II 1II
3456789
MINIMUM NUMBER OF EXCEEDENCES
10
100-
80
60
40
SAMPTYP=BT TEST=HA28
-r-i | . i i . i i
345678
MINIMUM NUMBER OF EXCEEDENCES
9 10
Figure 25 Observed and expected toxicity of HA28 samples based on the minimum number of ERM exceedances for the entire database using
only individual ERMs for PAHs or PCBs calculated using dry-weight concentrations or sediment concentrations normalized to total
organic carbon (TOG) concentration which correctly classify >60% of the samples. See legend of Figure 21 for a description of
Figure 25.
-------
GL SECs-ERM-MT DATA
FIGURE 26: 70% CRITERION
SAMPTYP=BT TEST=CR14
HI
O
a:
oi
Q.
100
90
80
70
60:
50-
40:
30^
20
10
0
111
N=1
SEC=
BORFBWC/NO HIT
TOXIC/NO HIT
1 23456789
MINIMUM NUMBER OF EXCEEDANCES
10
SAMPTYP=BTTEST=HA28
01
o
IT
UJ
D.
TOXIC/NO HIT
HOEFE3CIC/NO HIT
\
2345678
MINIMUM NUMBER OF EXCEEDANCES
NUUlVtU9IC/HIT
10
Figure 26 Observed and predicted toxicity of Clark Fork River samples based on the minimum number of Great Lakes ERM exceedances using
dry-weight concentrations and using only those chemicals for which individual SECs correctly classify >70% of the Great Lakes
samples. See legend of Figure 21 for a description of Figure 26.
-------
THRESHOLDS
FIGURE 27
CHEMCODE = BAP
ALL-CR14 BT
ALL-HA14 BT
ALL-HA28 BT
OTHER
^
T~
10
100 1000
CONCENTRATION (NG/G)
10000
100000
Figure 27
Comparability of our SECs tor the entire database to published SECs tor benzo[a)pyrene (BaP) based on dry-weight concentrations. Marine ERL and ERM (ERLM and ERMM; Long et
al., 1995); marine TEL and PEL (TELM and PELM; MacDonald, et al., 1995); freshwater TEL and PEL (TELF and PELF; Smith et al., 1996); (4) marine AETs (AET1 for amphipods,
AET2 tor oysters. AET3 for Mlcrotox, AET4 tor benthos; Barrick et al., 1988); freshwater AETs (AETS for Hyalella azfeca and AET6 for Microtox; Baits and Cubbage, 1995 (assumed 2%
total organic carbon (TOC)); (6) Screening Level Concentrations (SLC1 for lowest effect level. SLC2 for severe effect level (assumed 2% TOC); Persaud et al., 1992); and (7) EQP
(USEPA, 1988; Hoke et al., 1995; assumed 2% TOC).
-------
ALL-CR14 BT
ALL-HAH BT
ALL-HA28 BT
OTHER
THRESHOLDS
FIGURE 28
CHEMCODE = COPPER
A • •
A • • A
I]
10
_•*,.
100
CONCENTRATION (NG/G)
^f- ^\~t T^ "-
1000
-r-r-p
10000
Figure 28 Comparability of our SECs to published SECs for copper based on dry-weight concentrations. See legend of Figure 27 for an description of the abbreviations in Figure 28.
-------
&
UJ
cc
flC
PELF/SLC1/AET5/EQP
FIGURE 29
SAMPTYP=BT TEST=HA28
T
23456789
MINIMUM NUMBER OF EXCEEDENCES
10
SAMPTYP=BT TEST=HA28
23456789 10
MINIMUM NUMBER OF EXCEEDENCES
&
UJ
CL
100-
80:
60:
40 -
20
0
SAMPTYP=BT TEST=HA28
•3-
±=*=*=i=Z-*-+-
23456789
MINIMUM NUMBEB OF EXCEEDENCES
10
Figure 29 Observed and predicted toxicity of HA28 samples based on dry-weight concentrations and the minimum number of exceedances of
published freshwater PELs (PELF; Smith et al., 199S), Hyalella azteca AETs (AET5; Batts and Cubbage, 1995; assumed 2% TOC),
EQP (USEPA, 1988; Hoke et al., 1995; assumed 2% TOG) and SLCs {SLC1; lowest effect level for Screening Level Concentrations;
Persuad etal., 1992). See legend of Figure 21 for a description of Figure 29.
-------
Figure 30: Hyalella azteca 28-d test: toxicity vs. ERM
^u
*-*
(/) 4c
UJ ID
O
z
Q m
UJ 1U
UJ
o
X
III
5 5
jS
uu
UJ
0
o NOT TOXIC
. TOXIC
•
•
• •
_ o
•
00
OOD»
• •
O O OD
cm o
GODX3DO
i i i i 1 1 uL,~-J_a- u mil i i iiiinl i i iiiinl i i linn
0.1 1 10 100 1,000 10,1
SUM ERM TOXIC QUOTIENT
Figure 30 Relationship between the frequency of ERM exceedances and the sum of the ERM toxic quotient for toxic and non-toxic HA28 samples using all ERMs regardless of the percent correct
classification using dry-weight concentrations. Adapted from Canfleld et al. (199Ga,b) and Kemble et al. (1996).
-------
Appendix 1 Summary of biological, chemical, and physical characterization performed on
sediment samples from each site.
-------
APPENDIX 1: BIOLOGICAL, PHYSICAL AND CHEMICAL CHARACTERIZATIONS PERFORMED
CHAR
NAME
INDIANA BUFFALO SAGINAW SAGINAW WAUKEGAN UPPER CLARK TRINITY MOBILE GALVESTON
TYPE HARBOR RIVER RIVER-1 RIVER-3 HABOR MISS MILLTOWN FORK RIVER BAY BAY
***BIOLOGICAL***
CR14 OVERALL TOXICITY
CR14 OVERALL TOXICITY
CR14 SURVIVAL
CR14 SURVIVAL
CR14 GROWTH
CR14 GROWTH
HA14 OVERALL TOXICITY
HA14 OVERALL TOXICITY
HA14 SURVIVAL
HA14 SURVIVAL
HA14 GROWTH
HA14 GROWTH
HA14 MATURATION
HA14 MATURATION
HA28 OVERALL TOXICITY
HA28 OVERALL TOXICITY
HA28 SURVIVAL
HA28 SURVIVAL
HA28 GROWTH
HA28 GROWTH
HA28 MATURATION
HA28 MATURATION
***PHYSICAL & CHEMICAL***
101 Total Organic Carbon
102 Acid Volatile Sulfides
104 Clay
105 Sand
106 Water
107 Silt
108 Ash-Free Dry Weight
109 Cation Exchange Capacity
110 Porewater ammonia
111 Porewater hydrogen sulfide
201 2,3,7,8-Tetrachlorodibenzofuran
202 Total Tetrachlorodibenzofuran
203 2,3,7,8-Tetrachlorodibenzodioxin
204 Total Tetrachlorodibenzodioxin
205 1,2,3,7,8-Pentachlorodibenzofuran
206 2,3,4,7,8-Pentachlorodibenzofuran
207 Total Pentachlorodibenzofuran
208 1,2,3,7,8-Pentachlorodibenzodioxin
209 Total Pentachlorodibenzodioxin
210 1,2,3,4,7,8-Hexachlorodibenzofuran
211 1,2,3,6,7,8-Hexachlorodibenzofuran
212 1,2,3,7,8,9-Hexachlorodibenzofuran
213 2,3,4,6,7,8-Hexachlorodibenzofuran
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
1
4
1
4
1
1
4
1
4
3
3
1
4
1
4
3
3
5
5
1
5
5
1
3
2
3
3
3
3
3
3
3
3
2
3
3
3
3
3
4
2
5
1
1
5
5
1
1
5
2
4
2
4
2
4
4
2
6
6
6
1
6
6
1
6
5
3
5
1
5
5
5
5
1
5
5
5
5
3
1
3
1
3
1
3
1
3
1
4
4
1
3
3
1
1
3
3
1
4
4
1
4
4
1
4
3
3
3
3
3
3
3
3
3
3
3
3
3
8
8
8
7
1
8
8
7
1
8
8
8
8
8
7
1
8
8
1
8
7
7
7
7
7
7
7
4
6
7
7
7
7
2
2
2
2
2
2
2
2
4
2 5
2
2 5
2
3
1
4 5
4 5
4 5
4 5
4 5
7
1
7
1
7
1
2
6
7
1
2
6
6
2
8
8
8
8
8
8
8
8
8
8
7
7
7
5
5
555
2
655
1
5
2
6
1
755
7
7 5
7 5
7 5
7 5
7
7
7 .
7
2
3
2
3
3
1
5
5
5
5
5
5
5
-------
APPENDIX 1: BIOLOGICAL, PHYSICAL AND CHEMICAL CHARACTERIZATIONS PERFORMED
CHAR
214
215
216
217
218
219
220
221
222
223
224
225
300
300
301
301
302
302
302
303
303
303
304
304
304
305
305
305
306
306
307
307
308
308
309
309
309
310
310
310
311
312
312
312
313
314
315
316
399
NAME
Total Hexachlorodibenzofuran
1,2,3,4,7,8 -Hexachlorodibenzodioxin
1,2,3,6,7,8 -Hexachlorodibenzodioxin
1,2,3,7,8,9- Hexachlorodibenzodioxin
Total Hexachlorodibenzodioxin
1,2,3,4,6,7,8 -Heptachlorodibenzof uran
1,2,3,4,7,8,9 -Heptachlorodibenzof uran
Total Heptachlorodibenzofuran
1,2,3,4,6,7, 8-Heptachlorodibenzodioxin
Total Heptachlorodibenzodioxin
Octachlorodibenzofuran
Octachlorodibenzodioxin
Aluminum
Aluminum
Silver
Silver
Arsenic
Arsenic
Arsenic
Cadmium
Cadmium
Cadmium
Chromium
Chromium
Chromium
Copper
Copper
Copper
Iron
Iron
Mercury
Mercury
Manganese
Manganese
Nickel
Nickel
Nickel
Lead
Lead
Lead
Selenium
Zinc
Zinc
Zinc
Methyl -mercury
Tributylin
Dibutylin
Monobutylin
Ratio of SEM metals to AVS
TYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
PW
BS
BT
PW
BS
BT
PW
BS
BT
PW
BS
BT
PW
BS
BT
BT
PW
BS
BT
BS
BT
PW
BS
BT
PW
BT
BS
BT
PW
BT
BT
BT
BT
BS
INDIANA
HARBOR
3
3
3
3
3
3
3
3
3
3
3
3
1
1
4
4
1
5
5
5
5
5
5
5
5
5
5
5
5
5
4
4
5
5
5
5
5
5
5
5
4
5
5
5
4
4
4
4
4
BUFFALO
RIVER
5
5
5
5
3
5
5
5
5
5
5
5
1
1
5
5
1
6
6
6
6
6
6
6
6
6
6
6
6
6
5
5
6
6
6
6
6
6
6
6
5
6
6
6
5
5
5
5
5
SAGINAW
RIVER- 1
3
3
3
3
3
3
3
3
3
3
3
3
1
1
3
3
1
4
4
4
4
4
4
4
4
4
4
4
4
4
3
3
4
4
4
4
4
4
4
4
3
4
4
4
3
3
3
3
3
SAGINAW
RIVER -3
7
5
5
7
7
7
7
7
7
7
7
7
1
1
7
4
1
8
5
7
8
5
7
8
5
7
8
5
1
1
7
4
7
8
7
8
5
7
8
5
7
7
8
5
6
WAUKEGAN UPPER
HABOR MISS MILLTOWN
8
8
8
4 . 8
8
8
458
8
8
458
8
8
4 . 8
8
8
8
8
8
8
458
8
8
458
8
a
458
8
7
CLARK
FORK
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
.
7
7
7
7
7
7
7
7
7
7
7
6
TRINITY MOBILE
RIVER BAY
1
1
1
5
1
1
5 5
1
1
5 5
1
1
5
1
1
1
1
1
1
5 5
1
1
5 5
1
1
5 5
1
GALVESTON
BAY
5
5
5
5
5
5
5
5
5
5
5
-------
APPENDIX 1: BIOLOGICAL, PHYSICAL AND CHEMICAL CHARACTERIZATIONS PERFORMED
CHAR NAME
401 1,4-Dichlorobenzene
402 1,2-Dichlorobenzene
403 1,3-Dichlorobenzene
404 Naphthalene
405 2-Methylnaphthalene
406 Acenaphthene
407 Dibenzofuran
408 Fluorene
409 Phenanthrene
410 Anthracene
411 Fluoranthene
412 Pyrene
413 Benz(a)anthracene
414 Chrysene
415 Benzo(b)fluoranthene
416 Benzo(k)fluoranthene
417 Benzo(a)pyrene
418 Indeno (1,2,3-c,d)pyrene
419 Benzo(g,h,i)perylene
420 Benzo(b,k)fluoranthene
421 Acenaphthylene
422 Dibenz(a,h)anthracene
423 4-Methylanphthalene
450 PAH-T
451 PAH-L
452 PAH-H
501 PCB 1016
502 PCB 1221
503 PCB 1232
504 PCB 1242
505 PCB 1248
506 PCB 1254
507 PCB 1260
508 TOTAL PCBS
601 Dimethyl Phthalate
602 Dibutyl Phthalate
603 Diethyl Hexglphthalate
604 2 Fluorobiphenyl
605 Nitrobenzene
606 Butyl Benzyl Phthalate
607 Di-n-octylphalate
608 Bis(2-ethylhexyl)Phthalate
701 Aldrin
702 Hexachlorocyclohexane-alpha
703 Hexachlorocyclohexane-beta
704 Hexachlorocyclohexane-delta
705 Hexachlorocyclohexane-gamma
706 trans-chlordane
707 cis-chlordane
TYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
INDIANA
HARBOR
4
5
4
1
4
5
5
5
5
5
5
S
4
4
5
5
5
1
1
1
5
5
5
4
4
4
4
4
4
4
1
4
4
4
4
4
4
4
4
4
4
4
4
4
BUFFALO
RIVER
5
6
5
1
5
6
6
6
6
6
6
6
5
5
6
6
6
1
1
1
6
6
6
5
5
5
5
5
5
5
1
5
5
5
5
5
5
5
5
5
5
5
5
5
SAGINAW
RIVER- 1
3
4
3
1
3
4
4
4
4
4
4
4
3
3
4
4
4
1
1
1
4
4
4
3
3
3
3
3
3
3
1
3
3
3
3
3
3
3
3
3
3
3
3
3
SAGINAW
RIVER- 3
7
7
7
8
7
1
7
8
8
8
8
8
8
8
7
7
8
8
8
1
8
1
7
8
8
8
7
7
7
1
7
7
7
7
7
7
7
7
7
7
7
7
7
WAUKEGAN
HABOR
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
UPPER
MISS
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
MILLTOWN
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
8
CLARK
FORK
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
7
TRINITY
RIVER
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
1
MOBILE
BAY
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
GALVESTON
BAY
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
-------
APPENDIX 1: BIOLOGICAL, PHYSICAL AND CHEMICAL CHARACTERIZATIONS PERFORMED
CHAR NAME
708 4,4,DDD
709 4, 4,DDE
710 4, 4, DDT
711 Dieldrin
712 Endosulfan-alpha
713 EndosuLfan-beta
714 Endosulfan sulphate
715 Endrin
716 Endrin Aldehyde
717 Endrin Ketone
718 Heptachlor
719 Heptachlor epoxide
720 Toxaphene
721 Methoxychlor
TYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
INDIANA
HARBOR
4
4
4
4
4
4
4
4
4
4
4
4
4
4
BUFFALO
RIVER
5
5
5
5
5
5
5
5
5
5
5
5
5
5
SAGINAW
RIVER- 1
3
3
3
3
3
3
3
3
3
3
3
3
3
3
SAGINAW WAUKEGAN
RIVER- 3 HABOR
7
7
7
7
7
7
7
7
7
7
7
7
7
7
UPPER CLARK TRINITY MOBILE GALVESTON
MISS MILLTOWN FORK RIVER BAY BAY
-------
Appendix 2a Biology database. The computer disk that accompanies the report contains the
electronic version of this entire appendix (file name: "apdx2a.txt" for the ascii
format and "apdx2a.dbf' for the database file).
Appendix 2b Chemistry database. The computer disk that accompanies the report contains the
electronic version of this entire appendix (file name: "apdx2b.txt" for the ascii
format and "apdx2b.dbf' for the database file).
-------
Appendix 2c Chemistry codes. NUMCODE =Numeric code, MOLE. WT. = molecular
weight, NFCRC REPORT = Designation in USEPA (1993), CHEMCODE -
Designation for the current report, CHEMICAL NAME, NA = not applicable.
NUMCODE MOLE. WT.
101 NA
102 NA
103 NA
104 NA
105 NA
106 NA
107 NA
108 NA
109 NA
110 NA
111 NA
201 305.98
202 305.98
203 321.98
204 321.98
205 340.43
206 340.43
207 340.43
208 356.43
209 356.43
210 374.87
211 374.87
212 374.87
213 374.87
214 374.87
215 390.87
216 390.87
217 390.87
218 390.87
219 409.32
220 409.32
221 409.32
222 425.32
223 425.32
224 443.76
225 459.76
300 26.9815
301 107.87
302 74.92
303 112.4
304 51.996
305 63.54
306 55.847
307 200.59
308 54.938
309 58.71
310 207.19
311 78.96
312 65.37
NFCRC REPORT
TOC
AVS
SOLIDS
CLAY
SAND
WATER
SILT
AFDW
CEC
NH3-P
HS-P
2378-TCDF
Total TCDF
2378 TCDD
Total TCDD
12378-PeCDF
23478-PeCDF
Total PeCDF
12378-PeCDD
Total PeCDD
123478-HxCDF
123678-HxCDF
123789-HxCDF
234678-HxCDF
Total HxCDF
123478-HxCDD
123678-HxCDD
123789-HxCDD
Total HxCDD
1234678-HpCDF
1234789-HpCDF
Total HpCDF
1234678-HpCDD
Total HpCDD
OCDF
OCDD
Al
Ag
As
Cd
Cr
Cu
Fe
Hg
Mn
Ni
Pb
Se
Zn
CHEMCODE CHEMICAL NAME
TOC Total Organic Carbon
AVS Acid Volatile Sulfides
NA Total Solids
CLAY Clay
SAND Sand
WATER Water
SILT Silt
AFDW Ash-Free Dry Weight
CEC Cation Exchange Capacity
NH3P Pore-water ammonia
HSP Pore-water hydrogen sulfide
TCDF 2,3,7,8-Tetrachlorodibenzofuran
TCDF-T Total Tetrachlorodibenzofuran
TCDD 2,3,7,8-Tetrachlorodibenzodioxin
TCDD-T Total Tetrachlorodibenzodioxin
PECDF-A 1,2,3,7,8-Pentachlorodibenzofuran
PECDF-B 2,3,4,7,8-Pentachlorodibenzofuran
PECDF-T Total Pentachlorodibenzofuran
PECDD-A 1,2.3,7,8-Pentachlorodibenzodioxin
PECDD-T Total Pentachlorodibenzodioxin
HXCDF-A 1,2,3,4,7,8-Hexachiorodibenzofuran
HXCDF-B 1,2,3,6,7,8-Hexachlorodibenzofuran
HXCDF-C 1,2,3,7,8,9-Hexachlorodibenzofuran
HXCDF-D 2,3,4,6,7,8-Hexachlorodibenzofuran
HXCDF-T Total Hexachlorodibenzofuran
HXCDD-A 1,2,3,4,7,8-Hexachlorodibenzodioxin
HXCDD-B 1,2,3,6,7,8-Hexachlorodibenzodioxin
HXCDD-C 1,2,3,7,8,9-Hexachlorodibenzodioxin
HXCDD-T Total Hexachlorodibenzodioxin
HPCDF-A 1,2,3,4,6,7,8-Heptachlorodibenzofuran
HPCDF-B 1,2,3,4,7,8,9-Heptachlorodibenzofuran
HPCDF-T Total Heptachlorodibenzofuran
HPCDD-A 1,2,3,4,6,7,8-Heptachlorodibenzodioxin
HPCDD-T Total Heptachlorodibenzodioxin
OCDF Octachlorodibenzofuran
OCDD Octachlorodibenzodioxin
AL Aluminum
SILVER Silver
ARSENIC Arsenic
CADMIUM Cadmium
CHROMIUM-T Chromium
COPPER Copper
IRON Iron
MERCURY Mercury
MANGANESE Manganese
NICKEL Nickel
LEAD Lead
SELENIUM Selenium
ZINC Zinc
-------
Appendix 2c (continued)
313
314
315
316
317
318
319
320
399
401
402
403
404
405
406
407
408
409
410
411
412
413
414
415
416
417
418
419
420
421
422
423
424
450
451
452
501
502
503
504
505
506
507
508
601
602
603
604
605
606
607
608
701
702
215.63
290.04
232.93
175.81
NA
NA
NA
NA
NA
147.01
147.01
147.01
128.16
142.2
154.21
168
166.21
178.22
178.22
202.3
202.24
228.28
228.28
252.30
252.30
252.30
276
276
252.30
152.2
278
142.2
NA
NA
NA
NA
257.5
196
219
258
289
326
371
NA
194.19
NA
NA
NA
NA
312
390.54
390.54
364.92
291
Hg-Me
TBT
DBT
MET
NA
NA
NA
NA
SEMAVS
1,4DCB
1,2 DCB
1,3 DCB
Naph(l)
2-MNaph
Acnaph(3)
DBF
Fluore(4)
Phen(5)
Anth(6)
Fluora(7)
Pyrene(8)
BAA(9)
Chrys(lO)
BbFluor
BkFluor
BAP(13)
IndPyr(14)
BghiPer(16)
BbkFluor(ll)
Acenaphthylene(2)
DBA(15)
4-MNaph
NA
PAH-T
PAH-L
PAH-H
PCB 1016
PCB 1221
PCB 1232
PCB 1242
PCB 1248
PCB 1254
PCB 1260
PCB(17)
DMPH
NA
NA
NA
NA
BBPh
DnOPh
BisPh
Aldrin
BHC-a
METHYL-HG
TBT
DBT
MET
BERYILLIUM
BORON
MOLYBDENUM
STRONTIUM
SEMAVS
14-2CLBNZ
12-2CLBNZ
13-2CLBNZ
NAPHTHALENE
2-METHNAP
ACENA
DIBNZFURAN
FLUORENE
PHENANTHRN
ANTHRACENE
FLUORANTHN
PYRENE
BAA
CHRYSENE
BBF
BKF
BAP
ICDP
BGHIP
BBKF
ACENAPTYLE
DBA
4-METHNAP
PERYLENE
PAH-T
PAH-L
PAH-H
PCB 1016
PCB 1221
PCB 1232
PCB 1242
PCB 1248
PCB 1254
PCB 1260
PCB-T
DIMP
DIMBP
DEHP
2FLUOROBIP
NBNZ
BUTBNZ PHT
2NOCTP
B2ETHXPHTH
ALDRIN
6CL-CHX-A
Methyl-mercury
Tributylin
Dibutylin
Monobutylin
NA
NA
NA
NA
Ratio of SEM metals to AVS
1,4-Dichlorobenzene
1,2-DichIorobenzene
1,3-Dichlorobenzene
Naphthalene
2-Methylnaphthalene
Acenaphthene
Dibenzofuran
Fluorene
Phenanthrene
Anthracene
Fluoranthene
Pyrene
Benz(a)anthracene
Chrysene
Benzo(b)fluoranthene
Benzo(k)fluoranthene
Benzo(a)pyrene
Indeno (l,2,3-c,d)pyrene
Benzo(g,h,i)perylene
Benzo(b,k)fluoranthene
Acenaphthylene
Dibenz(a,h)anthracene
4-Methylnaphthalene
NA
PAH Total (others)
PAH Low
PAH High
PCB 1016
PCB 1221
PCB 1232
PCB 1242
PCB 1248
PCB 1254
PCB 1260
TOTAL PCBS
Dimethyl Phthalate
Dibutyl Phthalate
Diethyl Hexglphthalate
2 Fluorobiphenyl
Nitrobenzene
Butyl Benzyl Phthalate
Di-n-octylphalate
Bis(2-ethylhexyl)Phthalate
Aldrin
Hexachlorocyclohexane-alpha
-------
Appendix 2c (continued)
703
704
705
706
707
708
709
710
711
712
713
714
715
716
717
718
719
720
721
900
901
902
903
904
905
906
907
908
909
910
911
912
913
914
915
916
917
918
920
921
922
923
924
925
291
291
291
410
410
320
318
354.6
381
407
407
421
381
380.92
380.92
373
389
414
346
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
BHC-b
BHC-d
BHC-g
Chlordane-trans
Chlordane-cis
4,4,DDD
4,4,DDE
4,4,DDT
Dieldrin
Endosulfan I
Endosulfan II
Endosulfan sulph.
Endrin
Endrin Aldehyde
Endrin Ketone
Heptachlor
Heptachlor epox.
Toxaphene
Methoxychlor
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
6CL-CHX-B
6CL-CHX-D
6CL-CHX-G
CHLORDAN-G
CHLORDAN-A
DDD
DDE
DDT
DIELDRIN
ENDOSLFN-A
ENDOSLFN-B
ENDOSLFN-S
ENDRIN
ENDRIN-ALD
ENDRIN-KETONE Endrin Ketone
HEPTACHLOR Heptachlor
HEPCL EPOX
TOXAPHENE
METHOXYCL
BENZOIC_AC
PCT_FINES
BARIUM
ANTIMONY
CALCIUM
COBALT
MAGNESIUM
POTASSIUM
SODIUM
VANADIUM
12-2CLETHE
2-BUTANONE
ACETONE
CHLOROFORM
METHYLE_CL
TOLUENE
3CLETHENE
CHLORDANE
ENDOSULFAN
THALLIUM
PCT_MOIS
PH
CYANIDE
ODD-SUM
DDE-SUM
Hexachlorocyclohexane-beta
Hexachlorocyclohexane-delta
Hexachlorocyclohexane-gamma
trans-chlordane
cis-chlordane
4,4DDD
4,4,DDE
4.4,DDT
Dieldrin
Endosulfan-alpha
Endosulfan-beta
Endosulfan sulphate
Endrin
Endrin Aldehyde
Heptachlor epoxide
Toxaphene
Methoxychlor
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
-------
-8
o
o
cn
o o o o o
O O O O O
o o o o o
I I I I I /—>
—i m r^ oo o\
o o o o o
I I I I I
o o o o o o U
i i i i i i t
o o o o
I I I I
o o o o
o o o o
I I I I f~\
m rr vo r~- x
o o o o U
—i (N m rf
0000
c\ o o o
»-<(Nt^'- 9J (U (U
> > > > >
1_ >-H t-l i-l i->
O O O O O
A i i i
OJ> > > >
2
Kt ^H ^H *-H >-H J-H
-------
Location name Letter Sample number Sample code
SaginawRiver-3 G 401 SR-3-CO
TabbsBay N 1102 TB-1-01
TabbsBay N 1103 TB-1-02
TabbsBay N 1104 TB-1-03
TabbsBay N 1105 TB-1-04
TabbsBay N 1101 TB-l-RE
Trinity River T 902 TR-1-01
Trinity River T 903 TR-1-02
Trinity River T 904 TR-1-03
Trinity River T 905 TR-1-04
Trinity River T 901 TR-l-CO
Upper Mississippi U 603 UM-1-01
Upper Mississippi U 604 UM-1-02
Upper Mississippi U 605 UM-1-03
Upper Mississippi U 601 UM-l-CO
Upper Mississippi U 602 UM-l-RE
Waukengan Harbor W 503 WH-1-01
Waukengan Harbor W 504 WH-1-02
Waukengan Harbor W 501 WH-l-CO
Waukengan Harbor W 502 WH-l-RE
-------
Appendix 3 a Summary of sediment effect concentrations (SECs) calculated using dry-weight
concentrations and listed by chemical, test type, and sample type for the entire
database.
NUMCODE
CHEMCODE
TEST
SAMPTYP
UNITS
SEC
C
N
TOX
EFFECT
HIT
TOTAL
CORRECT
TOXHIT
NOTNOT
NOTHIT
TOXNOT
Numerical code for chemical (Appendix 2c)
Chemistry code for chemical (Appendix 2c)
Toxicity test (HAM = Hyalella azeteca 14-d test; HA28 =
Hyalella azteca 28-d test; CR-14 = Chironomus riparius 14-d
test)
BT= total extraction of sediment; BS = weak acid digestion of
sediment (SEM metals); PW = pore water
Chemical concentrations
Sediment effect concentrations (NR = not reported)
An "x" indicates SECs which correctly classify <70% of the
samples correctly. An "@" indicates an unreliable SEC (e.g., less
than five of the samples were designated as toxic for the chemical
or the number of toxic samples with concentrations below the
SEC was greater than the number of toxic samples with
concentrations above the SEC).
Total number of samples used to calculate each SEC.
Number of toxic samples.
Number of toxic samples where the concentration of a chemical
was greater than the mean concentration of the chemical in the
non-toxic samples at a site.
Number of samples with concentrations greater than the SEC.
Percentage samples correctly classified as toxic.
Percentage of toxic samples correctly classified as toxic (toxic
sample and hit).
Percentage of non-toxic samples correctly classified as not toxic
(non-toxic sample and no hit).
Percentage of non-toxic samples incorrectly classified as toxic
(Type I error; non-toxic sample and hit [false positive]).
Percentage of toxic samples incorrectly classified as not toxic
(Type II error; toxic sample and no hit [false negative]).
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
101 TOC
101 TOC
101 TOC
102 AVS
102 AVS
102 AVS
104 CLAY
104 CLAY
104 CLAY
105 SAND
105 SAND
105 SAND
106 WATER
CR14 BT % ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
HA14 BT % ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
HA28 BT % ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
CR14 BT UM/G ERL
ERM
TEL X
PEL
NEC @
NERM X
NERH X
HA14 BT UM/G ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
HA28 BT UM/G ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
CR14 BT % NR X
HA14 BT % NR X
HA28 BT % NR X
CR14 BT % ERL X
ERM X
TEL X
PEL X
NEC @
NERM X
NERH X
HA14 BT * ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
HA28 BT % ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
CR14 BT % ERL X
ERM X
2.
5.
2,
4.
8.
1,
3.
1.
4.
1.
3.
4.
1.
3.
1.
3.
1.
3.
9.
1 .
3.
15.
33.
8.
20.
161
4
13
5
15
3
9
8
2
6
5
15
4
14
19
3
12
16
32
29
49
98
53
73
15
32
25
46
98
42
65
16
53
28
61
98
47
70
44
46
67 42
65 42
04 42
38 42
90 42
56 42
40 42
70 32
65 32
30 32
86 32
00 32
00 32
20 32
.70 62
.00 62
.49 €2
.29 62
.00 62
.30 62
.60 62
.50 37
.50 37
.26 37
.87 37
.00 37
.40 37
.00 37
.10 22
.60 22
.46 22
.67 22
.90 22
.35 22
.00 22
.70 42
.60 42
.27 42
.02 42
.20 42
.20 42
.60 42
23
13
38
.00 42
.95 42
.24 42
.11 42
.50 42
.45 42
.20 42
.60 32
.95 32
.60 32
.49 32
.50 32
.00 32
.60 32
.70 57
.45 57
.08 57
.26 57
.50 57
.20 57
.20 57
.10 42
.70 42
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
9
9
9
9
9
11
11
11
11
11
22
22
22
22
22
1
4
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
8
8
8
8
8
12
12
12
12
12
17
17
17
17
17
5
5
5
5
5
10
10
10
10
10
17
17
17
17
17
8
8
8
8
8
12
12
12
12
12
20
20
20
20
20
9
9
17
7
20
8
2
17
6
18
7
7
33
20
33
16
2
9
4
13
5
1
12
5
13
6
7
23
11
25
13
8
-
31
26
27
22
1
23
17
19
14
1
42
24
38
15
1
22
18
67
76
64
79
74
81
78
84
75
75
60
58
60
61
61
78
81
68
78
73
77
73
82
77
73
64
64
69
69
62
38
36
33
36
71
56
44
44
47
56
51
51
47
60
56
60
55
17
10
19
12
2
38
19
41
19
19
26
15
26
13
2
14
8
14
8
41
23
45
27
27
36
21
40
26
17
19
12
12
7
34
19
22
16
33
18
28
14
19
12
50
67
45
67
71
44
59
44
56
56
34
44
34
48
60
65
73
54
70
73
36
50
36
50
45
29
43
29
43
45
19
24
21
29
71
22
25
22
31
56
18
33
19
46
56
40
43
24
7
29
7
2
16
16
3
3
27
18
27
13
2
11
3
22
5
3
14
14
5
19
5
19
5
2
55
SO
52
45
2
38
34
38
28
3
40
25
39
12
2
33
31
10
17
7
14
24
3
22
22
22
13
24
13
26
37
11
16
11
16
24
9
27
5
23
23
17
31
12
26
36
7
14
14
19
26
6
22
19
25
41
9
25
14
28
42
7
14
-------
APPENDIX 3A:
NDMCODE CHEMCODE TEST SAMPTYP UNITS
SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
106
106
106
107
107
107
108
108
109
109
110
110
110
111
111
111
300
300
300
300
300
300
WATER
WATER
WATER
SILT
SILT
SILT
AFDW
AFDW
CEC
CEC
NH3P
NH3P
NH3P
HSP
HSP
HSP
AL
AL
AL
AL
AL
AL
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA28
CR14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
CR14
HA14
HA14
HA28
HA28
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BS
BT
BS
BT
%
%
fc
%
%
%
%
%
MEQ/KG
MEQ/KG
MG/L
MG/L
MG/L
MG/L
MG/L
MG/L
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
X
X
8
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
42
53
76
41
61
41
46
40
SO
76
39
55
44
54
42
54
85
40
55
12
15
12
14
15
13
14
0
0
0
0
0
0
0
0
0
0
0
0
0
0
13500000
58030000
25519404
59572012
.88
.50
.40
.70
.30
.70
.30
.43
.55
.40
.20
.20
.10
.00
.44
.60
.00
.85
.20
.70
.60
.85
.94
.20
.00
.30
.02
.27
.01
.10
.09
.01
.04
.02
.08
.01
.06
.14
.01
.05
•
-
-
.00
.00
.38
.30
42
42
42
42
42
32
32
32
32
32
32
32
57
57
57
57
57
57
57
23
13
38
15
15
15
15
15
15
15
15
IS
15
36
21
21
21
21
21
21
21
41
41
41
41
41
41
41
17
2
17
19
19
5
5
20
25
25
25
25
11
11
11
13
13
13
13
13
24
24
24
24
24
1
3
1
4
1
8
8
8
8
8
3
9
9
9
9
9
20
20
20
20
20
3
1
4
11
11
11
11
9
9
9
10
10
10
10
10
15
15
IS
15
IS
5
5
5
5
5
7
7
7
7
7
16
16
16
16
16
•
-
-
5
5
5
5
23
12
1
18
13
19
9
1
29
16
31
14
1
11
3
9
5
5
12
4
12
4
S
24
11
25
12
8
-
-
23
10
21
7
57
60
71
59
50
63
50
56
53
58
49
54
56
53
67
53
67
67
67
76
67
76
71
71
63
68
66
66
44
64
44
52
19
7
28
16
31
9
23
14
23
11
40
20
33
27
27
33
19
33
19
19
39
20
39
22
17
40
24
36
12
38
52
71
31
34
31
41
56
30
44
26
44
56
13
47
20
40
40
.
33
57
33
57
52
32
44
29
44
49
4
40
8
40
36
21
2
28
25
28
19
3
28
14
32
14
2
33
27
7
7
24
.
24
5
20
7
22
7
2
52
16
48
16
7
19
26
13
25
9
31
41
19
28
19
32
42
13
33
20
27
27
10
24
10
24
24
10
29
10
27
32
4
20
8
32
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE
300 AL
TEST SAMPTYP UNITS
HA28 BT NG/G
SEC C
# ft # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
NEC X 73160000.00 25 11
NERM X 48240000.00 25
52
302 ARSENIC
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
302 ARSENIC
UG/L
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
302 ARSENIC
BS
NG/G
302 ARSENIC
NG/G
302 ARSENIC
UG/L
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL
NEC
NERM X
NERH X
12100.00 32
33000.00 32
11244.78 32
39466.44 32
92900.00 32
10450.00 32
47200.00 32
1.70 21
2.30 21
1.37 21
1.92 21
2.30 21
1.10 21
1.60 21
7400.00 20
24800.00 20
3331.67 20
16365.82 20
23800.00 20
1500.00 20
10800.00 20
13100.00 52
49600.00 52
10797.68 52
48385.12 52
102000.00 52
8900.00 52
47200.00 52
X
X
303 CADMIUM
CR14
BS
NG/G
303 CADMIUM
CR14
BT
NG/G
ERL X
ERM X
TEL X
PEL X
NEC a
NERM X
NERH X
ERL
ERM
1.70 36
6.80 36
1.37 36
10.58 36
53.70 36
1.10 36
16.45 36
787.00 37
1405.00 37
514.99 37
1817.07 37
31300.00 37
337.00 37
2350.00 37
9100.00 42
11700.00 42
13
13
13
13
13
10
10
10
10
10
24
24
24
24
24
19
19
19
19
19
11
11
10
10
10
10
10
16
16
16
16
16
16
16
16
16
16
19
10
20
9
2
8
5
10
5
5
9
4
10
5
5
27
11
32
11
2
22
12
24
10
4
17
12
21
9
1
69
66
66
63
59
71
67
62
67
67
75
80
80
75
75
63
63
62
63
54
69
58
64
58
53
62
59
57
62
73
86
81
52
301 SILVER CR14
301 SILVER CR14
301 SILVER HA14
301 SILVER HA14
301 SILVER HA28
301 SILVER HA28
302 ARSENIC CR14
302 ARSENIC CR14
302 ARSENIC CR14
302 ARSENIC HA14
BT NG/G
PW UG/L
BT NG/G
PW UG/L
BT NG/G
PW UG/L
BS NG/G
BT NG/G
PW UG/L
BS NG/G
JNEKil
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
A t
X
X
X
X
X
X
X
X
X
X
@
X
X
X
X
>J.X^^UUU.UU ^3
19 2
16 ..
19 1
16 ..
19 2
16 ..
19 1
32000.00 42 11 6 20 60
57000.00 42 11 6 7 71
21762.35 42 11 6 22 55
54022.22 42 11 6 8 69
404000.00 42 11 6 1 71
14800.00 42 ..
51200.00 42 ..
35 3
5
17 43 31 10
7 64 10 19
17 38 36 10
7 62 12 19
71 2 26
17
7
17
7
34
19
34
16
3
29
19
29
19
19
30
20
35
20
20
31
15
35
15
2
42
22
42
19
8
16
8
19
5
14
10
43
64
38
62
71
34
47
31
47
56
43
48
33
48
48
45
60
45
55
55
33
48
27
48
52
28
36
22
39
44
46
51
38
57
73
71
71
31
10
36
12
2
25
13
28
13
3
10
5
19
5
5
15
15
5
5
21
6
27
6
2
19
11
25
8
3
30
24
38
19
3
2
2
10
19
10
19
26
6
22
6
25
38
19
29
19
29
29
10
20
5
20
20
IS
31
12
31
44
11
31
11
33
44
8
16
5
19
24
12
17
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
303 CADMIUM
303 CADMIUM
CR14
CR14
BT
NG/G
UG/L
303 CADMIUM
BS
NG/G
303 CADMIUM
BT
NG/G
303 CADMIUM
HA14
PW
UG/L
303 CADMIUM
HA28
NG/G
303 CADMIUM
HA28
NG/G
303 CADMIUM
HA28
PW
UG/L
304 CHROMIUM-T CR14
BS
NG/G
304 CHROMIUM-T CR14
NG/G
304 CHROMIUM-T CR14
UG/L
CONC
# # * TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL
ERM X
TEL
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
2893
6623
41100
920
3750
0
1
0
0
2
0
0
337.
1068
237
774
899.
167.
562
700.
5200.
591.
3224.
8000.
500.
2000.
0.
0.
0.
0.
0.
0.
0.
562.
1405.
314.
1494.
3870.
175.
1590.
700.
3875.
583.
3246.
8000,
486.
2720.
0.
1.
0.
0.
0.
0,
0.
3010.
31665.
2275,
10265.
14975.
1720.
3328.
39300.
363000.
39796.
159405.
312000
40300.
70000.
0.
18.
.44
.82
.00
.00
.00
.19
.05
.12
.52
.35
.08
.26
.00
.00
.23
.74
.00
.00
.00
.00
.00
.61
.90
.00
.00
.00
.10
.92
.09
.43
.20
.08
.20
.00
,00
.06
.64
.00
.50
.00
.00
.00
.27
.54
.00
.00
,00
.19
.05
.12
.46
.36
.08
.20
.00
.50
.35
.61
.00
.00
.00
.00
.00
.86
.14
.00
.00
.00
.40
.80
42
42
42
42
42
35
35
35
35
35
35
35
23
23
23
23
23
23
23
32
32
32
32
32
32
32
21
21
21
21
21
21
21
38
38
38
38
38
38
38
62
62
62
62
62
62
62
36
36
36
36
36
36
36
37
37
37
37
37
37
37
42
42
42
42
42
42
42
35
35
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
11
11
11
11
11
9
9
7
7
7
6
6
6
6
6
10
10
10
10
10
11
11
11
11
11
6
6
6
6
6
16
16
16
16
16
18
18
18
18
18
10
10
10
10
10
6
6
6
6
6
8
8
8
8
8
6
6
16
9
2
15
5
16
7
3
12
5
12
7
6
19
7
19
8
6
10
3
10
4
8
21
12
23
11
3
35
12
35
14
8
15
5
16
7
8
12
3
17
6
6
25
4
24
7
6
31
3
69
81
74
66
77
63
83
77
78
74
78
74
70
81
75
81
78
72
62
67
62
71
52
74
66
74
63
53
66
71
66
74
71
56
61
58
67
64
81
84
68
86
86
62
83
60
86
83
26
83
17
14
2
17
9
17
14
6
39
22
39
26
22
41
19
41
22
16
29
14
29
19
19
39
24
42
21
5
31
15
31
18
11
25
14
28
19
19
19
8
19
14
14
24
10
21
14
12
20
9
52
67
71
49
69
46
69
71
39
52
39
48
48
41
56
41
56
56
33
52
33
52
33
34
42
32
42
47
35
56
35
56
60
31
47
31
47
44
62
76
49
73
73
38
74
38
71
71
6
74
21
7
2
26
6
29
6
3
13
13
4
4
19
3
19
3
3
19
.
19
19
16
8
18
8
3
.
26
5
26
5
2
17
17
3
14
27
3
3
36
36
2
2
69
10
12
24
9
17
9
11
20
9
26
9
22
26
22
19
25
19
33
19
29
29
11
26
8
29
45
8
24
8
21
27
28
39
25
33
33
5
16
5
11
11
2
17
5
12
14
6
17
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP ONITS
304 CHROMIUM-T CR14 PK UG/L
304 CHROMIDM-T HA14
BS
NG/G
304 CHROMIUM-T HA14
BT NG/G
304 CHROMIUM-T HA14
PW
UG/L
304 CHROMIUM-T HA28
BS
NG/G
304 CHROMIUM-T HA28 BT NG/G
304 CHROMIUM-T HA28
PW
UG/L
305 COPPER
305 COPPER
CR14 BS NG/G
CR14 BT NG/G
305 COPPER
CR14
UG/L
30S COPPER
305 COPPER
HA14 BS NG/G
HA14 BT NG/G
SEC
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
«
X
X
X
X
X
X
X
X
CONC
0
3
2
0
0
14975
22254
4499
6059
2184
1352
1650
56000
293000
47916
130921
95000
41000
58500
2
13
1
3
2
0
0
1820
3328
1732
3052
4450
1650
2800
38500
274000
36286
119364
95000
34200
52000
0
7
0
2
2
0
0
96500
206500
67453
291327
7820000
47150
411000
5
20
4
17
102
4
15
41300
122250
28012
77711
54800
19000
.47
.88
.50
.55
.80
.00
.00
.58
.63
.00
.00
.00
.00
.00
.59
.73
.00
.00
.00
.46
.20
.28
.45
.50
.67
.90
.00
.00
.92
.61
.00
.00
.00
.00
.00
.36
.99
.00
.00
.00
.80
.85
.62
.33
.50
.48
.69
.00
.00
.50
.14
.00
.00
.00
.30
.60
.98
.64
.00
.68
.10
.00
.00
.50
.97
.00
.00
N TOX EFFECT
35
35
35
35
35
23
23
23
23
23
23
23
32
32
32
32
32
32
32
21
21
21
21
21
21
21
38
38
38
38
38
38
38
62
62
62
62
62
62
62
36
36
36
36
36
36
36
37
42
42
42
42
42
42
42
35
35
35
35
35
35
35
23
32
32
32
32
32
32
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
4
11
11
11
11
11
9
9
9
9
9
3
13
13
13
13
13
6
6
6
7
7
7
7
7
12
12
12
12
12
7
7
7
7
7
15
15
15
15
15
13
13
13
13
13
8
8
8
8
8
8
8
8
8
8
6
6
6
6
6
12
12
12
12
12
HIT C
21
4
g
6
4
6
6
8
15
6
20
7
9
7
4
8
4
6
21
10
21
10
8
31
7
31
7
9
10
4
19
7
6
18
13
18
10
1
16
6
16
8
2
15
6
16
7
9
ORREC
49
86
80
78
70
78
78
78
81
78
66
81
81
76
71
71
71
71
68
66
68
66
66
60
73
60
73
73
58
58
39
61
58
64
62
64
60
71
63
74
63
80
74
81
78
84
81
81
17
11
11
26
17
26
26
30
34
19
34
22
25
29
19
29
19
24
37
21
37
21
18
24
11
24
11
13
19
11
22
17
14
17
10
17
5
17
9
17
14
3
34
19
38
22
25
31
74
69
52
52
52
52
48
47
59
31
59
56
48
52
43
52
48
32
45
32
45
47
35
61
35
61
60
39
47
17
44
44
48
52
48
55
71
46
66
46
66
71
47
59
47
59
56
43
6
4
13
28
3
5
10
5
18
5
18
5
3
26
26
2
8
31
3
3
26
21
26
19
2
29
9
29
9
3
13
13
3
9
14
14
22
30
22
22
17
6
22
6
19
16
19
29
19
29
24
13
29
13
29
32
15
27
15
27
26
33
42
31
36
39
10
17
10
21
26
9
17
9
11
23
6
22
3
19
16
-------
APPENDIX 3A: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
:ODE CHEMCODE TEST SAMPTYP UNITS
305 COPPER HA14 BT NG/G
305 COPPER HA14 PW UG/L
305 COPPER HA28 BS NG/G
305 COPPER HA28 BT NG/G
305 COPPER HA28 PW UG/L
306 IRON CR14 BS %
306 IRON CR14 BT %
306 IRON HA14 BS %
306 IRON HA14 BT %
306 IRON HA28 BS *
306 IRON HA28 BT %
307 MERCURY CR14 BT NG/G
307 MERCURY CR14 PW UG/L
307 MERCURY HA14 BT NG/G
307 MERCURY HA14 PW UG/L
307 MERCURY HA28 BT NG/G
SEC
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
49400.
5.
19.
3.
9.
4.
2.
4.
16965.
209000.
9248.
50079.
325000.
5042.
12000.
41300.
187000.
28012.
101230.
583000.
19000.
54800.
5.
19.
4.
13.
35.
3.
8.
5.
8.
3.
7.
18.
2.
5.
3.
5.
2.
3.
2.
1.
2.
5.
7.
3.
5.
7.
2.
4.
19.
28.
18.
24.
28.
18.
21.
00
30
80
89
63
68
85
68
00
00
65
94
00
00
00
00
00
50
43
00
00
00
30
80
43
16
60
70
75
31
49
81
04
47
74
84
57
81
19
99
74
34
74
19
15
77
71
31
74
56
70
00
84
76
99
02
89
N
32
21
21
21
21
21
21
21
38
38
38
38
38
38
38
52
52
52
52
52
52
52
36
36
36
36
36
36
36
31
31
31
31
31
31
31
31
17
17
17
17
17
17
17
17
32
32
32
32
32
32
32
37
37
37
37
37
37
37
19
16
19
16
19
TOX EFFECT HIT CORREl
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
3
10
10
10
10
10
2
19
19
19
19
19
.
22
22
22
22
22
1
2
1
1
3
5
5
5
5
5
10
10
10
10
10
21
21
21
21
21
11
11
11
11
11
•
5
5
5
S
5
5
5
5
5
5
8
8
8
8
8
•
7
7
7
7
7
5
3
10
4
10
13
7
22
11
4
26
14
29
17
3
16
7
22
11
5
9
4
12
5
1
5
3
10
4
10
-
10
5
12
8
5
14
5
14
£
3
76
67
52
71
52
63
58
50
58
SB
73
69
71
71
56
64
61
47
67
56
74
77
65
74
68
71
59
41
65
41
53
50
59
47
50
57
49
57
46
43
24
14
24
19
24
24
13
29
18
8
35
21
37
25
4
31
17
31
25
11
16
10
16
10
29
18
29
24
29
22
13
28
16
13
27
11
27
11
5
52
52
29
52
29
39
45
21
39
47
38
48
35
46
52
33
44
17
42
44
58
68
48
65
68
41
41
12
41
12
31
38
31
31
38
30
38
30
35
38
24
24
11
5
29
11
3
15
6
19
8
2
14
3
31
6
3
13
3
23
6
3
29
29
9
3
9
9
3
11
3
11
5
3
24
33
24
29
24
26
37
21
32
42
12
25
10
21
42
22
36
22
28
42
13
19
13
19
29
29
41
29
35
29
38
47
31
44
47
32
49
32
49
54
-------
APPENDIX 3A: SUMMARY OF SECs NORM. - IZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
307 MERCURY HA28 PW UG/L
308 MANGANESE CR14 BS NG/G
308 MANGANESE CR14 BT NG/G
308 MANGANESE HA14 BS NG/G
308 MANGANESE HA14 BT NG/G
308 MANGANESE HA28 BS NG/G
308 MANGANESE HA28 BT NG/G
309 NICKEL
CR14
BS NG/G
309 NICKEL
CR14
BT NG/G
309 NICKEL
CR14
UG/L
309 NICKEL
BS NG/G
309 NICKEL
BT NG/G
309 NICKEL
HA14
PW UG/L
SEC
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
C
X
X
@
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
1673000
2410000
1079077
1S38382
4460000
696000
982000
726000
1678000
614721
1080688
819000
520500
696000
726000
1673000
631327
1184756
4460000
549000
839000
4873
7010
4038
5419
8160
3347
4190
40000
47500
26608
38681
57000
17700
31500
5
10
4
7
20
4
4
4873
6693
2829
5282
4170
1643
4170
39600
47500
27717
38496
37900
19400
31200
5
10
4
6
4
4
4
.00
.00
.38
.27
.00
.00
.00
.00
.00
.89
.67
.00
.00
.00
.00
.00
.17
.09
.00
.00
.00
.00
.00
.86
.58
.00
-SO
.00
.00
.00
.27
.39
.00
.00
.00
.80
.40
.82
.14
.30
.00
.90
.00
.00
.98
.97
.00
.50
.00
.00
.00
.14
.75
.00
.00
.00
.80
.40
.82
.99
.90
.00
.70
H
16
37
38
38
38
38
38
38
38
23
24
24
24
24
24
24
24
38
44
44
44
44
44
44
44
37
37
37
37
37
37
37
42
42
42
42
42
42
42
35
35
35
35
35
35
35
23
23
23
23
23
23
23
32
32
32
32
32
32
32
21
21
21
21
21
21
21
TOX EFFECT HIT CORREi
3 ...
1
9
9
9
9
9
11
11
11
11
11
4
22
22
22
22
22
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
5
5
5
5
5
8
8
8
8
8
11
11
11
11
11
5
5
5
5
5
10
10
10
10
10
5
5
5
5
5
5
5
5
5
5
12
12
12
12
12
5
5
5
5
5
8
5
9
8
1
9
4
15
5
6
18
8
26
9
1
8
4
18
6
3
10
6
17
11
4
7
4
10
4
3
5
3
11
4
10
11
6
17
11
12
5
3
7
3
7
.
82
79
79
82
74
83
71
67
75
71
68
59
59
61
48
81
81
54
81
78
93
83
76
90
79
83
80
74
80
77
74
65
57
70
52
94
78
81
94
91
76
67
67
67
67
13
8
13
13
33
17
38
21
21
30
14
34
16
14
8
14
11
5
21
12
21
21
7
14
9
14
9
6
22
13
26
17
22
34
19
38
34
34
24
14
24
14
24
68
71
66
68
74
50
54
29
54
SO
39
45
25
45
48
68
73
41
70
73
71
71
55
69
71
69
71
60
71
71
52
52
30
52
30
59
59
44
59
56
52
52
43
52
43
8
5
11
8
3
4
25
4
11
5
25
5
2
8
3
35
5
3
2
2
19
5
2
6
3
14
3
3
22
22
16
3
10
10
11
16
11
11
24
13
29
8
25
25
20
36
16
34
50
11
16
11
14
19
5
14
5
5
19
11
17
11
17
20
26
35
22
30
26
6
22
3
6
6
24
33
24
33
24
-------
APPENDIX 3A: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE
309 NICKEL
TEST SAMPTYP UNITS
HA28 BS NG/G
SEC C
309 NICKEL
HA28
BT NG/G
309 NICKEL
HA28
PW
UG/L
310 LEAD
BS
NG/G
310 LEAD
CR14
BT NG/G
310 LEAD
CR14
PW
UG/L
310 LEAD
BS
NG/G
310 LEAD
NG/G
310 LEAD
HA14
PW
UG/L
310 LEAD
HA28
BS NG/G
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC @
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL
PEL
NEC X
NERM X
NERH X
6517
7010
4630
5406
5230
3290
4170
23800
44700
19514
32821
43000
16000
24100
5
10
4
6
6
4
4
10360
81115
11009
62786
569000
11700
48600
99000
396000
69649
191803
679000
49000
92900
0
62
0
14
5
0
3
13882
59878
10658
26468
11700
8184
11700
51000
251000
34174
117494
68700
22900
55000
0
5
0
4
4
0
3
32000
55000
17079
32664
62400
9116
19400
.00
.00
.44
.63
.00
.00
.00
.00
.00
.10
.79
.00
.00
.00
.80
.40
.82
.99
.10
.00
.70
.00
.00
.63
.85
.00
.00
.00
.00
.00
.12
.02
.00
.00
.00
.90
.85
.60
.83
.70
.40
.50
.00
.00
.81
.33
.00
.00
.00
.00
.00
.55
.68
.00
.00
.00
.70
.50
.70
.39
.10
.70
.50
.00
.00
.58
.97
.00
.00
.00
38
38
38
38
38
38
38
62
62
62
62
62
62
62
36
36
36
36
36
36
36
37
37
37
37
37
37
37
42
42
42
42
42
42
42
35
35
35
35
35
35
35
23
23
23
23
23
23
23
32
32
32
32
32
32
32
21
21
21
21
21
21
21
38
38
38
38
38
38
38
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
7
7
7
7
7
14
14
14
14
14
7
7
7
7
7
6
6
6
6
6
7
7
7
7
7
6
6
6
6
6
7
7
7
7
7
11
11
11
11
11
10
10
10
10
10
13
13
13
13
13
6
4
8
6
7
20
7
24
14
9
7
4
10
4
5
24
4
23
4
1
10
5
18
7
3
14
3
19
4
5
6
4
11
5
11
14
6
16
6
10
16
5
16
6
7
IS
8
16
14
S
66
61
66
66
63
68
73
65
74
73
61
58
58
58
56
49
81
46
81
73
83
81
74
81
76
74
83
71
86
83
78
70
57
74
57
78
78
84
78
84
71
76
71
81
76
74
66
71
71
58
16
11
18
16
16
19
11
21
18
13
17
11
19
11
11
•
19
8
16
8
17
10
21
12
5
20
9
26
11
11
26
17
26
22
26
31
19
38
19
28
48
24
48
29
29
32
18
32
29
11
50
50
47
50
47
48
61
44
56
60
44
47
39
47
44
30
73
30
73
73
67
71
52
69
71
54
74
46
74
71
52
52
30
52
30
47
59
47
59
56
24
52
24
52
48
42
47
39
42
47
3
3
13
18
5
2
3
8
3
46
3
46
3
3
7
2
21
5
2
20
29
3
22
22
13
13
3
29
29
5
8
3
11
8
3
34
39
32
34
34
19
27
18
21
26
36
42
33
42
42
5
16
8
16
24
10
17
5
14
21
6
17
14
14
22
30
22
26
22
9
22
3
22
13
24
19
19
18
32
18
21
39
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE
310 LEAD
TEST SAMPTYP UNITS
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
HA28
NG/G
310 LEAD
HA28
PW
UG/L
311 SELENIUM
311 SELENIUM
311 SELENIUM
312 ZINC
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
CR14 BS NG/G
312 ZINC
CR14
BT NG/G
312 ZINC
PW
UG/L
312 ZINC
BS
NG/G
312 ZINC
NG/G
312 ZINC
HA14
PW UG/L
312 ZINC
HA28
BS NG/G
312 ZINC
HA28
BT NG/G
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
@
X
X
X
X
@
X
X
X
X
3
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
S5000.
98700.
37229.
81743.
127000.
2S200.
67700.
0,
0.
0,
1.
4.
0.
3.
12747.
107991.
133S8.
270987.
8873000.
14000.
680000.
381000
2750000
280832.
1532481
10090000.
207000
854000.
6.
55
4
52.
2630.
3.
50.
12747.
84066.
11901.
34306.
17388.
11113.
14000.
159000.
422000.
94150
384042
541000
55750
349500
6
49
3
13
10
1
3
65893
408000
30372
346340
1064000
14000
294000
113000
547000
.00
.00
.02
.44
.00
.00
,00
.70
.90
.46
.77
.10
.30
.50
.00
.50
.82
.49
.00
.00
.00
.00
.00
.69
.65
.00
.00
.00
.30
.20
.96
.90
.00
.90
.70
.00
.00
.99
.33
.00
.00
.00
.00
.00
.15
.97
.00
.00
.00
.30
.60
.37
.91
.70
.80
.90
.00
.00
.72
.87
.00
.00
.00
.00
.00
62
62
62
62
62
62
62
36
36
36
36
36
36
36
19
19
19
37
37
37
37
37
37
37
42
42
42
42
42
42
42
35
35
35
35
35
35
35
23
23
23
23
23
23
23
32
32
32
32
32
32
32
21
21
21
21
21
21
21
38
38
38
38
38
38
38
62
62
24
24
24
24
24
19
19
19
19
19
2
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
24
24
19
19
19
19
19
15
15
15
15
15
6
6
6
6
6
8
8
8
8
8
6
6
6
6
6
6
6
6
6
6
12
12
12
12
12
5
5
5
5
5
11
11
11
11
11
20
20
26
12
32
18
8
19
14
19
10
7
26
13
25
12
1
18
5
23
6
1
19
7
19
7
1
12
3
13
4
6
17
7
20
7
6
6
3
11
4
5
15
10
15
10
3
37
16
74
74
71
77
71
67
58
67
53
61
38
57
35
54
73
64
81
57
83
71
54
71
54
71
71
52
65
48
70
70
81
75
78
75
72
71
67
48
71
67
68
61
68
61
53
63
74
16
14
5
17
10
19
12
17
9
17
9
26
13
26
17
22
38
19
41
19
16
24
14
24
19
19
29
18
29
18
5
31
19
22
49
22
49
73
48
71
38
71
71
37
63
37
63
71
26
52
22
52
48
44
56
38
56
56
48
52
24
52
48
39
42
39
42
47
32
55
54
27
54
27
3
26
2
36
2
2
37
11
37
11
3
26
30
4
16
3
22
3
3
5
29
5
11
8
11
8
3
29
6
8
16
11
19
24
10
17
7
14
26
9
17
9
17
26
22
35
22
30
26
3
22
22
25
24
33
24
29
29
21
32
21
32
45
8
19
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
:ODE
312
312
313
313
313
314
314
314
315
315
315
316
316
316
399
399
399
401
401
401
402
402
402
403
403
403
404
404
404
CHEMCODE
ZINC
ZINC
METHYL -HG
METHYL -HG
METHYL -HG
TBT
TBT
TBT
DBT
DBT
DBT
MET
MET
MET
SEMAVS
SEMAVS
SEMAVS
14-2CLBN2
14-2CLBNZ
14-2CLBNZ
12-2CLBNZ
12-2CLBNZ
12-2CLBNZ
13-2CLBNZ
13-2CLBNZ
13-2CLBNZ
NAPHTHALENE
TEST
HA28
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
NAPHTHALENE HA14
NAPHTHALENE HA28
SAMPTYP
BT
PW
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
UNITS
NG/G
UG/L
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
SEC
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
.NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
8
X
X
X
X
X
X
CONC
98091.
543991.
1300000.
85150.
541000.
19.
121.
8.
59.
166.
3.
29.
-
55.
1890.
34.
687.
20000.
21.
250.
55.
325.
32.
285.
290.
19.
250.
13.
97.
54
73
00
00
00
00
90
61
66
00
90
20
00
00
39
39
00
SO
00
00
00
75
04
00
50
00
00
50
N
62
62
62
62
62
36
36
36
36
36
36
36
12
12
12
12
12
12
12
12
12
12
12
12
31
18
31
19
19
19
7
7
7
7
7
7
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT T
24 20 39 63 32 31 31
24 20 16 74 19 55 6
24 20 7 69 10 60 2
.
19 8 14 64 28 36 11
19 8 6 53 11 42 6
19 8 18 64 33 31 17
19 8 7 56 14 42 6
19 8 5 56 11 44 3
1 ...
1 ...
3 ...
2 ...
1 ...
1 ...
3 ...
4 ...
4 ...
2 ...
1 ...
3 ...
.
.
11 8 18 79 24 55 19
11 8 5 81 10 71 2
11 8 21 76 26 50 24
11 8 5 81 10 71 2
11 8 1 71 .71 2
13 12 18 78 38 41 19
13 12 6 78 19 59
13 12 20 78 41 38 22
13 12 7 75 19 56 3
13 12 7 75 19 56 3
24 18 46 55 34 21 40
24 18 18 61 15 47 15
OXNO'
6
19
29
25
42
19
39
42
2
17
17
26
3
22
22
22
5
24
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
404 NAPHTHALENE HA28 BT
405 2-METHNAP CR14 BT
405 2-METHNAP HA14 BT
405 2-METHNAP HA28 BT
406 ACENA CR14 BT
406 ACENA HA14 BT
406 ACENA HA28 BT
407 DIBNZFURAN CR14 BT
407 DIBNZFURAN HA14 BT
407 DIBNZFURAN HA28 BT
408 FLUORENE CR14 BT
408 FLUORENE HA14 BT
408 FLUORENE HA28 BT
409 PHENANTHRN CR14 BT
409 PHENANTHRN HA14 BT
409 PHENANTHRN HA28 BT
410 ANTHRACENE CR14 BT
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
14.65 62
139.64 62
1400.00 62
16.50 62
200.00 62
19
19
19
23
13
38
19
19
19
88.00 42
1700.00 42
29.66 42
651.92 42
1800.00 42
10.00 42
250.00 42
50.00 32
595.00 32
34.64 32
385.68 32
290.00 32
24.00 32
250.00 32
10.00 62
140.00 62
10.00 62
149.67 62
3000.00 62
10.00 62
160.00 62
350.00 42
2250.00 42
95.39 42
1142.37 42
6100.00 42
26.00 42
580.00 42
390.00 32
1100.00 32
197.48 32
777.82 32
J.000.00 32
100.00 32
550.00 32
27.00 62
345.00 62
18.73 62
409.05 62
20000.00 62
13.00 62
485.00 62
140.00 42
1250.00 42
37.42 42
547.72 42
1700.00 42
10.00 42
240.00 42
24
24
24
1
1
3
2
2
3
1
1
3
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
18
18
18
7
7
7
7
7
12
12
12
12
12
15
15
15
IS
15
8
8
8
8
8
13
13
13
13
13
22
22
22
22
22
8
8
8
8
8
43
17
6
16
5
20
6
4
19
6
21
7
8
58
16
58
15
3
17
5
21
6
4
17
7
21
8
8
36
19
38
17
2
16
5
20
6
4
56
63
68
74
81
74
83
79
75
78
75
81
78
42
61
42
60
63
81
81
71
83
79
81
81
75
78
78
65
66
68
63
61
74
81
74
83
79
32
15
8
19
10
24
12
7
38
19
41
22
22
37
13
37
11
3
24
10
24
12
7
38
22
41
22
22
31
18
34
15
2
19
10
24
12
7
24
48
60
55
71
50
71
71
.
38
59
34
59
56
S
48
5
48
60
57
71
48
71
71
44
59
34
56
56
34
48
34
48
60
55
71
50
71
71
37
13
2
19
2
24
2
2
22
25
3
56
13
56
13
2
17
2
26
2
2
16
25
3
3
27
13
27
13
2
19
2
24
2
2
6
24
31
7
17
2
14
19
3
22
19
19
2
26
2
27
35
2
17
2
14
19
3
19
19
19
8
21
5
24
37
7
17
2
14
19
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
12
NUMCODE CHEMCODE TEST SAMPTYP UNITS
410 ANTHRACENE HA14 BT NG/G
SEC C
410 ANTHRACENE HA28
BT
NG/G
411 FLUORANTHN CR14
BT
NG/G
411 FLUORANTHN HA14 BT NG/G
411 FLUORANTHN HA28
BT
NG/G
412 PYRENE
CR14
BT
NG/G
412 PYRENE
HA14
BT
NG/G
412 PYRENE
BT NG/G
413 BAA
BT
NG/G
413 BAA
BT
NG/G
# # # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
100.00 32
670.00 32
31.62 32
409.27 32
290.00 32
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
13
13
13
13
13
12
12
12
12
12
18
6
20
6
7
78
78
78
78
75
38
19
41
19
19
41
59
38
59
56
19
22
3
3
22
22
22
10.00 32 ....
250.00 32 ....
10.00 62
140.00 62
10.00 62
167.33 62
2000.
10.
200.
110.
2900.
64.
1484.
7500.
37.
760.
160.
1200.
144.
834.
1200.
130.
580.
33.
175.
31.
318.
10000.
30.
580.
120.
3225.
67.
1684.
6100.
38.
880.
570.
1100.
231.
908.
1800.
94.
750.
40.
347.
44.
493.
9000.
49.
700.
300.
4200.
75.
1194.
3500.
19.
340.
260.
490.
103.
363.
690.
41.
270.
00 62
00 62
00 62
00 42
00 42
23 42
59 42
00 42
50 42
00 42
00 32
00 32
22 32
27 32
00 32
00 32
00 32
00 62
00 62
46 62
59 62
00 62
00 62
00 62
00 42
00 42
53 42
64 42
00 42
00 42
00 42
00 32
00 32
47 32
30 32
00 32
00 32
00 32
00 62
50 62
27 62
20 62
00 62
00 62
00 62
00 42
00 42
50 42
99 42
00 42
00 42
00 42
00 32
00 32
25 32
73 32
00 32
00 32
00 32
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
.
17
17
17
17
17
8
8
8
e
8
13
13
13
13
13
20
20
20
20
20
8
8
8
8
8
13
13
13
13
13
22
22
22
22
22
7
7
7
7
7
13
13
13
13
13
56
18
56
15
4
23
5
24
6
4
21
8
21
10
8
37
24
37
21
3
.
22
5
23
7
4
17
8
20
10
7
39
22
36
21
4
13
4
21
5
5
15
8
20
10
6
45
61
45
63
65
67
81
69
S3
79
69
78
69
84
78
56
55
56
56
63
69
81
67
81
79
81
78
72
78
75
60
61
55
63
65
-
81
83
67
81
81
88
78
72
78
72
37
IS
37
13
5
24
10
26
12
7
38
22
38
28
22
27
16
27
15
3
24
10
24
12
7
38
22
38
25
19
31
18
26
18
5
19
10
21
10
10
38
22
38
25
16
8
47
8
50
60
43
71
43
71
71
31
56
31
56
56
.
29
39
29
42
60
45
71
43
69
71
44
56
34
53
56
.
29
44
29
45
60
62
74
45
71
71
50
56
34
53
56
S3
15
53
11
2
31
2
31
2
2
28
3
28
3
3
32
23
32
19
2
29
2
31
5
2
16
3
25
6
3
32
18
32
16
2
12
29
2
2
9
3
25
6
3
2
24
2
26
34
2
17
14
19
3
19
3
13
19
11
23
11
24
35
2
17
2
14
19
3
19
3
16
22
8
21
13
21
34
7
17
5
17
17
3
19
3
16
25
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
13
NUMCODE CHEMCODE TEST SAMPTYP UNITS SEC C
CONC
# f # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
413 BAA HA28 BT NG/G
414 CHRYSENE CR14 BT NG/G
414 CHRYSENE HA14 BT NG/G
414 CHRYSENE HA28 BT NG/G
415 BBF CR14 BT NG/G
415 BBF HA14 BT NG/G
415 BBF HA28 BT NG/G
416 BKF CR14 BT NG/G
416 BKF HA14 BT NG/G
416 BKF HA28 BT NG/G
417 BAP CR14 BT NG/G
417 BAP HA14 BT NG/G
417 BAP HA28 BT NG/G
418 ICDP CR14 BT NG/G
418 ICDP HA14 BT NG/G
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
19.00
300.00
15.72
284.60
3000.00
13.00
270.00
500.00
5200.00
122.47
1512.61
4000.00
30.00
440.00
330.00
690.00
135.94
551.00
600.00
56.00
440.00
30.00
500.00
26.83
406.20
3000.00
24.00
330.00
210.00
8500.00
51.23
1724.82
5800.00
12.50
350.00
350.00
620.00
119.79
393.70
440.00
41.00
250.00
84.00
465.00
32.40
319.84
1000.00
12.50
220.00
30.00
2800.00
17.32
836.66
3800.00
10.00
250.00
78.00
410.00
86.53
326.50
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
19
19
19
19
19
19
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
4
1
1
4
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
19
19
19
19
19
7
7
7
7
7
13
13
13
13
13
17
17
17
17
17
6
6
6
6
6
11
11
11
11
11
14
14
14
14
14
8
8
8
8
8
12
12
12
12
38
16
39
16
6
10
4
19
5
5
16
7
21
9
9
36
11
38
16
6
18
3
20
5
5
11
6
19
10
10
25
8
31
12
6
23
5
23
5
5
21
6
20
6
55
68
56
68
68
88
83
71
81
81
84
81
69
81
81
52
73
52
68
68
74
81
69
81
81
88
78
75
84
84
60
71
53
71
68
67
81
67
81
81
69
78
66
78
27
16
29
16
8
19
10
21
10
10
38
22
38
25
25
24
15
26
16
8
21
7
21
10
10
31
19
38
28
28
19
11
21
IS
8
24
10
24
10
10
38
19
34
19
27
52
27
52
60
69
74
50
71
71
47
59
31
56
56
27
58
26
52
60
52
74
48
71
71
56
59
38
56
56
40
60
32
56
60
43
71
43
71
71
31
59
31
59
34
10
34
10
2
5
24
2
2
13
28
3
3
34
3
35
10
2
21
26
2
2
3
22
3
3
21
2
29
5
2
31
2
31
2
2
28
28
11
23
10
23
31
7
17
5
17
17
3
19
3
16
16
15
24
13
23
31
5
19
5
17
17
9
22
3
13
13
19
27
18
24
31
2
17
2
17
17
3
22
6
22
-------
APPENDIX 3A: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
418 ICDP HA14 BT NG/G
SEC C
# f # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
418 ICDP
HA28 BT NG/G
419 BGHIP CR14 BT NG/G
419 BGHIP HA14 BT NG/G
419 BGHIP HA28 BT NG/G
NEC
NERM
NERH
EEL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
290
96
260
30
250
17
239
770
10
230
290
6300
74
1279
3800
19.
260
91.
460
89.
349
310
88.
265
13.
275.
15.
251
1200.
18.
230
.00 32
.00 32
.00 32
.00 SI
.00 57
.32 57
.79 57
.00 57
.00 57
.00 57
.00 42
.00 42
.23 42
.84 42
.00 42
.00 42
.00 42
.00 32
.00 32
.49 32
.14 32
.00 32
.00 32
.00 32
.00 62
.00 62
.51 62
.50 62
.00 62
.50 62
.00 62
13
21
21
21
21
21
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
12
15
15
15
15
15
7
7
7
7
7
12
12
12
12
12
18
18
18
18
18
9
32
14
33
14
6
10
4
19
5
5
21
6
21
6
7
40
11
38
14
6
75
56
67
54
67
70
83
83
71
81
81
69
78
69
78
75
52
73
52
71
68
22
25
14
25
14
9
17
10
21
10
10
38
19
38
19
19
27
15
26
16
S
53
32
53
30
53
61
67
74
50
71
71
31
59
31
59
56
24
58
26
55
60
6
32
11
33
11
2
7
24
2
2
28
28
3
37
3
35
6
2
19
12
23
12
23
28
10
17
5
17
17
3
22
3
22
22
11
24
13
23
31
420 BBKF CR14 BT NG/G
420 BBKF HA14 BT NG/G
420 BBKF HA28 BT NG/G
23
13
ERL
ERM
TEL
PEL
NEC
NERM
NERH
X
X
X
X
X
X
X
37
71.
27
157.
4000.
20
350.
.00 43
.00 43
.20 43
.64 43
.00 43
.00 43
.00 43
13
13
13
13
13
6
6
6
6
6
19
14
19
10
1
.
53
51
53
56
67
14
7
14
5
40
44
40
51
67
30
26
30
19
2
16
23
16
26
30
421 ACENAPTYLE CR14 BT NG/G
421 ACENAPTYLE HA14
421 ACENAPTYLE HA28
422 DBA CR14
422 DBA HA14
422 DBA HA28
NR
30
BT NG/G NR
BT NG/G NR
BT NG/G NR
BT NG/G NR
BT NG/G ERL
ERM
TEL
PEL
NEC
NERM
NERH
X
X
X
X
X
X
X
X
X
X
X
10
15
10
28
870
10
53
.00
.00
.00
.20
.00
.00
.00
20
45
23
13
43
43
43
43
43
43
43
2
2
2
2
13
13
13
13
13
6
6
6
6
6
-
40
12
40
3
1
37
56
37
56
67
30 7
7 49
30 7
2 53
67
63
21
63
16
2
23
28
30
423 4-METHNAP CR14 BT NG/G
423 4-METHNAP HA14 BT NG/G
423 4-METHNAP HA28 BT NG/G
450 PAH-T CR14 BT NG/G
NR
NR X
NR X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
1297
33819
588
13660
84600
267
5518
.00
.00
.47
.65
.00
.00
.00
7
7
42
42
42
42
42
42
42
-
11
11
11
11
11
8
8
8
8
8
-
20
5
23
5
4
.
74
81
67
81
79
24
10
24
10
7
50
71
43
71
71
24
2
31
2
2
2
17
2
17
19
-------
APPENDIX 3A: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRES USING ALL DATA
NUMCODE CHEMCODE
450 PAH-T
TEST SAMPTYP UNITS
HA14 BT NG/G
SEC C
450 PAH-T
HA28
BT
NG/G
451 PAH-L
CR14
BT NG/G
451 PAH-L
BT
NG/G
451 PAH-L
HA28
BT
NG/G
452 PAH-H
NG/G
452 PAH-H
BT
NG/G
452 PAH-H
HA28
NG/G
508 PCB-T
508 PCB-T
508 PCB-T
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
NR
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
3553
8498
1589
6736
9240
711
5340
240
2226
264
3368
62220
290
5095
653
7204
231
4140
33600
82
2380
786
3369
387
2919
3040
191
2530
80
653
76
1176
29380
73
2120
486
26614
309
10122
51000
197
3850
2900
5650
1228
4353
6200
520
3355
170
1747
192
2338
32840
219
3130
.00
.00
.40
.42
.00
.00
.00
.00
.50
.05
. 09
.00
.50
.00
.00
.50
.40
.86
.00
.00
.00
.00
.00
.46
.52
.00
.00
.00
.00
.00
.42
.59
.00
.00
.00
.00
.50
.81
.54
.00
.50
.00
.00
.00
.01
.82
.00
.00
.00
.00
.00
.95
.40
.00
.00
.00
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
13
13
13
13
13
22
22
22
22
22
8
8
8
8
8
13
13
13
13
13
21
21
21
21
21
8
8
8
8
8
13
13
13
13
13
22
22
22
22
22
18
8
21
9
7
41
24
38
20
5
19
5
20
5
3
18
7
21
8
8
37
21
37
16
4
23
5
23
5
4
16
8
21
10
7
42
24
38
23
6
78
78
69
81
75
56
58
55
61
66
76
81
74
81
76
78
81
75
78
78
63
63
63
61
65
67
81
67
81
79
84
78
69
84
75
55
58
52
60
68
38
22
38
25
19
31
18
27
16
6
24
10
24
10
5
38
22
41
22
22
31
18
31
13
5
24
10
24
10
7
38
22
38
28
19
31
18
26
18
8
41
56
31
56
56
26
40
27
45
60
52
71
50
71
71
41
59
34
56
56
32
45
32
48
60
43
71
43
71
71
47
56
31
56
56
24
40
26
42
60
19
3
28
3
3
35
21
34
16
2
21
2
24
2
2
19
25
3
3
29
16
29
13
2
31
2
31
2
2
13
3
28
3
3
37
21
35
19
2
3
19
3
16
22
8
21
11
23
32
2
17
2
17
21
3
19
19
19
8
21
8
26
34
2
17
2
17
19
3
19
3
13
22
8
21
13
21
31
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
50.
730.
31.
244.
194.
20.
82.
.00
.00
,62
.66
.00
.00
.00
29
29
29
29
29
29
29
10
10
10
10
10
5
5
5
5
5
9
3
9
3
4
69
76
69
76
72
17
10
17
10
10
52
66
52
66
62
14
14
3
17
24
17
24
24
-------
Appendix 3b Summary of sediment effect concentrations (SECs) calculated using dry-weignt
concentrations and listed by chemical, test type, and sample type for the Great Lakes
database. See legend to Appendix 3 a for a description of the headings.
-------
NUMCODE CHEMCODE
101 TOC
APPENDIX 3B:
TEST SAMPTYP DNITS
CR14 BT %
SOMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
SEC C
101 TOC
BT
101 TOC
HA28
102 AVS
CR14
BT
UM/G
102 AVS
HA14
UM/G
102 AVS
HA28
UM/G
104 CLAY
104 CLAY
104 CLAY
105 SAND
CR14
HA14
HA28
CR14
BT %
BT %
BT *
BT %
NR
NR
NR
105 SAND
HA14
105 SAND
HA28
BT
106 WATER
CR14
CONC
# t # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
X
X
X
X
X
X
X
X
X
X
X
X
X
@
X
X
X
X
X
X
X
X
X
X
X
3.
5.
2.
4.
8.
1.
3.
1.
4.
1.
3.
4.
1.
3.
2.
4.
1.
3.
4.
1
3
15
33
7
14
161
3
6
5
15
3
9
8
2
6
5
15
3
9
8
2
5
70 27
70 27
39 27
47 27
90 27
55 27
50 27
70 27
.65 27
.30 27
.98 27
.00 27
.00 27
.40 27
.00 27
.65 27
.41 27
.98 27
.00 27
.00 27
.40 27
.50 22
.50 22
.15 22
.18 22
.00 22
.30 22
.00 22
.10 22
.60 22
.46 22
.67 22
.90 22
.35 22
.00 22
.10 22
.50 22
.64 22
.48 22
.90 22
.60 22
.80 22
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
9
9
9
9
9
11
11
11
11
11
22
22
22
22
22
7
7
7
7
7
12
12
12
12
12
12
12
12
12
12
5
5
5
5
5
10
10
10
10
10
11
11
11
11
11
10
7
18
8
2
17
6
18
7
7
28
11
33
13
13
9
4
14
9
1
12
5
13
6
7
25
12
26
16
17
79
76
64
79
74
81
78
84
75
75
61
66
60
63
63
78
81
65
78
73
77
73
82
77
73
69
67
67
67
64
14
10
17
12
2
38
19
41
19
19
23
11
26
11
11
14
8
14
14
41
23
45
27
27
40
24
40
29
29
64
67
48
67
71
44
59
44
56
56
39
55
34
52
52
65
73
51
65
73
36
50
36
SO
45
29
43
26
38
36
10
7
26
7
2
16
16
3
3
23
6
27
10
10
11
3
24
11
3
14
14
5
19
5
21
10
12
12
17
10
14
24
3
22
22
22
16
27
13
27
27
11
16
11
11
24
9
27
5
23
23
12
29
12
24
24
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
X
X
X
X
®
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
16.
32.
21,
49.
98.
29
73
15
32
21
49
98
29
73
15
32
21
48
98
29
70
44
46
.00 27
.95 27
.69 27
.11 27
.50 27
.40 27
.20 27
.60 27
.95 27
.42 27
.11 27
.50 27
.40 27
.20 27
.60 27
.95 27
.42 27
.09 27
.50 27
.40 27
.20 27
.10 27
.30 27
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
8
8
8
8
8
12
12
12
12
12
12
12
12
12
12
.
8
8
31
26
28
22
1
23
17
19
13
1
44
36
39
30
1
22
18
38
36
36
36
71
56
44
44
SO
56
54
47
46
51
56
60
55
19
12
14
7
34
19
22
16
37
26
28
23
19
12
19
24
21
29
71
22
25
22
34
56
18
21
18
28
56
40
43
55
50
52
45
2
38
34
38
25
3
40
37
40
30
2
33
31
7
14
12
19
26
6
22
19
25
41
5
16
14
19
42
7
14
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NDMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
106
106
106
107
107
107
110
110
110
111
111
111
300
300
300
300
300
300
301
301
301
301
301
301
302
302
WATER
WATER
WATER
SILT
SILT
SILT
NH3P
NH3P
NH3P
HSP
HSP
HSP
AL
AL
AL
AL
AL
AL
SILVER
SILVER
SILVER
SILVER
SILVER
SILVER
ARSENIC
ARSENIC
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
CR14
HA14
HA14
HA28
HA28
CR14
CR14
HA14
HA14
HA28
HA28
CR14
CR14
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BS
BT
BS
BT
BT
PW
BT
PW
BT
PW
BS
BT
%
%
*
%
*
%
MG/L
MG/L
MG/L
MG/L
MG/L
MG/L
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
UG/L
NG/G
UG/L
NG/G
UG/L
NG/G
NG/G
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
X
X
®
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
42.
54.
76.
41.
64.
41.
46.
40.
54.
76.
40.
64.
44.
48.
42.
54.
76.
41.
61.
-
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
•
32000.
60000.
88
44
40
70
00
70
30
84
44
40
00
00
10
60
88
58
40
70
30
02
27
01
10
09
01
04
02
17
01
07
09
01
03
00
00
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
8
8
8
21
21
21
21
21
21
21
21
21
21
21
21
21
21
21
2
2
2
4
4
4
4
4
4
19
16
19
16
19
16
4
27
27
11 8 23 57
11 8 10 60
11 8 1 71
13 10 18 S3
13 10 13 50
13 10 18 59
13 10 8 53
13 10 1 56
24 8 29 53
24 8 22 54
24 8 31 49
24 8 14 54
24 8 2 54
3 ...
9 7 12 67
9 7 4 76
9 7 12 67
9 7 4 76
97 5 71
20 8 24 71
20 8 6 66
20 8 25 68
20 8 11 63
20 8 9 63
2 ...
1 ...
2 ...
11 5 20 60
11 5 7 71
19 38 36 7
5 55 19 21
71 2 26
28 31 28 13
16 34 25 25
28 31 28 13
9 44 16 31
56 3 41
23 30 28 19
18 37 21 25
23 26 32 19
11 44 14 32
54 4 42
.
33 33 24 10
19 57 . 24
33 33 24 10
19 57 . 24
19 52 5 24
39 32 20 10
15 51 . 34
39 29 22 10
20 44 7 29
17 46 5 32
.
.
.
.
.
.
.
17 43 31 10
7 64 10 19
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NUMCODE CHEMCODE
302 ARSENIC
302 ARSENIC
302 ARSENIC
302 ARSENIC
TEST SAMPTYP UNITS
NG/G
CR14 PW UG/L
HA14 BS NG/G
HA14 BT NG/G
SEC C
302 ARSENIC
HA14
DG/L
302 ARSENIC
302 ARSENIC
HA28 BS NG/G
HA28 BT NG/G
302 ARSENIC
UG/L
303 CADMIUM
CR14
BS NG/G
303 CADMIUM
NG/G
303 CADMIUM
CR14
PW
UG/L
303 CADMIUM
HA14
BS
NG/G
303 CADMIUM
HA14
BT
NG/G
CONC
# # # TOTAL
N TOX EFFECT HI1'1 CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
TEL
PEL
NEC
NERM
NERH
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
20435.
53216.
92900.
13050.
47200.
12100.
33000.
13200.
39466.
92900.
14400.
47200.
1.
2.
1.
1.
2.
1.
1.
13000.
34000.
13124.
40059.
92900.
13250.
47200.
1.
2.
1.
1.
2.
1.
1.
787.
1349.
420.
870.
1349.
225.
562.
5200,
10850.
2026.
5208,
8000,
790,
2500
0
1
0
0
0
0
0
337
1068
237
774
899
167
562
700
5200
674
3605
26
54
00
00
00
00
00
00
44
00
00
00
70
30
37
98
30
10
70
00
,00
.40
.96
00
,00
.00
,70
,00
,37
.79
.30
,10
,60
,00
.00
.80
.71
,00
,00
,00
.00
.00
.82
.17
.00
.00
.00
.19
.00
.12
.45
.20
.08
.20
.00
.00
.23
.74
.00
.00
.00
.00
.00
.54
.55
27
27
27
27
27
20
4
27
27
27
27
27
27
27
20
20
20
20
20
20
20
4
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
11
11
11
3
13
13
13
13
13
10
10
10
10
10
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
13
13
5
5
5
10
10
10
10
10
7
7
7
7
7
9
9
9
9
9
8
8
8
8
8
5
5
5
5
5
6
6
6
6
6
5
5
5
5
5
10
10
10
10
10
11
11
11
11
i
4
19
10
15
9
2
8
5
10
5
5
28
19
26
17
4
22
19
24
19
19
17
15
21
16
IS
10
5
20
9
8
IS
6
16
7
14
12
5
12
7
6
19
7
19
8
55
71
69
69
66
63
63
59
71
67
62
67
67
65
63
62
60
54
69
61
64
61
61
62
62
57
59
62
83
81
64
81
83
66
80
63
83
63
78
74
78
74
70
81
75
81
78
17
10
2
34
19
25
16
3
29
19
29
19
19
33
23
29
19
4
42
33
42
33
33
16
14
19
14
14
17
10
19
14
14
17
11
17
14
14
39
22
39
26
22
41
19
41
22
38
62
67
34
47
38
47
56
43
48
33
48
48
33
40
33
40
50
28
28
22
28
28
46
49
38
46
49
67
71
45
67
69
49
69
46
69
49
39
52
39
48
48
41
56
41
56
36
12
7
25
13
22
13
3
10
5
19
5
5
21
13
21
13
4
19
19
25
19
19
30
27
38
30
27
7
2
29
7
5
26
6
29
6
26
13
13
4
4
19
3
19
3
10
17
24
6
22
16
25
38
19
29
19
29
29
13
23
17
27
42
11
19
11
19
19
8
11
5
11
11
10
17
7
12
12
9
14
9
11
11
9
26
9
22
26
22
19
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
303 CADMIUM
303 CADMIUM
HA14
HA14
BT
PW
NG/G
UG/L
303 CADMIUM
HA28
BS
NG/G
303 CADMIUM
HA28
BT NG/G
303 CADMIUM
HA28
PW
UG/L
304 CHROMIUM-T CR14
BS
NG/G
304 CHROMIUM-T CR14
BT
NG/G
304 CHP.OMIUM-T CR14
PW
UG/L
304 CHROMIUM-T HA14
BS
NG/G
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
304 CHROMIUM-T HA14
BT
NG/G
304 CHROMIUM-T HA14
PW
UG/L
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
ITRM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
8000.
650.
2500.
0.
0.
0.
0.
0.
0.
0.
337.
1068.
237.
774.
899.
167.
S62.
900.
5200.
737.
3605.
8000.
605.
2500.
0.
0.
0.
0.
0.
0.
0.
21682.
41077.
5414.
9471.
14975.
1352.
2184.
274000.
407000.
119364.
195075.
312000.
52000.
93500.
2.
24.
1.
6.
2.
0.
1.
14975.
22254.
4499.
6059.
2184.
13S2.
1650.
56000.
293000.
53962.
131480.
95000.
52000.
59000.
2.
13.
1.
5.
00
00
00
10
92
09
43
20
08
20
00
OC
23
74
00
00
00
00
00
90
55
00
00
00
10
92
09
43
20
08
20
00
00
25
65
00
00
00
00
00
99
£3
00
00
00
46
40
28
81
SO
67
90
00
00
58
£3
00
00
00
00
00
95
04
00
00
00
46
20
28
01
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
13
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
11
11
11
11
11
.
9
9
9
9
9
11
11
11
11
11
13
13
13
13
13
10
10
10
10
11
6
6
6
6
6
10
10
10
10
10
11
11
11
11
11
6
6
6
6
6
5
5
5
5
5
7
7
7
7
7
5
5
5
5
5
7
7
7
7
7
12
12
12
12
12
7
7
7
7
6
10
3
10
4
8
23
15
23
17
16
31
10
33
14
8
18
6
18
7
14
5
3
7
6
6
7
4
7
7
6
7
3
8
4
6
6
4
6
6
8
15
6
15
7
9
7
4
8
4
72
62
67
£2
71
52
74
74
74
74
71
69
71
66
74
71
64
64
64
67
53
89
84
84
86
86
86
83
86
86
83
83
83
80
86
80
78
70
78
78
78
81
78
81
81
81
76
71
71
71
16
29
14
29
19
19
42
32
42
34
32
29
13
29
18
11
33
17
33
19
22
14
a
14
14
14
14
10
14
14
12
14
9
14
11
11
26
17
26
25
3 11
34
19
34
22
25
29
19
29
19
56
33
52
33
52
33
32
42
32
39
39
40
58
37
56
60
31
47
31
47
31
-
75
76
70
73
73
•
71
74
71
71
71
69
74
66
74
69
52
52
52
52
48
47
59
47
59
56
48
52
43
52
3
19
19
19
18
8
18
11
11
21
3
24
5
2
17
17
17
5
3
3
2
2
2
2
6
9
6
4
13
13
3
5
10
25
19
33
19
29
29
8
18
8
16
18
10
26
10
21
27
19
36
19
33
31
11
16
11
11
11
12
17
12
12
14
11
17
11
14
14
22
30
22
22
17
6
22
6
19
16
-
19
29
19
29
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NOMCODE CHEMCODE TEST SAMPTYP UNITS
304 CHROMIDM-T HA14 PW UG/L
304 CHROMIUM-T HA28 BS NG/G
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
304 CHROMIUM-T HA28 BT NG/G
304 CHROMIDM-T HA28
UG/L
305 COPPER CR14 BS NG/G
305 COPPER CR14 BT NG/G
305 COPPER
CR14
UG/L
305 COPPER HA14 BS NG/G
305 COPPER HA14 BT NG/G
305 COPPER
PW
UG/L
305 COPPER HA28 BS NG/G
305 COPPER HA28 BT NG/G
305 COPPER
HA28
PW
UG/L
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
2
0
1
1300
18328
1325
5499
2184
1352
1650
90000
312000
68410
135676
95000
52000
59000
0
7
0
3.
2
0
1.
96500.
187000.
52488.
99882.
148000.
28550.
53350.
5.
19.
3.
9.
4.
2.
4.
41300.
122250.
28012.
78025.
54800.
19000.
49800.
5.
19.
3.
9.
4.
2.
4.
41300.
122250.
28012.
78025.
54800.
19000.
49800.
3.
19.
2.
9.
4.
2.
.50
.67
.90
.00
.50
.75
.27
.00
.00
.00
.00
.00
.53
.08
.00
.00
.00
.80
.85
.73
.86
.50
.67
.90
.00
.00
.81
.18
.00
.00
.00
.30
.80
.78
.63
68
70
68
00
00
SO
96
00
00
00
30
80
78
63
68
70
68
00
00
SO
96
00
00
00
30
45
96
54
68
65
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
27
27
27
27
27
27
27
20
20
20
20
20
20
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
3
11
11
11
11
11
9
9
9
9
9
3
13
13
13
13
13
10
10
10
10
10
3
24
24
24
24
24
19
19
19
19
19
7
10
10
10
10
10
11
11
11
11
11
8
8
8
8
8
7
7
7
7
7
5
5
5
5
5
12
12
12
12
12
5
5
5
5
B
12
12
12
12
12
6
6
6
6
6
6
31
5
30
7
19
11
6
12
7
9
10
4
10
4
6
18
14
20
17
16
16
7
21
11
21
15
6
16
7
9
S
3
10
4
10
26
17
29
18
20
24
7
26
11
22
71
53
63
50
68
68
76
71
74
73
73
58
58
58
58
58
64
64
64
62
64
63
77
49
71
49
81
78
84
81
81
76
67
52
71
52
73
71
71
73
73
53
61
47
67
47
48
24
42
13
39
18
34
16
10
16
11
13
19
11
19
11
14
17
12
19
14
14
17
11
17
14
17
34
19
38
22
25
24
14
24
19
24
35
25
37
27
29
36
17
36
25
31
11
50
11
50
34
60
61
58
61
60
39
47
39
47
44
48
52
45
48
50
46
66
31
57
31
47
59
47
59
56
52
52
29
52
29
38
46
35
46
44
17
44
11
42
17
39
39
16
2
3
2
8
8
3
26
21
29
26
24
29
9
43
17
43
13
13
3
24
24
15
8
19
8
10
31
3
36
6
31
8
37
11
32
16
23
29
23
27
26
33
42
33
42
39
10
14
7
12
12
9
14
9
11
9
6
22
3
19
16
24
33
24
29
24
12
21
10
19
17
17
36
17
28
22
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
:ODE
305
306
306
306
306
306
306
307
307
307
307
307
307
308
308
308
308
308
308
309
309
309
CHEMCODE TEST
COPPER HA28
IRON CR14
IRON CR14
IRON HA14
IRON HA14
IRON HA28
IRON HA28
MERCURY CR14
MERCURY CR14
MERCURY HA14
MERCURY HA14
MERCURY HA28
MERCURY HA28
MANGANESE CR14
MANGANESE CR14
MANGANESE HA14
MANGANESE HA14
MANGANESE HA28
MANGANESE HA28
NICKEL CR14
NICKEL CR14
NICKEL CR14
SAMPTYP UNITS
PW UG/L
BS %
BT %
BS %
BT %
BS %
BT %
BT NG/G
PW UG/L
BT NG/G
PW UG/L
BT NG/G
PW UG/L
BS NG/G
BT NG/G
BS NG/G
BT NG/G
BS NG/G
BT NG/G
BS NG/G
BT NG/G
PW UG/L
SEC
NERH
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
4.68
3.
5.
2.
3.
2.
1.
2.
3.
5.
2.
3.
2.
1.
2.
726000.
1678000.
597655.
1080688.
819000.
492000.
696000.
726000.
1678000.
597655.
1080688.
731000.
492000.
696000.
43000.
50000.
29544.
43531.
57000.
20300.
37900.
5.
10.
4.
6.
4.
4.
4.
57
81
10
99
74
23
74
57
81
10
99
74
23
74
00
00
42
67
00
00
00
00
00
42
67
00
00
00
00
00
88
£0
00
00
00
80
40
82
99
90
00
70
N
20
16
16
16
16
16
16
16
16
16
16
16
16
16
16
16
16
16
16
19
16
19
16
19
16
22
23
22
23
23
23
23
23
23
23
22
23
23
23
23
23
23
23
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
TOX EFFECT
4
2
10
10
10
10
10
2
19
19
19
19
19
2
1
2
1
1
3
3
4
•
11
11
11
11
11
22
22
22
22
22
4
11
11
11
11
11
9
9
9
9
9
5
5
5
5
5
5
5
5
5
5
8
8
8
8
8
8
8
8
8
8
9
9
9
9
9
5
5
5
5
5
HIT C
-
5
3
10
4
10
14
8
25
11
22
9
4
15
5
6
18
7
26
9
16
9
6
15
8
4
7
4
10
4
10
ORREC
71
59
41
65
41
66
47
44
56
47
83
71
67
75
71
68
57
59
61
64
90
83
81
88
79
83
80
74
80
74
29
18
29
24
29
34
16
41
25
38
33
17
38
21
21
30
11
34
16
25
19
12
21
17
7
14
9
14
9
14
41
41
12
41
12
31
31
3
31
9
50
54
29
54
50
39
45
25
45
39
71
71
60
71
71
69
71
60
71
60
29
29
9
9
38
9
31
4
25
4
11
5
25
5
11
2
2
14
2
2
6
3
14
3
14
29
41
29
35
29
25
44
19
34
22
13
29
8
25
25
20
39
16
34
25
7
14
5
10
19
11
17
11
17
11
-------
APPENDIX 3B: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NDMCODE CHEMCODE
309 NICKEL
TEST SAMPTYP UNITS
HA14 BS NG/G
SEC C
309 NICKEL
BT NG/G
309 NICKEL
UG/L
309 NICKEL
BS
NG/G
309 NICKEL
BT
NG/G
309 NICKEL
HA28
UG/L
310 LEAD
CR14
NG/G
CR14
NG/G
# # # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
310 LEAD
CR14
PW
UG/L
310 LEAD
HA14
NG/G
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
4873.
6693.
2726.
5282.
4170.
1526.
4170.
39600.
47500.
27717.
38681.
37900.
19400.
31500.
5.
10.
4.
6.
4.
4.
4.
4873.
6693.
2726.
5282.
4170.
1526.
4170.
39600.
50000.
27717.
39686.
43000.
19400.
31500,
5.
10.
4,
6.
4.
4.
4.
10360
102352
9494
34605
39159
8702
11700
86000
492500
52786
183942
286000
32400
68700
5
89
2
17
5
0
3
13882
59878
10315
26468
11700
7666
11700
00
00
94
97
00
00
00
00
00
14
39
00
00
00
80
40
82
99
90
00
.70
00
.00
.94
,97
.00
.00
.00
.00
.00
,14
.27
.00
.00
.00
.80
.40
.82
.99
.90
.00
.70
.00
.00
.88
.18
.00
.00
.00
.00
.00
.36
.25
.00
.00
.00
.30
.50
.06
.70
.70
.80
.50
.00
.00
.98
.33
.00
.00
.00
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
11
11
11
11
11
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
5
5
5
5
5
12
12
12
12
12
5
5
5
5
5
5
5
5
5
5
11
11
11
11
11
5
5
5
5
5
5
5
5
5
5
6
6
6
6
6
5
5
5
5
5
7
7
7
7
7
5
3
11
4
10
11
6
17
11
12
5
3
7
3
7
8
5
23
6
16
11
6
18
10
9
7
4
10
4
10
24
4
24
14
13
14
4
23
7
6
6
3
10
4
5
6
4
12
5
11
74
65
57
70
52
94
78
81
94
91
76
67
67
67
67
66
63
53
66
50
76
71
68
74
73
61
58
58
58
58
49
81
49
65
68
79
79
62
81
79
86
83
74
86
83
78
70
61
74
57
22
13
26
17
22
34
19
38
34
34
24
14
24
14
24
18
13
32
16
21
16
10
18
15
13
17
11
19
11
19
19
8
19
14
14
19
7
21
12
10
14
9
14
11
11
26
17
30
22
26
52
52
30
52
30
59
59
44
59
56
52
52
43
52
43
47
50
21
50
29
60
61
50
60
60
44
47
39
47
39
30
73
30
51
54
60
71
40
69
69
71
74
60
74
71
52
52
30
52
30
.
22
22
16
3
10
10
•
3
29
21
2
11
2
2
•
3
8
a
46
3
46
24
22
•
14
2
33
5
5
3
14
3
22
22
26
35
22
30
26
6
22
3
6
6
24
33
24
33
24
32
37
18
34
29
23
29
21
24
26
36
42
33
42
33
5
16
5
11
11
7
19
5
14
17
11
17
11
14
14
22
30
17
26
22
-------
APPENDIX 3B: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NOMCODE CHEMCODE
310 LEAD
TEST SAMPTYP DNITS
HA14 BT NG/G
SEC C
# # # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
310 LEAD
HA14
PW
UG/L
310 LEAD
HA28 BS
NG/G
310 LEAD
BT
NG/G
310 LEAD
PW
UG/L
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
51000.
251000.
39825.
1206SS.
68700.
31100.
58000.
0.
5.
0.
4.
4.
0.
1.
13882.
81115.
10658.
30806.
11700.
8184.
11700.
55000.
251000.
41358.
1206S6.
68700.
31100.
58000.
0.
5.
0.
4 .
4 .
0.
3.
00
00
87
54
00
00
00
70
50
73
39
10
76
50
00
00
81
58
00
00
00
00
00
19
54
00
00
00
70
30
70
31
10
70
50
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
13
13
13
13
13
10
10
10
10
10
19
19
19
19
19
24
24
24
24
24
19
19
19
19
19
11
11
11
11
11
10
10
10
10
10
6
6
6
6
6
11
11
11
11
11
11
11
11
11
11
14
6
15
6
10
16
5
13
6
7
17
4
24
IS
24
26
7
28
8
21
19
6
19
6
7
78
78
81
78
84
71
76
67
81
76
74
61
55
74
55
74
73
74
71
76
67
64
67
64
61
31
19
34
19
28
48
24
38
29
29
34
11
34
32
34
27
11
29
11
24
36
17
36
17
17
47
59
47
59
56
24
52
29
52
48
39
50
21
42
21
47
61
45
60
52
31
47
31
47
44
13
13
3
29
24
5
11
29
8
29
15
16
2
10
17
17
3
9
22
6
22
13
24
10
19
19
16
39
16
18
16
11
27
10
27
15
17
36
17
36
36
311 SELENIUM
311 SELENIUM
311 SELENIUM
312 ZINC
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
CR14 BS NG/G
NR
19
312 ZINC
CR14
BT
NG/G
312 ZINC
CR14
PW
UG/L
312 ZINC
HA14
BS
NG/G
312 ZINC
BT
NG/G
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
12747.
102239.
11901.
37833.
27390.
11113.
14000.
381000.
2250000.
248822.
899374.
900000.
162500.
359500.
6.
49.
2.
13.
10.
1.
3.
12747.
84066.
10762.
34306.
17388.
9086.
14000.
159000.
422000.
00
00
99
13
00
00
00
00
00
23
78
00
00
00
30
60
86
91
70
30
90
00
00
23
33
00
50
00
00
00
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
9
9
9
9
9
11
11
11
11
11
9
9
9
9
9
11
11
11
11
11
13
13
5
5
5
5
5
7
7
7
7
7
5
5
S
5
5
6
6
6
6
6
12
12
26
14
27
15
16
18
6
23
10
10
19
9
24
14
15
12
3
15
4
6
17
7
38
59
35
62
59
64
83
57
74
74
54
71
40
63
60
52
65
39
70
70
81
75
16
11
16
14
14
17
12
19
12
12
17
11
17
14
14
26
13
26
17
22
38
19
22
49
19
49
46
48
71
38
62
62
37
60
23
49
46
26
52
13
52
48
44
56
54
27
57
27
30
26
2
36
12
12
37
14
51
26
29
26
39
4
16
3
8
14
8
11
11
10
14
7
14
14
9
14
9
11
11
22
35
22
30
26
3
22
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NOMCODE CHEMCODE TEST SAMPTYP UNITS
SEC
CONC
tt » # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
312
312
312
312
312
313
313
313
314
314
314
315
315
315
316
316
316
399
399
399
401
401
401
402
402
402
ZINC
ZINC
ZINC
ZINC
ZINC
METHYL-HG
METHYL-HG
METHYL-HG
TBT
TBT
TBT
DBT
DBT
DBT
MET
MET
MET
SEMAVS
SEMAVS
SEMAVS
14-2CLBNZ
14-2CLBNZ
14-2CLBNZ
12-2CLBNZ
12-2CLBNZ
12-2CLBNZ
HA14
HA14
HA28
HA28
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
CR14
HA14
HA28
BT
PW
BS
BT
PW
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BT
BT
NG/G
UG/L
NG/G
NG/G
UG/L
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
125463.
385414.
541000.
99000.
352000.
6.
49.
2.
13,
10,
1.
3.
27390.
102239.
17446.
37833.
17388.
11113.
14000.
127000.
381000.
116244
363602
541000.
106400
347000.
6
49
2
13
10
1
3
.14
.06
.00
.00
.00
.30
.60
.86
.91
.70
.30
.90
.00
.00
.63
.13
.00
.00
.00
.00
.00
.57
.81
.00
.00
.00
.30
.60
.86
.91
.70
.30
.90
27
27
27
27
27
20
20
20
20
20
20
20
22
22
22
22
22
22
22
27
27
27
27
27
27
27
20
20
20
20
20
20
20
12
12
12
12
12
12
12
12
12
12
12
12
18
18
18
19
19
19
7
7
7
13 12 19
13 12 7
13 12 6
10 5 6
10 5 3
10 5 11
10 5 4
10 5 5
19 5 16
19 5 14
19 5 18
19 5 15
19 5 19
24 13 35
24 13 19
24 13 36
24 13 21
24 13 17
19 5 19
19 5 9
19 5 25
19 5 14
19 5 15
1
1
3
2
1
1
3
3
2
1
3
81
75
72
71
67
48
71
67
71
66
71
68
68
66
76
65
73
73
67
61
50
64
61
41
19
16
24
14
24
19
19
32
26
34
29
34
31
23
31
23
19
36
19
36
28
28
41
56
56
48
52
24
52
48
39
39
37
39
34
35
53
34
50
53
31
42
14
36
33
19
3
3
5
29
5
11
11
13
11
16
26
27
11
17
6
33
11
14
22
25
24
33
24
29
29
18
24
16
21
16
16
19
17
33
17
25
25
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
403 13-2CLBNZ CR14
403 13-2CLBNZ HA28
404 NAPHTHALENE CR14 BT
404 NAPHTHALENE HA14 BT
405 2-METHNAP CR14
405 2-METHNAP HA14
405 2-METHNAP HA28
406 ACENA CR14
406 ACENA HA14
406 ACENA HA28
407 DIBNZFURAN CR14
407 DIBNZFURAN HA14
407 DIBNZFURAN HA28
408 FLUORENE CR14
408 FLUORENE HA14
408 FLUORENE HA28
409 PHENANTHRN CR14
WPTTf
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
'P UNITS
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
NG/G
SEC
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
C
X
X
X
@
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONG
160
3600
126
1003
20000
99
280
55
325
43
285
290
35
2SO
42
325
49
285
290
59
250
88
1700
91
689
1800
95
280
50
595
43
385
290
38
250
46
595
47
385
290
50
250
390
3400
394
1709
6100
400
860
.00
.00
.17
.99
.00
.50
.00
.00
.00
.87
.04
.00
.00
.00
.00
.00
.78
.04
.00
.00
.00
•
•
-
.00
.00
.43
.93
.00
.00
.00
.00
.00
.59
.68
.00
.00
.00
.00
.00
.96
.68
.00
.00
.00
.00
.00
.97
.97
.00
.00
.00
N
7
7
7
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
19
19
19
8
8
8
19
19
19
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
TOX EFFECT HIT CORRE'
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
3
2
2
2
1
1
3
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
7
7
7
7
7
12
12
12
12
12
12
12
12
12
12
7
7
7
7
7
12
12
12
12
12
12
12
12
12
12
7
7
7
7
7
•
15
5
16
5
1
18
6
18
7
7
22
7
21
8
8
16
5
15
6
4
19
6
20
7
8
24
7
23
8
9
16
5
15
5
4
71
81
74
81
71
78
78
78
75
75
61
69
60
68
68
74
81
71
83
79
75
78
78
81
78
58
69
56
71
69
79
81
76
81
79
17
10
19
10
38
19
38
19
19
18
10
16
10
10
19
10
17
12
7
38
19
41
22
22
18
10
16
11
11
21
10
19
10
7
55
71
55
71
71
41
59
41
56
56
44
60
44
58
58
55
71
55
71
71
38
59
38
59
56
40
60
40
60
58
57
71
57
71
71
19
2
19
2
2
19
19
3
3
18
2
18
3
3
19
2
19
2
2
22
22
3
21
2
21
2
3
17
2
17
2
2
10
17
7
17
26
3
22
3
22
22
21
29
23
29
29
7
17
10
14
19
3
22
19
19
21
29
23
27
27
5
17
7
17
19
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
11
NUMCODE CHEMCODE TEST SAMPTYP UNITS
409 PHENANTHRN HA14 BT NG/G
SEC C
409 PHENANTHRN HA28
NG/G
410 ANTHRACENE CR14 BT NG/G
410 ANTHRACENE HA14
NG/G
410 ANTHRACENE HA28
NG/G
411 FLUORANTHN CR14
NG/G
411 FLUORANTHN HA14 BT NG/G
411 FLUORANTHN HA28
NG/G
412 PYRENE
CR14
BT
NG/G
412 PYRENE
HA14
BT
NG/G
ft # f TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTH-T TOXNOT
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
390
1100
225
749
1000
130
510
340
1100
270
798
1000
215
580
140
1250
129
580
1700
120
270
100
670
81
409
290
66
250
66
670
88
409
290
120
250
160
4800
234
2400
7500
345
1200
160
1200
152
774
1200
145
500
110
1200
153
869
1200
215
630
570
SSOO
594
2824
6100
620
1450
570
1100
269
908
1800
127
750
.00
.00
.17
.00
.00
.00
.00
.00
.00
.37
.75
.00
.00
.00
.00
.00
.61
.95
.00
.00
.00
.00
.00
.24
.27
.00
.00
.00
.00
.00
.99
.27
.00
.00
.00
.00
.00
.95
.00
.00
.00
.00
.00
.00
.32
.60
.00
.00
.00
.00
.00
.79
.48
.00
.00
.00
.00
.00
.47
.00
.00
.00
.00
.00
.00
.05
.30
.00
.00
.00
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
13
13
13
13
13
13
13
13
13
13
8
8
8
8
8
12
12
12
12
12
12
12
12
12
12
7
7
7
7
7
13
13
13
13
13
-
13
13
13
13
13
7
7
7
7
7
13
13
13
13
13
.
17
7
20
8
8
20
8
21
9
9
16
5
16
6
4
18
6
18
6
7
21
7
20
7
8
19
5
16
5
4
21
8
21
10
8
31
9
26
11
9
16
5
15
5
4
17
8
20
10
7
81
81
78
78
78
68
71
66
69
69
74
81
74
83
79
78
78
78
78
75
63
69
61
69
68
71
81
74
81
79
69
78
69
84
78
56
69
55
73
69
79
81
76
81
79
81
78
72
78
75
38
22
41
22
22
19
11
19
11
11
19
10
19
12
7
38
19
38
19
19
18
10
16
10
10
21
10
19
10
7
38
22
38
28
22
23
11
18
15
11
21
10
19
10
7
38
22
33
25
19
44
59
38
56
56
48
60
47
58
58
55
71
55
71
71
41
59
41
59
56
45
60
45
60
58
50
71
55
71
71
31
56
31
56
56
34
58
37
58
58
57
71
57
71
71
44
56
34
53
56
16
22
3
3
13
2
15
3
3
19
2
19
2
2
19
19
3
16
2
16
2
3
24
2
19
2
2
28
3
28
3
3
27
3
24
3
3
17
2
17
2
2
16
3
25
6
3
3
19
19
19
19
27
19
27
27
7
17
7
14
19
3
22
3
22
22
21
29
23
29
29
5
17
7
17
19
3
19
3
13
19
16
27
21
24
27
5
17
7
17
19
3
19
3
16
22
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL OS ING GL DATA
12
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CONG
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
412 PYRENE HA28 BT NG/G
413 BAA CR14 BT NG/G
413 BAA HA14 BT NG/G
413 BAA HA28 BT NG/G
414 CHRYSENE CR14 BT NG/G
414 CHRYSENE HA14 BT NG/G
414 CHRYSENE HA28 BT NG/G
415 BBF CR14 BT NG/G
415 BBF HA14 BT NG/G
415 BBF HA28 BT NG/G
416 BKF CR14 BT NG/G
416 BKF HA14 BT NG/G
416 BKF HA28 BT NG/G
417 BAP CR14 BT NG/G
417 BAP HA14 BT NG/G
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
EKL.
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
120.
1100.
160.
983.
1800.
215.
880.
300.
4200.
273.
1554.
3500.
250.
575.
260.
490.
161.
363.
690.
100.
270.
35.
490.
84.
408.
690.
205.
340.
500.
5200.
367.
1831.
4000.
270.
645.
330.
690.
188.
525.
600.
108.
400.
110.
690.
150.
551.
600.
205.
440.
210.
8500
219.
1933.
5800.
230
440.
350
620
187
409
00 27
00 27
62 27
87 27
00 27
00 27
00 27
00 27
00 27
86 27
03 27
00 27
00 27
00 27
00 27
00 27
65 27
73 27
00 27
50 27
00 27
00 27
00 27
71 27
17 27
00 27
00 27
00 27
00 27
00 27
42 27
39 27
00 27
00 27
00 27
00 27
00 27
79 27
36 27
00 27
00 27
00 27
00 27
00 27
17 27
00 27
00 27
.00 27
00 27
19
19
19
19
19
19
.00 27
.00 27
.77 27
.91 27
.00 27
.00 27
.00 27
.00 27
.00 27
.55 27
.15 27
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
4
1
1
4
11
11
11
11
11
13
13
13
13
13
13
13
13
13
7
7
7
7
7
13
13
13
13
13
13
13
13
13
13
7
7
7
7
7
13
13
13
13
13
13
13
13
13
13
6
6
6
6
6
11
11
11
11
30
9
25
10
8
13
4
13
5
5
15
8
18
10
6
33
9
28
11
7
10
4
14
5
5
16
7
20
9
9
28
8
25
10
10
18
3
17
5
5
11
6
18
10
58
69
56
68
68
81
83
81
81
81
88
78
78
78
72
56
69
58
69
66
88
83
83
81
81
84
81
72
81
81
61
71
56
71
71
74
81
71
81
81
38
78
78
84
23
11
18
11
10
19
10
19
10
10
38
22
38
25
16
24
11
21
13
8
19
10
21
10
10
38
22
38
25
25
23
11
18
13
13
21
7
19
10
10
31
19
38
28
35
58
39
56
58
62
74
62
71
71
50
56
41
53
se
32
58
37
56
58
69
74
62
71
71
47
59
34
56
56
39
60
39
58
58
52
74
52
71
71
56
59
41
56
26
3
23
5
3
12
12
2
2
9
3
19
6
3
29
3
24
5
3
5
12
2
2
13
25
3
3
23
2
23
3
3
21
21
2
2
3
19
3
16
27
21
27
29
7
17
7
17
17
3
19
3
16
25
15
27
18
26
31
7
17
5
17
17
3
19
3
16
16
16
27
21
26
26
5
19
7
17
17
9
22
3
13
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
13
NUMCODE CHEMCODE TEST SAMPTYP UNITS SEC C
# # # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
417 BAP HA14
417 BAP HA28
418 ICDP CR14
418 ICDP HA14
418 ICDP HA28
419 BGHIP CR14
419 BGHIP HA14
419 BGHIP HA28
420 BBKF CR14
420 BBKF HA14
420 BBKF HA28
421 ACENAPTYLE CR14
421 ACENAPTYLE HA14
421 ACENAPTYLE HA28
422 DBA CR14
422 DBA HA14
422 DBA HA28
423 4-METHNAP CR14
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
440.00 27
100.50 27
270.00 27
280.00 27
620.00 27
167.75 27
409.15 27
440.00 27
100.50 27
270.00 27
160.00 27
5300.00 27
183.30 27
1218.20 27
3800.00 27
210.00 27
280.00 27
78.00 27
410.00 27
111.71 27
320.16 27
290.00 27
160.00 27
250.00 27
160.00 27
410.00 27
111.71 27
320.16 27
290.00 27
78.00 27
250.00 27
290.00 27
6300.00 27
249.70 27
1374.77 27
3800.00 27
21S.OO 27
300.00 27
91.00 27
460.00 27
120.66 27
352.42 27
310.00 27
160.00 27
270.00 27
30.00 27
310.00 27
61.36 27
278.39 27
290.00 27
125.50 27
250.00 27
8
8
8
15
15
15
8
8
8
7
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
21
21
21
21
21
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
1
2
2
2
2
2
2
11
11
11
11
11
11
7
7
7
7
7
12
12
12
12
12
12
12
12
12
12
7
7
7
7
7
12
12
12
12
12
13
13
13
13
13
10
13
7
20
11
11
18
4
16
5
5
21
6
20
6
9
21
7
22
7
10
10
4
14
5
5
21
6
20
6
7
33
8
29
11
11
84
73
69
65
73
73
69
83
69
81
81
69
78
66
78
75
65
72
63
72
70
83
83
79
81
81
69
78
66
78
75
50
71
53
73
73
28
16
10
18
IS
15
19
10
17
10
10
38
19
34
19
22
19
11
19
11
12
17
10
19
10
10
38
19
34
19
19
21
11
19
15
15
56
56
60
47
58
58
SO
74
52
71
71
31
59
31
" 59
53
46
61
44
61
58
67
74
eo
71
71
31
59
31
59
56
29
60
34
58
58
3
5
2
15
3
3
24
21
2
2
28
28
6
18
2
19
2
5
7
14
2
2
28
28
3
32
2
27
3
3
13
23
29
21
24
24
7
17
10
17
17
3
22
6
22
19
18
26
18
26
25
10
17
7
17
17
3
22
6
22
22
18
27
19
24
24
-------
APPENDIX 3B: SUMMARY OF SECS NORMALIZED TO DRY WEIGHT
SEC IN THRESGL USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
423 4-METHNAP HA14 BT NG/G
423 4-METHNAP HA28 BT NG/G
450 PAH-T CR14 BT NG/G
450 PAH-T
NG/G
450 PAH-T
BT
NG/G
451 PAH-L
CR14
NG/G
451 PAH-L
HA14
NG/G
451 PAH-L
KA28
NG/G
452 PAH-H
CR14
NG/G
452 PAH-H
HA14
BT
NG/G
452 PAH-H
HA28
BT
NG/G
508 PCB-T
508 PCB-T
CR14 BT NG/G
HA14 BT NG/G
SEC
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
3SS3.
59140.
4081.
21911.
84600.
4687.
8118.
3553.
8498.
2468.
6736.
9240.
1715.
5340.
1297.
8498.
2145.
6786.
9240.
3547.
5420.
811.
11040.
922.
5658.
33600.
1049.
2900.
786.
3369.
534.
2919.
3040.
363.
2530.
536.
3369.
744.
2919.
3040.
1033.
2530.
2900.
48100.
2813.
16881.
51000.
2730,
5925.
2900.
5650.
1685.
4089
6200.
980.
2960.
486
5650.
969
4503
6200
1935
3589
00
.00
02
15
00
SO
00
00
00
84
42
00
50
00
00
oo
02
€9
00
50
00
00
00
36
27
00
00
00
00
00
52
52
00
50
00
00
00
10
52
00
00
.00
.00
.00
.72
.72
.00
.00
.00
.00
.00
.82
.50
.00
.00
.00
.00
.00
.75
.09
.00
.00
.00
N
7
7
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
a
8
TOX EFFECT HIT CORSE)
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
2
2
7
7
7
7
7
13
13
13
13
13
13
13
13
13
13
7
7
7
7
7
13
13
13
13
13
13
13
13
13
13
7
7
7
7
7
13
13
13
13
13
13
13
13
13
13
17
5
16
5
4
18
8
20
9
7
27
9
24
10
8
17
5
15
5
3
18
7
21
8
8
23
8
19
9
9
15
5
16
5
4
16
8
20
10
7
32
9
26
11
8
76
81
74
81
79
78
78
72
81
75
56
69
58
71
68
71
81
71
81
76
78
81
75
78
78
63
71
63
69
69
81
81
79
81
79
84
78
72
84
75
55
69
55
73
68
21
10
19
10
7
38
22
38
25
19
19
11
18
13
10
19
10
17
10
5
38
22
41
22
22
19
11
16
11
11
21
10
21
10
7
38
22
38
28
19
23
11
18
15
10
55
71
55
71
71
41
56
34
56
56
37
58
40
58
58
52
71
55
71
71
41
59
34
56
56
44
60
47
58
58
60
71
57
71
71
47
56
34
56
56
32
58
37
58
58
19
2
19
2
2
19
3
25
3
3
24
3
21
3
3
21
2
19
2
2
25
3
3
18
2
IS
3
3
14
2
17
2
2
13
3
25
3
3
29
3
24
3
3
5
17
7
17
19
3
19
3
16
22
19
27
21
26
29
7
17
10
17
21
3
19
19
19
19
27
23
27
27
5
17
5
17
19
3
19
3
13
22
16
27
21
24
29
-------
APPENDIX 3B: SUMMARY OF SECs NORMALIZED TO DRY WEIGHT IS
SEC IN THRESGL USING GL DATA
# # # TOTAL
NUMCODE CHEMCODE TEST SAMPTYP UNITS SEC C CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
508 PCB-T HA28 BT NG/G NRX .82...
-------
Appendix 3c Summary of sediment effect concentrations (SECs) calculated using sediment
concentrations normalized to total organic carbon (TOC) concentrations and listed by
chemical, test type, and sample type for the entire database. See legend to Appendix
3a for a description of the headings.
-------
APPENDIX 3C: SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
401 14-2CLBNZ CR14 BT NG/G
401 14-2CLBNZ HA14 BT NG/G
401 14-2CLBNZ HA28 BT NG/G
402 12-2CLBNZ CR14 BT NG/G
402 12-2CLBNZ HA14 BT NG/G
402 12-2CLBNZ HA28 BT NG/G
403 13-2CLBNZ CR14 BT NG/G
403 13-2CLBNZ HA14 BT NG/G
403 13-2CLBNZ HA28 BT NG/G
404 NAPHTHALENE CR14 BT NG/G
404 NAPHTHALENE HA14 BT NG/G
404 NAPHTHALENE HA28 BT NG/G
405 2-METHNAP CR14 BT NG/G
405 2-METHNAP HA14 BT NG/G
405 2-METHNAP HA28 BT NG/G
406 ACENA CR14 BT NG/G
406 ACENA HA14 BT NG/G
406 ACENA HA28 BT NG/G
407 DIBNZFURAN CR14 BT NG/G
407 DIBNZFURAN HA14 BT NG/G
407 DIBNZFURAN HA28 BT NG/G
408 FLUORENE CR14 BT NG/G
408 FLUORENE HA14 BT NG/G
SEC
MR
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
C
X
X
X
X
X
X
X
X
X
e
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
s
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
2619
30571
1884
20898
224719
1356
14285
2619
15867
2642
16306
80000
2666
16758
1166
3636
1149
5134
80000
1133
7250
714
884
718
1330
31111
723
2000
3285
20000
1812
16903
80000
1000
14285
2090
17053
2361
16905
80000
2666
.05
.25
.57
.14
.10
.06
.71
.05
.65
.75
.87
.00
.67
.24
.67
.36
.88
.55
.00
.33
.00
.29
.62
.97
.12
.11
.68
.00
.71
.00
.65
.09
.00
.00
.71
.91
.57
.30
.26
.00
.67
N
19
19
19
7
7
7
7
7
7
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
19
19
19
23
13
38
38
38
38
38
38
38
19
19
19
42
42
42
42
42
42
42
32
32
32
32
32
32
TOX EFFECT HIT CORRE
2 . . .
1
3
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
3
1
1
10
10
10
10
10
1
1
3
11
11
11
11
11
13
13
13
13
13
8
8
8
8
8
12
12
12
12
12
19
19
19
19
19
6
6
6
6
6
9
9
9
9
9
12
12
12
12
12
18
6
19
8
1
21
9
20
9
3
37
19
38
16
3
22
17
21
7
1
16
8
18
9
2
21
9
20
9
2
79
79
76
79
71
69
69
66
69
63
60
63
61
58
63
47
45
45
61
71
74
79
74
76
74
69
69
66
69
59
24
10
24
12
38
19
34
19
6
29
16
31
11
3
16
8
13
3
19
12
21
12
2
38
19
34
19
3
55
69
52
67
71
31
50
31
50
56
31
47
31
47
60
32
37
32
58
71
55
67
52
64
71
31
50
31
50
56
19
5
21
7
2
28
9
28
9
3
31
15
31
15
2
42
37
42
16
3
19
7
21
10
2
28
9
28
9
3
2
17
2
14
26
3
22
6
22
34
10
23
8
27
35
11
18
13
24
26
7
14
5
14
24
3
22
6
22
38
-------
APPENDIX 3C:
NUMCODE CHEMCODE TEST SAMPTYP ONITS
408 FLUORENE HA14 BT NG/G
408 FLUORENE HA28 BT NG/G
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
SEC C
# t # TOTAL
CONC N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
NERH X 16758.24 32
409 PHENANTHRN CR14
BT NG/G
409 PHENANTHRN HA14
BT NG/G
409 PHENANTHRN HA28
BT NG/G
410 ANTHRACENE CR14
BT
NG/G
410 ANTHRACENE HA14
NG/G
410 ANTHRACENE HA28
BT NG/G
411 FLUORANTHN CR14
BT
NG/G
411 FLUORANTHN HA14
BT
NG/G
411 FLUORANTHN HA28
NG/G
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
909.
328S.
953.
5635.
80000.
1000.
9666.
6140.
50357.
2626.
36913.
80000.
1123.
27058.
18571.
51428.
7867.
61411.
137500.
3333.
73333.
1000.
13848.
1014.
23308.
222222.
1029.
39230.
2456.
25000.
1567.
18898.
80000.
1000.
14285.
2456.
16609.
2402.
16683.
80000.
2350.
16758.
909.
4545.
909.
5740.
80000.
909.
7250.
27027.
90357.
7367.
58951.
84269.
2008.
38461.
27027.
71252.
13014.
64964.
177500.
6266.
59230.
2086.
7619.
2824.
17118.
177500.
3823.
09
71
46
77
00
00
67
35
14
67
48
00
61
82
43
57
96
96
00
33
33
00
48
60
51
22
41
77
14
00
21
22
00
00
•71
14
39
48
65
00
00
24
09
45
09
60
00
09
00
03
14
55
46
66
39
54
03
48
20
14
00
67
77
96
05
.81
.42
00
.53
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
19
19
19
19
19
10
10
10
10
10
13
13
13
13
13
24
24
24
24
24
9
9
9
9
9
12
12
12
12
12
19
19
19
19
19
6
8
8
8
8
12
12
12
12
12
21
21
21
21
21
43
22
39
18
2
20
8
24
10
4
18
10
21
8
2
47
24
39
19
2
18
7
20
9
2
.
21
9
21
9
2
41
20
41
18
2
14
4
19
7
6
16
9
19
9
2
39
25
36
19
2
47
58
47
58
61
74
79
64
79
79
78
72
69
66
59
53
61
63
63
61
74
81
74
76
74
69
69
69
69
59
53
61
53
58
61
79
83
71
81
83
78
69
69
69
59
56
56
52
60
61
27
16
24
13
2
24
12
24
14
7
38
22
38
16
3
34
19
32
16
2
21
12
24
12
2
38
19
38
19
3
29
16
29
13
2
19
10
21
12
12
34
19
34
19
3
29
18
24
15
2
19
42
23
45
60
50
67
40
64
71
41
50
31
SO
56
19
42
31
47
60
52
69
50
64
71
31
50
31
50
56
24
45
24
45
60
SO
74
50
69
71
44
50
34
50
56
27
39
27
45
60
42
19
39
16
2
24
7
33
10
2
19
9
28
9
3
42
19
31
15
2
21
5
24
10
2
28
9
28
9
3
37
16
37
16
2
14
24
5
2
16
9
25
9
3
34
23
34
16
2
11
23
15
26
37
2
14
2
12
19
3
19
3
25
38
5
19
6
23
37
5
14
2
14
24
3
22
3
22
38
10
23
10
26
37
7
17
5
14
14
6
22
6
22
38
10
21
15
24
37
-------
APPENDIX 3C:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
411 FLUORANTHN HA28 BT NG/G
412 PYRENE CR14 BT NG/G
412 PYRENE
NG/G
412 PYRENE
HA28
BT NG/G
413 BAA
CR14
BT NG/G
HA14
NG/G
NG/G
414 CHRYSENE CR14 BT NG/G
414 CHRYSENE HA14
BT NG/G
414 CHRYSENE HA28
BT NG/G
SEC
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
c
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
38461.
25675.
81460.
6971.
60545.
80000.
1892.
45000.
25675.
64705.
11990.
71947.
147500.
5600.
80000.
2101.
18333.
2646.
31643.
147500.
3333.
54615.
14285.
54500.
3779.
30661.
80000.
1000.
17250.
14090.
30823.
6129.
30282
80000.
2666.
29750.
1289.
14090.
1135.
16461.
80000.
1000.
19230.
16756.
47794.
4918.
31953.
80000.
1443.
21363.
16756
40588
10674
53302
112500
6800
70000
1637
16756
1642
20261
112500
1647
24500
54
,68
08
.35
,06
,00
,83
00
68
88
,99
69
,00
.00
,00
,45
,33
.66
.04
.00
,33
.38
.71
,00
.64
.46
.00
.00
.00
.91
.53
.91
.01
.00
.67
.00
.86
.91
.72
.44
.00
.00
.77
.76
.12
.75
.97
.00
.84
.64
.76
.24
.55
.69
.00
.00
.00
.68
.76
.36
.80
.00
.06
.00
N
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
TOX EFFECT
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
10
10
10
10
10
13
13
13
13
13
23
23
23
23
23
8
8
8
8
8
12
12
12
12
12
19
19
19
19
19
10
10
10
10
10
13
13
13
13
13
19
19
19
19
19
HIT O
18
5
20
9
6
20
10
21
8
4
41
24
38
16
4
14
5
20
7
4
17
9
20
9
4
37
20
38
17
4
15
6
20
8
S
17
10
20
8
3
39
19
38
17
3
ORREI
74
86
69
81
83
72
72
69
66
66
60
61
55
61
65
79
81
69
81
79
75
69
72
69
66
56
61
55
60
65
81
83
69
83
81
81
72
72
66
63
53
63
52
63
63
415 BBF
415 BBF
415 BBF
CR14 BT NG/G NR X
HA14 BT NG/G NR X
HA28 BT NG/G NR X
19 1
19 1
19 3
21
12
21
14
12
38
22
38
16
9
32
19
27
13
5
19
10
21
12
7
34
19
38
19
9
27
16
27
13
5
21
12
21
14
10
38
22
38
16
6
27
16
26
15
3
52
74
48
67
71
34
50
31
50
56
27
42
27
48
60
60
71
48
69
71
41
50
34
50
56
29
45
27
47
60
60
71
48
69
71
44
50
34
50
56
26
47
26
48
60
21
26
7
2
25
9
28
9
3
34
19
34
13
2
14
2
26
5
2
19
9
25
9
3
32
16
34
15
2
14
2
26
5
2
16
9
25
35
15
35
13
2
5
14
5
12
14
3
19
3
25
31
6
19
11
26
34
7
17
5
14
19
6
22
3
22
31
11
23
11
26
34
5
14
5
12
17
3
19
3
25
34
11
23
13
24
35
-------
APPENDIX 3C:
SUMMARY OF SECS NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
NDMCODE CHEMCODE
416 BKF
416 BKF
416 BKF
417 BAP
TEST SAMPTYP UNITS
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
CR14 BT NG/G
417 BAP
BT
NG/G
HA28
NG/G
418 ICDP
CR14
NG/G
418 ICDP
HA14
NG/G
418 ICDP
HA28
BT
NG/G
419 BGHIP
CR14
BT
NG/G
419 BGHIP
HA14
BT
NG/G
419 BGHIP
HA28
NG/G
SEC
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
12432
125000
3525
50000
80000
1000
20000
12432
36470
7725
26483
80000
4800
19230
1217
11216
1158
13185
80000
1102
15500
8108
94642
2847
36770
80000
1000
14285
7619
26000
5039
26495
80000
3333
27000
1000
9054
1000
8801
80000
1000
8555
13809
112500
4154
40089
80000
1250
14285
8108
31000
5198
28930
80000
3333
27000
1250
10621
1165
11900
80000
1087
13333
-
.43
.00
.97
.00
.00
.00
.00
.43
.59
.00
.15
.00
.00
.77
.39
.22
.75
.27
.00
.94
.00
.11
.86
.47
.11
.00
.00
.71
.05
.00
.53
.28
.00
.33
.00
.00
.05
.00
.28
.00
.00
.56
.52
.00
.74
.19
.00
.00
.71
.11
.00
.75
.95
.00
.33
.00
.00
.21
.92
.26
.00
.50
.33
N
19
19
19
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
57
57
57
57
57
57
57
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
TOX EFFECT HIT CORRE'
1 . . .
1 . . .
3
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
21
21
21
21
21
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
7
7
7
7
7
11
11
11
11
11
18
18
18
18
18
7
7
7
7
7
11
11
11
11
11
16
16
16
16
16
7
7
7
7
7
11
11
11
11
11
18
18
18
18
18
14
4
20
6
5
16
7
20
9
5
37
16
38
15
5
13
4
19
6
5
17
10
20
9
5
.
41
14
41
14
5
12
4
19
6
5
17
9
21
9
5
37
16
38
15
5
79
83
69
79
81
78
75
72
69
69
53
65
52
63
66
76
83
71
79
81
75
66
66
63
69
44
67
44
67
68
79
83
71
79
81
75
69
69
69
69
56
65
55
63
66
19
10
21
10
10
34
19
38
19
13
26
15
26
13
6
17
10
21
10
10
34
19
34
16
13
26
14
26
14
7
17
10
21
10
10
34
19
38
19
13
27
IS
27
13
6
60
74
48
69
71
44
56
34
SO
56
27
50
26
50
60
60
74
50
69
71
41
47
31
47
56
18
53
18
53
61
62
74
50
69
71
41
SO
31
50
56
29
50
27
50
60
26
5
2
16
3
25
9
3
34
11
35
11
2
24
5
2
19
13
28
13
3
46
11
46
11
2
12
24
5
2
19
9
28
9
3
32
11
34
11
2
7
17
5
17
17
6
22
3
22
28
13
24
13
26
32
10
17
5
17
17
6
22
6
25
28
11
23
11
23
30
10
17
5
17
17
6
22
3
22
28
11
24
11
26
32
420 BBKF
CR14
BT
NG/G
NR X
23
-------
APPENDIX 3C:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
420 BBKF
420 BBKF
HA14 BT NG/G
SA28 BT NG/G
421 ACENAPTYLE CR14 BT NG/G
421 ACENAPTYLE HA14 BT NG/G
421 ACENAPTYLE HA28 BT NG/G
422 DBA CR14 BT NG/G
422 DBA HA14 BT NG/G
422 DBA HA28 BT NG/G
423 4-METHNAP CR14 BT NG/G
423 4-METHNAP HA14 BT NG/G
423 4-METHNAP HA28 BT NG/G
450 PAH-T CR14 BT NG/G
450 PAH-T
BT
NG/G
450 PAH-T
HA28
BT NG/G
451 PAH-L
CR14
BT KG/G
451 PAH-L
HA14
BT
NG/G
SEC
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
e
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
1428
2394
1889
4206
192500
2500
7388
714
1000
845
2755
80000
1000
7590
769
1125
877
1936
23250
1000
3333
169190
£51000
52995
502025
1360000
16600
387142
169190
531264
116897
568416
1360000
80766
608166
15449
105200
20865
207877
1360000
28181
410769
31095
191571
13767
123158
640000
6095
79176
31095
138527
24263
157265
640000
18933
178538
.57
.93
.82
.64
.00
.00
.89
.29
.00
.15
.09
.00
.00
.52
.23
.00
.06
.49
.00
.00
.33
.48
.00
.87
.90
.00
.00
.86
.48
.71
.18
.65
.00
.67
.67
.28
.00
.97
.18
.00
.82
.23
.24
.43
.34
.23
.00
.45
.47
.24
.03
.89
.39
.00
.33
.46
N TOX EFFECT
13
43
43
43
43
43
43
43
30
20
45
45
45
45
45
45
45
23
13
43
43
43
43
43
43
43
7
7
7
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
1
13
13
13
13
13
1
1
10
10
10
10
10
1
1
13
13
13
13
13
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
8
8
8
8
8
5
5
5
5
5
8
8
8
8
8
9
9
9
9
9
12
12
12
12
12
23
23
23
23
23
8
8
8
8
8
12
12
12
12
12
HIT C
35
22
31
12
1
33
27
28
10
1
29
14
26
11
1
-
18
7
20
8
4
20
9
20
9
4
49
24
39
19
4
18
7
20
10
2
20
11
20
10
2
ORREC
30
47
35
56
67
27
31
29
56
76
35
56
37
S3
67
74
81
69
79
79
72
69
72
69
66
47
61
56
63
65
74
76
74
74
74
72
69
72
66
59
21
14
19
7
11
7
7
16
9
14
5
21
12
21
12
7
38
19
38
19
9
32
19
29
16
5
21
10
24
12
2
38
22
38
19
3
9
33
16
49
67
16
24
22
56
76
19
47
23
49
67
52
69
48
67
71
34
50
34
SO
56
15
42
27
47
60
52
67
50
62
71
34
47
34
47
56
60
37
53
21
2
62
53
56
22
2
51
23
47
21
2
21
5
26
7
2
25
9
25
9
3
47
19
34
IS
2
21
7
24
12
2
25
13
25
13
3
9
16
12
23
30
11
16
16
22
22
14
21
16
26
30
5
14
5
14
19
3
22
3
22
31
6
19
10
23
34
5
17
2
14
24
3
19
3
22
38
-------
APPENDIX 3C:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRESTOC USING ALL DATA
NDMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
451 PAH-L
HA28
NG/G
452 PAH-H
CR14
BT
NG/G
452 PAH-H
BT
NG/G
452 PAH-H
HA28
BT
NG/G
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
6100
31095
6049
54731
640000
6000
96333
138621
661964
39179
376058
720000
11073
213636
138621
398676
70609
410172
838750
35966
422000
10000
96166
13622
149272
838750
18556
231703
.00
.24
.79
.23
.00
.00
.33
.62
.29
.47
.03
.00
.53
.36
.62
.47
.90
.49
.00
.67
.00
. 00
.67
.10
.01
.00
.15
.30
62
62
62
62
62
62
62
42
42
42
42
42
42
42
32
32
32
32
32
32
32
62
62
62
62
62
62
62
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
21
21
21
21
21
e
8
8
8
8
12
12
12
12
12
22
22
22
22
22
37
23
38
19
2
IS
5
20
7
5
17
9
21
9
5
48
23
38
17
5
60
60
58
60
61
76
81
69
81
81
75
69
69
69
69
45
60
55
60
66
29
18
29
15
2
19
10
21
12
10
34
19
38
19
13
31
18
27
13
6
31
42
29
45
60
57
71
48
69
71
41
50
31
50
56
IS
42
27
47
60
31
19
32
16
2
17
2
26
5
2
19
9
28
9
3
47
19
34
15
2
10
21
10
24
37
7
17
5
14
17
£
22
3
22
28
8
21
11
26
32
508 PCB-T
508 PCB-T
508 PCB-T
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
NR
NR
23
ERL X
ERM
TEL X
PEL
NEC
NERM X
NERH X
1538.
4027.
1754.
3297.
10777.
2000.
2700.
.46
.78
.12
.73
.78
.00
.00
29
29
29
29
29
29
29
10
10
10
10
10
8
8
8
8
8
21
6
18
6
4
41
72
45
72
72
24
14
21
14
10
17
59
24
59
62
48
7
41
7
3
10
21
14
21
24
-------
Appendix 3d Summary of sediment effect concentrations (SECs) calculated using sediment
concentrations normalized to total organic carbon (TOC) concentrations and listed by
chemical, test type, and sample type for the Great Lakes database. See legend to
Appendix 3a for a description of the headings.
-------
APPENDIX 3D:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
401 14-2CLBNZ CR14 BT NG/G
401 14-2CLBNZ HA14 BT NG/G
401 14-2CLBNZ HA28 BT NG/G
402 12-2CLBNZ CR14 BT NG/G
402 12-2CLBNZ HA14 BT NG/G
402 12-2CLBNZ HA28 BT NG/G
403 13-2CLBNZ CR14 BT NG/G
403 13-2CLBNZ HA14 BT NG/G
403 13-2CLBNZ HA28 BT NG/G
404 NAPHTHALENE CR14 BT NG/G
404 NAPHTHALENE HA14 BT NG/G
404 NAPHTHALENE HA28 BT NG/G
405 2-METHNAP CR14 BT NG/G
405 2-METHNAP HA14 BT NG/G
405 2-METHNAP HA28 BT NG/G
406 ACENA CR14 BT NG/G
406 ACENA HA14 BT NG/G
406 ACENA HA28 BT NG/G
407 DIBNZFURAN CR14 BT NG/G
407 DIBNZFURAN HA14 BT NG/G
407 DIBNZFURAN HA28 BT NG/G
408 FLUORENE CR14 BT NG/G
408 FLUORENE HA14 BT NG/G
408 FLUORENE HA28 BT NG/G
SEC C
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
ERL
ERM
TEL
PEL
NEC 9
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
NR X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
CONC
3157.
56818.
4055.
37876.
224719.
5207.
25250.
2619.
15867.
2047.
17468.
80000.
1600.
19230.
2619.
23500.
2654.
21258
80000
2689
19230
3285
20000
2875
20112
80000
2516
20224
2090
17053
1627
18109
80000
1266
19230
1543
17053
2130
18109
N TOX EFFECT
19 2
19 1
19 3
7
7
7
7
7
7
89 27
18 27
.22 27
.89 27
.10 27
.52 27
.00 27
.05 27
,65 27
.07 27
.46 27
.00 27
.00 27
.77 27
.05 27
.00 27
.21 27
.48 27
.00 27
.84 27
.77 27
19
19
19
8
8
8
19
19
19
.71 27
.00 27
.24 27
.05 27
.00 27
.04 27
.72 27
.91 27
.57 27
.42 27
.48 27
.00 27
.67 27
.77 27
.86 27
.57 27
.91 27
.48 27
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
3
1
1
1
1
1
3
11
11
11
11
11
13
13
13
13
13
24
24
24
24
7
7
7
7
7
12
12
12
12
12
11
11
11
11
11
9
9
9
9
9
12
12
12
12
12
12
12
12
12
HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
17
6
15
6
1
21
9
21
9
3
24
8
23
8
3
16
8
17
7
2
21
9
22
9
2
28
10
23
10
76
79
71
79
71
69
69
69
69
63
61
68
60
68
63
74
79
76
76
74
69
69
66
69
59
55
65
56
65
21
10
17
10
38
19
38
19
6
19
10
18
10
3
19
12
21
10
2
38
19
38
19
3
19
10
16
10
55
69
55
69
71
31
50
31
50
56
42
58
42
58
60
55
67
55
67
71
31
50
28
50
56
35
55
40
55
19
5
19
5
2
28
9
28
9
3
19
3
19
3
2
19
7
19
7
2
28
9
31
9
3
26
6
21
6
5
17
10
17
26
3
22
3
22
34
19
29
21
29
35
7
14
5
17
24
3
22
3
22
38
19
29
23
29
-------
APPENDIX 3D:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
408 FLUORENE HA28
409 PHENANTHRN CR14
BT
NG/G
NG/G
409 PHENANTHRN HA14
NG/G
409 PHENANTHRN HA28
NG/G
410 ANTHRACENE CR14
NG/G
410 ANTHRACENE HA14
BT NG/G
410 ANTHRACENE HA28
NG/G
411 FLUORANTHN CR14
BT
NG/G
411 FLUORANTHN HA14
BT
NG/G
411 FLUORANTHN HA28
NG/G
412 PYRENE
CR14
BT
NG/G
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
NEC X 80000.00 27
NERM X 2941.18 27
NERH X 19230.77 27
61
60
37
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
18571.
60714.
17230.
55878.
80000.
15986.
51428.
18571.
51428.
11512.
37263.
80000.
7137.
27000.
6140.
40000.
9907.
39613.
80000.
15986.
39230.
2456.
25000.
3756.
21926.
80000.
5744.
19230.
2456.
16609.
2324.
17872.
80000.
2200.
19230.
2200.
16609.
3908.
17872.
80000.
6944.
19230.
27027.
90357.
19784.
70203.
84269.
14482.
54545.
27027.
71252.
10165.
46233.
80000.
3823.
30000.
43
29
61
88
00
59
57
43
57
99
54
00
25
00
35
00
74
52
00
59
77
14
00
38
45
00
95
77
14
39
54
08
00
00
77
00
39
68
08
00
44
77
03
14
49
79
66
76
45
03
48
56
91
00
53
00
6333.33
71252.48
9577.27
56439.39
80000.00
14482.76
44705.88
25675.68
81460.08
25768.70
71556.61
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
9
9
9
9
9
13
13
13
13
13
13
13
13
13
13
9
9
9
9
9
12
12
12
12
12
12
12
12
12
12
8
8
8
8
8
12
12
12
12
12
12
12
12
12
12
10
10
10
10
16
7
16
7
4
18
10
20
12
5
26
13
25
13
7
18
7
17
7
2
21
9
21
9
2
25
10
20
10
2
14
4
15
7
6
16
9
19
11
9
27
10
23
11
10
18
5
17
6
79
81
79
81
79
78
72
72
72
63
65
66
63
66
63
74
81
71
81
74
69
69
69
69
59
60
65
61
65
61
79
83
76
81
83
78
69
69
75
69
56
65
56
66
65
74
86
71
83
21
12
21
12
7
38
22
38
25
9
23
13
21
13
6
21
12
19
12
2
38
19
38
19
3
19
10
16
10
2
19
10
19
12
12
34
19
34
25
19
19
10
16
11
10
21
12
19
12
57
69
57
69
71
41
50
34
47
S3
42
53
42-
53
56
52
69
52
69
71
31
50
31
50
56
40
55
45
55
60
60
74
57
69
71
44
50
34
50
50
37
55
40
55
55
52
74
52
71
17
5
17
5
2
19
9
25
13
6
19
8
19
8
5
21
5
21
5
2
28
9
28
9
3
21
6
16
6
2
14
17
5
2
16
9
25
9
9
24
6
21
6
6
21
21
2
5
14
5
14
19
3
19
3
16
31
16
26
18
26
32
5
14
7
14
24
3
22
3
22
38
19
29
23
29
37
7
17
7
14
14
6
22
6
16
22
19
29
23
27
29
5
14
7
14
-------
APPENDIX 3D: SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
412 PYRENE CR14 BT NG/G
412 PYRENE HA14 BT NG/G
412 PYRENE HA28 BT NG/G
413 BAA CR14 BT NG/G
413 BAA HA14 BT NG/G
413 BAA HA28 BT NG/G
414 CHRYSENE CR14 BT NG/G
414 CHRYSENE HA14 BT NG/G
414 CHRYSENE HA28 BT NG/G
415 BBF CR14 BT NG/G
415 BBF HA14 BT NG/G
415 BBF HA28 BT NG/G
416 BKF CR14 BT NG/G
416 BKF HA14 BT NG/G
416 BKF HA28 BT NG/G
NEC
NERM X
NERH X
ERL
ERM
TEL X
PEL
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
NR X
NR X
NR X
80000.00 27
11
10
6
83
12
71
2
14
25862.07 27 ....
62857.
25675.
64705.
17083.
53960.
80000.
11366.
45000
4400
64705
10784
59446
80000
26431
54615
14285
54500
11097
38360
80000
8620
27000
14090
30823
4597
24346
80000
1500
19230
5666
30823
6989
27360
80000
8620
24285
16756
47794
14311
35922
80000
12222
27000
16756
40588
9905
27938
80000
5855
19230
2400
40588
5083
32411
80000
10766
25882
.14 27
.68 27
.88 27
.53 27
.77 27
.00 27
.67 27
.00 27
.00 27
.88 27
.09 27
.92 27
.00 27
.03 27
.38 27
.71 27
.00 27
.42 27
.14 27
.00 27
.69 27
.00 27
.91 27
.53 27
.43 27
.67 27
.00 27
.00 27
.77 27
.67 27
.53 27
.32 27
.03 27
.00 27
.69 27
.71 27
.76 27
.12 27
.00 27
.71 27
.00 27
.22 27
.00 27
.76 27
.24 27
.24 27
.20 27
.00 27
.17 27
.77 27
.00 27
.24 27
.22 27
.71 27
.00 27
.28 27
.35 27
19
19
19
19
19
19
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
-
1
1
3
1
1
3
13
13
13
13
13
13
13
13
13
13
8
8
8
8
8
12
12
12
12
12
12
12
12
12
12
10
10
10
10
10
13
13
13
13
13
13
13
13
13
13
20
10
21
12
8
33
11
25
12
9
14
5
17
6
4
17
9
21
11
4
25
11
23
12
4
15
6
16
8
5
17
10
20
10
6
33
10
26
11
6
72
72
69
72
66
53
66
63
65
63
79
81
76
79
79
75
69
69
69
66
63
66
60
68
65
81
83
79
83
81
81
72
72
72
66
56
68
58
66
65
38
22
38
25
16
23
11
21
11
8
19
10
21
10
7
34
19
38
22
9
21
11
18
13
5
21
12
21
14
10
38
22
38
22
13
24
11
19
11
6
34
50
31
47
SO
31
55
42
53
55
60
71
55
69
71
41
50
31
47
56
42
55
42
55
60
60
71
57
69
71
44
50
34
50
53
32
56
39
55
58
25
9
28
13
9
31
6
19
8
6
14
2
19
5
2
19
9
28
13
3
19
6
19
6
2
14
2
17
5
2
16
9
25
9
6
29
5
23
6
3
3
19
3
16
25
16
27
18
27
31
7
17
5
17
19
6
22
3
19
31
18
27
21
26
34
5
14
5
12
17
3
19
3
19
28
15
27
19
27
32
-------
APPENDIX 3D:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
NUMCODE CHEMCODE TEST SAMPTYP UNITS
SEC C
CR14
NG/G
417 BAP
HA14
BT
NG/G
417 BAP
HA28
NG/G
418 ICDP
CR14
NG/G
418 ICDP
BT NG/G
418 ICDP
HA28
NG/G
419 BGHIP
BT NG/G
419 BGHIP
HA14
BT
NG/G
CONC
# # ft TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
419 BGHIP
HA28
BT
NG/G
420 BBKF CR14 BT NG/G
420 BBKF HA14 BT NG/G
420 BBKF HA28 BT NG/G
421 ACENAPTYLE CR14 BT NG/G
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM
TEL
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL
ERM
TEL
PEL
NEC
NERM X
NERH X
ERL
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
NR X
12432.
125000.
10359.
56180.
80000.
8632.
25250.
12432.
36470 .
7117.
26483.
80000.
4075.
19230.
10000.
36470.
6383.
27401.
80000.
4075.
20588.
8108.
94642.
7585.
46772.
80000.
7097.
23115.
7619.
26000.
5S01.
22360.
80000.
3972.
19230.
7619.
26000.
4613.
22360.
80000.
2794.
19230.
13809.
112500.
9899.
50994.
80000.
7097.
23115.
8108.
31000.
5781.
24416.
80000.
4122.
19230.
8108.
23147.
6588.
21098.
80000.
5352.
19230.
43
00
49
51
00
18
00
43
59
88
15
00
16
77
00
59
70
92
00
16
24
11
86
85
92
00
22
38
05
00
32
68
00
22
77
05
00
95
68
00
12
77
52
00
96
91
00
22
38
11
00
30
26
00
22
77
11
06
04
24
00
94
77
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
8
8
8
15
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
21
21
21
21
21
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
1
1
1
1
7
7
7
7
7
11
11
11
11
11
11
11
11
11
11
7
7
7
7
7
11
11
11
11
11
11
11
11
11
11
7
7
7
7
7
11
11
11
11
11
•
12
12
12
12
12
14
4
15
6
5
16
7
20
9
5
19
7
22
7
5
13
4
IS
5
5
17
10
20
10
5
18
10
22
10
5
12
4
14
5
5
17
9
20
10
5
18
10
21
10
5
79
83
76
79
81
78
75
72
69
69
63
69
60
69
66
76
83
76
81
81
75
66
66
66
69
67
67
63
67
68
79
83
74
81
81
75
69
66
66
69
68
65
63
65
66
19
10
19
10
10
34
19
38
19
13
16
10
18
10
6
17
10
19
10
10
34
19
34
19
13
18
11
19
11
7
17
10
17
10
10
34
19
34
19
13
18
10
18
10
6
60
74
57
69
71
44
56
34
50
56
47
60
42
60
60
60
74
57
71
71
41
47
31
47
56
49
56
44
56
61
62
74
57
71
71
.
41
50
31
47
56
-
50
55
45
55
€0
14
17
5
2
16
3
25
9
3
15
2
19
2
2
14
17
2
2
19
13
28
13
3
14
7
19
7
2
12
17
2
2
19
9
28
13
3
11
6
16
6
2
7
17
7
17
17
6
22
3
22
28
23
29
21
29
32
10
17
7
17
17
6
22
6
22
28
19
26
18
26
30
10
17
10
17
17
6
22
6
22
28
21
29
21
29
32
-------
APPENDIX 3D:
SOMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
421 ACENAPTYLE HA14
421 ACENAPTYLE HA28
422 DBA CR14
422 DBA HA14
422 DBA HA28
423 4-METHNAP CR14
423 4-METHNAP HA14
423 4-METHNAP HA28
450 PAH-T CR14
450 PAH-T
450 PAH-T
HA28
451 PAH-L
CR14
451 PAH-L
451 PAH-L
HA28
452 PAH-H
CR14
452 PAH-H
HA14
iMPTYP UNITS
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
BT NG/G
SEC
NR
NR
NR
NR
NR
NR
NR
NR
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
NERM
NERH
ERL
ERM
TEL
PEL
NEC
C
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
CONC
169190.
651000.
171981.
581265.
1360000.
174818.
519000.
169190.
531264.
133412.
467147.
1360000.
105200.
410769.
22754.
411529.
63070.
411149.
1360000.
174818.
410769.
31095.
191571.
37916.
229942.
640000.
46235.
276000.
31095.
138527.
23570.
159251.
640000.
17866.
183076.
14228.
91054.
28790.
129111.
640000.
58256.
183076.
138621.
661964.
116513.
401070.
720000.
97931.
243000.
138621.
398676.
47680.
301289.
720000.
N TOX EFFECT
IS 1
15 1
8 1
8 1
8 1
7
7
48
00
23
00
00
01
00
48
71
29
94
00
00
23
39
41
41
15
00
01
23
24
43
98
85
00
29
00
24
03
50
69
00
67
92
07
05
24
95
00
54
92
62
29
34
22
00
03
00
62
47
13
84
00
7
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
27
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
24
24
24
24
24
11
11
11
11
11
13
13
13
13
13
9
9
9
9
9
12
12
12
12
12
13
13
13
13
13
8
8
8
8
8
12
12
12
12
12
13
13
13
13
13
8
8
8
8
8
12
12
12
12
12
HIT C
18
7
17
7
4
20
9
20
10
4
36
12
24
12
4
18
7
16
6
2
20
11
20
10
2
27
15
23
12
2
15
5
16
7
5
17
9
21
10
6
ORREC
74
81
71
81
79
72
69
72
66
66
55
65
61
65
65
74
76
74
74
74
72
69
72
66
59
63
63
60
61
61
76
81
79
81
81
75
69
69
72
66
21
12
19
12
7
38
19
38
19
9
26
11
19
11
5
21
10
19
7
2
38
22
38
19
3
23
13
18
10
2
19
10
21
12
10
34
19
38
22
13
52
69
52
69
71
34
50
34
47
56
29
S3
42
53
60
52
67
55
67
71
34
47
34
47
56
40
50
42
52
60
57
71
57
69
71
41
50
31
50
S3
21
5
21
5
2
25
9
25
13
3
32
8
19
8
2
21
7
19
7
2
25
13
25
13
3
21
11
19
10
2
17
2
17
5
2
19
9
28
9
6
5
14
7
14
19
3
22
3
22
31
13
27
19
27
34
5
17
7
19
24
3
19
3
22
38
16
26
21
29
37
7
17
5
14
17
6
22
3
19
28
NERM X 16400.00 27
NERH X 227692.31 27
-------
APPENDIX 3D:
SUMMARY OF SECs NORMALIZED TO TOTAL ORGANIC CARBON
SEC IN THRGLTOC USING GL DATA
NOMCODE CHEMCODE TEST SAMPTYP UNITS
452 PAH-H
508 PCB-T
508 PCB-T
508 PCB-T
HA28
BT
NG/G
CR14 BT NG/G
HA14 BT NG/G
HA28 BT NG/G
SEC C
CONC
# # # TOTAL
N TOX EFFECT HIT CORRECT TOXHIT NOTNOT NOTHIT TOXNOT
ERL X
ERM X
TEL X
PEL X
NEC X
NERM X
NERH X
NR X
NR X
NR X
87333
398676.
92480.
306551.
720000,
97931.
235714.
.33
.47
.50
.37
.00
.03
.29
27
27
27
27
27
27
27
e
8
8
24
24
24
24
24
2
2
2
12
12
12
12
12
24
9
23
11
6
.
-
61
66
60
66
65
19
10
18
11
6
42
56
42
55
58
19
5
19
6
3
19
29
21
27
32
-------
Appendix 4a Data grouped by chemical, test type, sample type, toxicity response, and sediment
concentrations normalized to dry weight (in ascending order). A value bracketed by
"~~" indicate published SECs (see Appendix 5). See Appendix 2c for a description of
the chemical name for each abbreviated CHEMCODE. See Appendix 3a for
additional descriptions of the headings for the columns. If SECs for a particular
chemical are not reported (NR) for a test type and sample type in both Appendix 3 a
and Appendix 3b, then an ascending data table is not included in Appendix 4a for
those SECs. If SECs for a particular chemical are not reported for a test type and
sample type in Appendix 3a or in Appendix 3b, then these particular SECs for this
particular test type and sample type are not reported in the ascending data table.
Examples are included for copper and benzo[a]pyrene. The computer disk that
accompanies the report contains the electronic version of this entire appendix (file
name: "apdx4a.wp").
CONC Concentration.
EFFECT
NE Non-toxic sample.
NC No concordance (concentration of the chemical in a toxic sample was less than
the mean concentration of the chemical in the non-toxic samples at a site;
designated as no effect in the calculations of SECs).
SG Small gradient (concentration of the chemical in a toxic sample 1 to <2 times
the mean concentration of the chemical in the non-toxic samples at a site).
* Concentration of the chemical in a toxic sample 2 to <4 times the mean
concentration of the chemical in the non-toxic samples at a site.
** Concentration of the chemical in a toxic sample >4 the mean concentration of
the chemical in the non-toxic samples at a site.
RATIO Concentration of the chemical in the sample divided by the mean concentration
of the chemical in the non-toxic samples at a site.
SITE 1: Indiana Harbor, 2: Buffalo River, 3: Saginaw River (1 st survey), 4: Saginaw
River (3rd survey), 5: Waukegan Harbor, 6: Upper Mississippi River, 7:
Milltown Reservoir of the Clark Fork River, 8: Clark Fork River, 9: Trinity
River, 10: Mobile Bay, 11: Tabbs Bay in Galveston Bay.
SAMPLE Sample identification code. CO: control, RE: reference.
CEN Censor. An @ indicates unreliable SEC (e.g., less than five of the samples
were designated as toxic for the chemical or the frequency of toxic samples
below the SEC was greater than the frequency of toxic samples above the
SEC).
TOXICALL Survival, growth, or maturation significantly less than the control response
(p<0.05).
SURV Percentage survival normalized to the control response.
NT Response not significantly less than the control response (p>0.05).
TX Response significantly less than the control response (p<0.05).
GROW Percentage growth normalized to the control response.
MATURE Percentage maturation normalized to the control response (Hyalella azteca
only).
ND Not determined.
MINTOX Minimum concentration in a toxic sample.
-------
CONC £
890.0
1017.0
1144.0
1334.0
1843.0
1843.0
2224.0
2796.0
2923.0
2986.0
3050.0
3177.0
3939.0
4384.0
5042.0
5700.0
6989.0
9248.7
10600.0
12000.0
12000.0
12000.0
12000.0
12000.0
12000.0
12000.0
12000.0
15694.0
16965.0
16965.0
17791.0
50079.9
77000.0
141000.0
178000.0
185000.0
209000.0
233000.0
251000.0
287000.0
325000.0
325000.0
354000.0
607000.0
6971000.0
.\JUCM-
5FFEC
NC
NE
NC
NE
NE
NC
NE
NE
NE
NC
NE
NC
NC
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
NE
SG
NE
*
*
NE
*
NE
*
**
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=bottom sediment - sem UNlTS=ng/g
GL-SECs NOT REPORTED
0.1 3 SR-1-10
4 SR-3-06
0.1 3 SR-1-06
4 SR-3-02
4 SR-3-05
0.3 2 BR-1-09
2 BR-1-08
4 SR-3-24
4 SR-3-16
0.4 2 BR-1-07
4 SR-3-08
0.3 3 SR-1-03
0.6 2 BR-1-01
0.6 2 BR-1-03
NERM-50% NO EFFECT
7 MR-l-CO
0.6 1 IH-1-06
TEL-SR(ERL*NERM)
0.1 7 MR-1-01
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
NERH-85% NO EFFECT
1.3 1 IH-1-04
1.4 1 IH-1-07
ERL-15% EFFECT
1.5 1 IH-1-03
PEL-SR(ERM*NERH)
8 CF-1-05
1.5 7 MR-1-02
7 MR-1-25
2.0 7 MR-1-17
ERM-50% EFFECT
2.5 7 MR-1-07
8 CF-1-04
2.1 8 CF-1-03
8 CF-1-02
NEC-MAX NO EFFECT
3.9 7 MR-1-19
6.6 7 MR-1-11
51.5 8 CF-1-01
leaiment. - sem uwiiB=ng/g
'OXIC SURV TOXS
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
100
100
10
103
96
88
97
102
96
80
88
96
89
79
100
1
108
100
100
100
100
100
120
100
0
0
1
114
109
109
115
91
128
123
102
114
90
64
.0
.0
.3
.8
.1
.2
.4
.6
.1
.3
.3
.2
.5
.0
.0
.4
.1
.0
.0
.0
.0
.0
.3
.0
.0
.0
.4
.9
.3
.3
.1
.9
.4
.0
.7
.0
.7
.9
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
GROW
97
92
60
10
94
92
10
10
10
85
92
91
96
85
10
68
79
ND
10
10
10
10
10
10
ND
ND
96
98
92
95
92
91
10
82
94
89
58
73
TOXG MATURE
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
TX
TX
NT
TX
NT
TX
TX
TX
10
96
37
10
11
10
10
10
95
10
95
10
10
10
10
0.
68
ND
10
10
10
10
90
10
ND
ND
0.
77
95
12
65
31
80
93
48
63
24
25
TOXM
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
-------
IY UIT
CONC ;
1700.0
7300.0
8800.0
9500.0
9600.0
10200.0
10400.0
10400.0
11000.0
13000.0
16000.0
16000.0
16000.0
18000.0
18300.0
18700.0
19000.0
19000.0
19000.0
19000.0
19000.0
19000.0
19000.0
19500.0
20300.0
24000.0
26500.0
28012.5
28012.5
29900.0
32800.0
33100.0
34000.0
35700.0
41300.0
41300.0
41300.0
45600.0
48700.0
49000.0
49800.0
49800.0
51900.0
54800.0
54800.0
54800.0
67000.0
78026.0
96500.0
101230.4
108000.0
110000.0
122250.0
128000.0
148000.0
182000.0
187000.0
187000.0
197000.0
226000.0
266000.0
270000.0
287000.0
364000.0
379000.0
390000.0
L.UJJE.:
EFFE<
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
NE
NE
SG
NE
SG
*
NE
NE
NE
*
**
NE
**
*+
* +
**
SG
**
SG
**
APPENDIX a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NOMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
0.2 11 TB-1-01
11 TB-l-RE
9 TR-1-03
5 WH-l-RE
9 TR-1-04
9 TR-1-01
5 WH-l-CO
9 TR-1-02
1.1 11 TB-1-02
11 TB-1-04
0.8 3 SR-1-10
8 CF-1-06
slcl——
1.8 11 TB-1-03
4 SR-3-06
—telm—
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
2.0 5 WH-1-01
4 SR-3-01
4 SR-3-02
8 CF-l-CO
TEL-SR (ERL*NERM)
GL - TEL - SR (ERL*NERM)
0.1 7 MR-1-01
7 MR-l-CO
4 SR-3-05
-erl—-
—telf~~
1.3 2 BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
2 BR-1-08
1.5 2 BR-1-07
2.6 3 SR-1-03
4 SR-3-24
GL-NERH-85% NO EFFECT
4 SR-3-15
4 SR-3-08
NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
2.1 2 BR-1-03
GL-PEL-SR(ERM*NERH)
9.7 5 WH-1-02
PEL-SR(ERM*NERH)
—pelm—
slc2
GL-ERM-50% EFFECT
8 CF-1-05
4.6 2 BR-1-01
9.6 1 IH-1-04
9.8 3 SR-1-06
ERM-50% EFFECT
—pelf —
11.9 1 IH-1-03
1.2 7 MR-1-02
—erm—
15.1 1 IH-1-07
1.6 7 MR-1-19
19.9 1 IH-1-06
=VA-*.UIdlU UWL
roxic SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
0
100
98
109
82
81
100
100
11
93
100
120
52
100
100
100
100
100
100
71
97
103
100
108
100
96
88
97
80
96
102
96
88
.0
.0
.6
.5
.9
.4
.0
.0
.4
.2
.0
.3
.3
.0
.0
.0
.0
.0
.0
.7
.4
.8
.0
.1
.0
.1
.2
.4
.3
.2
.6
.1
.3
.ax uj
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
.1 i iw> = .
GROW
ND
10
ND
11
ND
ND
10
ND
72
10
97
10
97
92
ND
10
10
10
10
91
94
10
10
79
10
94
92
10
85
91
10
10
92
iiy/y -
TOXG
ND
NT
ND
NT
ND
ND
NT
ND
TX
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
90
ND
96
ND
10
10
10
10
ND
11
10
10
68
10
11
10
10
10
10
10
95
95
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TOX
TOX
79.0 TX
36.5 TX
85
74
NOT 114.9 NT 98
TOX 89.5 TX 96
TOX 0.0 TX ND
TOX 10.3 TX 60
TOX 1.4 TX
TOX 109.3 NT
TOX
TOX
TOX
0.0 TX
114.0 NT
1.4 TX
96
92
ND
89
68
TX
TX
NT
NT
ND
TX
NT
TX
ND
TX
NT
10
ND
77
10
ND
37
0.
95
ND
63
0.
NT
ND
NT
NT
ND
TX
NT
NT
ND
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 * 2-4 | **>4
-- NUMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG
390000.
410000,
411000,
459000.
478000.
480000,
530000.
583000.
583000.
840000.
878000
1300000
7820000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
SG
*
NE
SG
NE
*
**
1.9
2.1
1.9
4.0
31.7
7
7
7
8
8
8
7
8
~~aet2— •
MR-1-25
MR-1-07
MR-1-17
CF-1-04
CF-1-03
— aet3~
CF-1-02
NEC-MAX NO EFFECT
~~aets~-
MR-1-11
— aetl—
CF-1-01
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
109
91
115
128
123
102
90
54
.3
.9
.1
.4
.0
.7
.7
.9
NT
TX
NT
NT
NT
NT
NT
TX
95
91
92
10
82
94
58
73
NT
TX
TX
NT
TX
NT
TX
TX
12
31
65
80
93
48
24
25
NT
TX
NT
NT
NT
NT
TX
TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER <--) SECs
ME no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=porewater UNITS=ug/l
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.6
1.1
1.3
1.5
1.7
1.7
1.9
2.3
2.6
2.7
2.7
3.0
3.0
3.0
3.3
3.3
3.7
3.7
4.4
4.7
4.7
4.7
4.7
4.7
4.7
4.7
4.7
5.3
5.3
5.4
8.7
8.8
8.8
9.5
9.5
13.2
14.8
15.1
16.4
19.1
19.5
19.8
19.8
21.4
35.6
35.6
79.4
89.9
102.0
126.3
NC
NE
NC
NE
NE
NC
NC
NC
NC
NE
NE
NE
SG
NC
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
SG
NE
SG
* *
**
**
NE
**
**
**
**
0
0
0
0
0
0
1
0
1
0
1
1
4
4
4
6
8
10
27
.1
.
.4
.5
.2
.7
.6
.
.
.0
.
.4
.
.
.1
.
.
.9
.
.4
.4
.1
.
.2
.6
.7
.8
.0
.0
3
4
2
8
2
2
7
2
3
.
4
4
4
2
.
7
.
.
9
4
3
1
8
2
1
7
8
8
7
7
7
8
1
3
1
8
8
7
7
1
SR-1-03
SR-3-02
BR-1-03
CF-1-06
BR-1-08
BR-1-07
MR-1-01
BR-1-09
SR-1-10
GL-NERM-50% NO EFFECT
SR-3-01
GL-TEL-SR(ERL*NERM) ®
SR-3-08
SR-3-06
BR-1-01
GL-ERL-15% EFFECT
MR-1-02
NERM-50% NO EFFECT
TEL-SR(ERL*NERM) 8
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-06
ERL-15% EFFECT
MR-l-CO
CF-1-05
CF-1-04
NERH-85% NO EFFECT
MR-1-07
GL-PEL-SR (ERM*NERH)
PEL-SR (ERM*NERH)
MR-1-17
MR-1-25
CF-1-03
IH-1-04
GL-ERM-50% EFFECT
SR-1-06
ERM-50% EFFECT
IH-1-03
CF-1-02
NEC-MAX NO EFFECT
CF-1-01
MR-1-11
MR-1-19
IH-1-07
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
96.2
103.8
79.0
120.3
97.4
80.3
108.1
88.2
100.0
.
97.4
.
88.3
100.0
89.5
.
109.3
.
.
100.0
100.0
100.0
100.0
100.0
100.0
.
1.4
100.0
114.9
128.4
.
91.9
.
115.1
109.3
123.0
0.0
10.3
1.4
102.7
64.9
90.7
114.0
0.0
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
TX
TX
NT
TX
NT
NT
TX
91
10
85
10
10
85
79
92
97
94
92
92
96
92
ND
10
10
10
10
10
68
10
98
10
91
92
95
82
ND
60
96
94
73
58
89
ND
TX
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
ND
TX
NT
NT
TX
TX
TX
ND
10
10
10
90
10
10
68
10
10
11
95
96
10
95
ND
10
10
10
10
10
0.
10
77
80
31
65
12
93
ND
37
0.
48
25
24
63
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
ND
TX
NT
NT
TX
TX
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (~~) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total
CONG EFFE<
0
6
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
12
15
20
20
20
24
25
30
31
32
41
48
56
62
80
82
84
84
87
88
100
100
100
160
167
180
210
220
220
230
250
250
270
270
280
280
319
350
409
430
440
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.0
.0
.0
.0
.9
.4
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.5
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.1
.0
.0
NE
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NG
NG
NG
NG
NG
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
SG
NE
NC
NE
NE
**
NE
NE
NE
NE
**
NE
NE
NE
NE
NE
**
NE
NE
NE
NE
NE
**
NE
NE
11 TB-l-RE
0.6 3 SR-1-10
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
9 TR-1-02
1.0 11 TB-1-03
1.0 11 TB-1-01
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
7 MR-1-25
1.0 7 MR-1-17
1.0 7 MR-1-11
1.0 7 MR-1-07
1.0 7 MR-1-02
1.0 7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-05
8 CF-1-04
0.9 8 CF-1-03
2 BR-l-CO
NERM-50* NO EFFECT
8 CF-1-02
6 UM-l-RE
11 TB-1-04
2.0 11 TB-1-02
9 TR-1-01
1.0 5 WH-1-02
6 UM-1-01
~~telf~~
TEL-SR(ERL*NERM)
5 WH-l-RE
4.8 7 MR-1-19
5 UM-1-02
9 TR-1-04
9 TR-1-03
6 UM-1-03
7.6 8 CF-1-01
ERL-15% EFFECT
10 MB-1-03
—telm—
10 MB-l-RE
10 MB-1-02
GL-NERM-50% NO EFFECT
4 SR-3-06
GL-TEL-SR(ERL*NERM)
10 MB-1-04
21.0 3 SR-1-06
4 SR-3-05
NERH-85% NO EFFECT
4 SR-3-16
4 SR-3-08
4 SR-3-02
4 SR-3-01
GL-NERH-85% NO EFFECT
28.0 3 SR-1-03
GL-ERL-15% EFFECT
PEL-SR(ERM*NERH)
2 BR-1-08
GL-PEL-SR(ERM*NERH)
—erl—
4 SR-3-24
MI set
70XIC
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
ii.meu
SU
100
100
100
100
100
100
52
0
100
100
100
109
115
90
91
109
108
100
100
120
114
128
123
100
102
86
93
11
81
36
119
109
114
117
82
98
114
64
95
100
97
100
95
10
96
96
88
103
97
L. -
RV
.0
.0
.0
.0
.0
.0
.3
.0
.0
.0
.0
.3
.1
.7
.9
.3
.1
.0
.0
.3
.9
.4
.0
.0
.7
.5
.2
.4
.4
.5
.3
.5
.0
.9
.9
.6
.9
.9
.5
.0
.0
.0
.5
.3
.1
.1
.3
.8
.4
L.UUC
TOXS
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ix u«.
GROW
10
97
10
ND
ND
ND
97
ND
10
10
10
95
92
58
91
92
79
10
10
10
98
10
82
10
94
ND
10
72
ND
74
ND
11
89
ND
ND
ND
ND
73
ND
ND
ND
92
ND
60
94
10
92
10
94
Lio=uy
TOXG
NT
TX
NT
ND
ND
ND
NT
ND
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
ND
NT
TX
ND
TX
ND
NT
TX
ND
ND
ND
ND
TX
ND
ND
ND
NT
ND
TX
NT
NT
NT
NT
NT
/a
MATURE
ND
10
ND
ND
ND
ND
ND
ND
10
10
10
12
65
24
31
95
68
10
10
90
77
80
93
10
48
ND
ND
ND
ND
ND
ND
ND
63
ND
ND
ND
ND
25
ND
ND
ND
96
ND
37
11
95
95
10
11
TOXM
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
TX
ND
ND
ND
NT
ND
TX
NT
NT
NT
NT
NT
TOX
NOT
NOT
96.2 NT
91
TX
97.4 NT 10 NT
102.6 NT
10
NT
10
10
10
NT
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
LU-'C^tx / \_n
CONC EFFECT
440
440
450
465
470
620
620
763
782
1000
1000
1580
1600
1600
1600
3000
3600
5800
7000
10000
18200
21000
22000
25000
.0 *
.0
.0 **
.0
.0 *
.0 *
.0
.0
.0
.0 NE
.0
.0
.0
.0
.0
.0
.0
.0 **
.0 **
.0 **
.0
.0 **
.0
.0 **
C<1 I—-I3C11«
-------
Appendix 4b PAH or PCB data grouped by chemical, test type, sample type, toxicity response, and
sediment concentrations normalized to total organic carbon (TOC; in ascending order).
See legend for Appendix 4a for a description of the headings. An example is included
for benzo[a]pyrene. The computer disk that accompanies the report contains the
electronic version of this entire appendix (file name: "apdx4b.wp").
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 [ SG 1-2 | * 2-4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC I
2.0
149.3
312.5
322.6
370.4
416.7
438.6
526.3
600.0
697.7
714.3
833.3
833.3
882.4
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1102.9
1158.8
1205.9
1217.4
1217.4
1250.0
1250.0
1428.6
1666.7
1818.2
1818.2
2900.0
3111.1
3333 .3
3692.3
3727.3
4075.2
4800.0
5000.0
6383 .7
6944.4
7931.0
9000.0
9333.3
10000.0
10000.0
11000.0
11111.1
11216.2
12432.4
13185.3
15500.0
15500.0
15714.3
19230.8
20000.0
20588.2
20588.2
23500.0
26666.7
27000.0
27401.9
-1 U. /
SFFEC
NE
NE
NE
NE
NC
NC
NC
NC
NC
NE
SG
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
*
NE
NE
NE
NE
SG
NE
NE
NE
**
NE
NE
* *
NE
NE
NE
* *
**
NE
NE
it *
NE
NE
NE
SG
NE
*
NE
NE
11 TB-l-RE
8 CF-1-06
7 MR-1-25
8 CF-1-04
0.6 7 MR-1-11
0.7 7 MR-1-07
0.4 5 WH-1-02
0.9 7 MR-1-17
0.6 3 SR-1-10
6 UM-1-01
1.2 8 CF-1-03
8 CF-l-CO
8 CF-1-05
8 CF-1-02
1.0 11 TB-1-03
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
5 WH-l-RE
2.0 8 CF-1-01
ERL-15% EFFECT
2.0 7 MR-1-02
10 MB-l-RE
6 UM-l-RE
10 MB-1-02
11 TB-1-04
2.0 11 TB-1-02
10 MB-1-03
6 UM-1-02
9 TR-1-02
6.0 7 MR-1-19
6 UM-1-03
GL-NERM-50% NO EFFECT
9 TR-1-01
5.5 11 TB-1-01
GL - TEL - SR (ERL*NERM)
4 SR-3-08
4 SR-3-16
10 MB-1-04
9.3 3 SR-1-03
10.0 3 SR-1-06
GL-ERL-15% EFFECT
4 SR-3-24
10 MB-1-01
ERM-50% EFFECT
11.3 5 WH-1-01
PEL-SR(ERM*NERH)
9 TR-1-04
NERH-85% NO EFFECT
4 SR-3-05
4 SR-3-02
1.9 2 BR-1-09
2 BR-1-08
GL-NERH-85% NO EFFECT
2.2 2 BR-1-03
9 TR-1-03
4 SR-3-01
GL-PEL-SR(ERM*NERH)
>m sediment -
:oxic SURV
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
100.
120.
109.
128.
90.
91.
36.
115.
100.
119.
123.
100.
114.
102.
52.
100.
100.
100.
100.
100.
100.
108.
100.
100.
109.
64.
109.
100.
86.
97.
93.
11.
95.
117.
100.
114.
114.
81.
0.
88.
96.
95.
96.
10.
102.
75.
71.
82.
96.
103.
88.
97.
79.
98.
97.
0
3
3
4
7
9
5
1
0
3
0
0
9
7
3
0
0
0
0
0
0
1
0
0
5
9
3
0
5
0
2
4
5
9
0
0
9
4
0
3
1
5
2
3
€
8
7
9
1
8
2
4
0
6
4
UOtc
TOXS
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
IX UJ.MJ
GROW
10
10
95
10
58
91
74
92
97
ND
82
10
98
94
97
10
10
ND
ND
10
10
79
10
10
11
73
92
ND
ND
ND
10
72
ND
ND
ND
89
ND
ND
ND
92
10
ND
91
60
10
ND
91
ND
94
10
92
10
85
ND
94
L i£>=ng
TOXG
NT
NT
NT
NT
TX
TX
TX
TX
TX
ND
TX
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
NT
TX
TX
ND
ND
ND
NT
TX
ND
ND
ND
TX
ND
ND
ND
NT
NT
ND
TX
TX
NT
ND
NT
ND
NT
NT
NT
NT
TX
ND
NT
/g -
MATURE
ND
90
12
80
24
31
ND
65
10
ND
93
10
77
48
ND
10
ND
ND
ND
10
10
68
10
10
ND
25
95
ND
ND
ND
ND
ND
ND
ND
ND
63
ND
ND
ND
95
95
ND
10
37
10
ND
ND
ND
11
10
10
10
10
ND
11
TOXM
ND
NT
NT
NT
TX
TX
ND
NT
NT
ND
NT
NT
NT
NT
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
NT
NT
ND
NT
TX
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=41"7 CHEM=Benzo (a) pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC
BR-1-07
GL-ERM-50% EFFECT
BR-1-01
SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-04
IH-1-03
IH-l-OS
IH-1-07
36470
36470
65168
80000
80000
80000
125000
129870
215517
238636
.6
.6
.S
.0
.0
.0
.0
.1
.2
.4
*
**
NE
* *
**
**
**
3
6
125
129
215
238
.4
.0
.0
.9
.5
.6
2
2
4
1
1
1
1
TOX
80.3 TX
85
TOX 89.5 TX 96
NOT 100.0 NT 92
TOX 0.0 TX ND
TOX 1.4 TX 96
TOX 1.4 TX 68
TOX 0.0 TX ND
. o=ny/y
MATURE TOXM
TX
NT
NT
ND
NT
NT
ND
10
10
96
ND
0.
0.
ND
NT
NT
NT
ND
NT
NT
ND
-------
Appendix 5 Other published toxicity data grouped by chemical, test type, sample type, toxiciry
response, and sediment concentrations normalized to dry weight (in ascending order).
Study Codes: (1) MCGEE: McGee et al. (1994) and Schlekat et al. (1994); (2) DAY:
Day et al. (1995); (3) HOKE: Hoke et al. (1995); (3) JFLD: Field and Cairncross
(1994); and (4) SUPRF: M.D. Sprenger, USEPA, Edison, NJ (unpublished data).
Tests: (1) HA10 to HA28: Hyalella azteca 10- to 28-d test; (2) CR14: Chironomus
riparius 14-d test; (3) TT28: Tubifex tubifex 28-d test; and (4) HS28: Hexagenia spp.
28-d test. See Appendix 2c for a description of the chemical name for each
abbreviated CHEMCODE. The first four pages of this appendix are included on the
following pages of the report. The computer disk that accompanies the report contains
the electronic version of this entire appendix (file name: "apdxS.wp").
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4
CONC
0.51
0.71
0.73
0.91
1.20
1.20
1.24
1.24
1.24
1.24
1.24
1.44
1.48
1.66
1.72
1.72
1.72
1.72
1.77
1.77
1.77
1.77
1.85
1.85
1.85
1.85
1.87
1.87
1.87
1.87
1.94
2.04
2.06
2.06
2.06
2.06
2.06
2.08
2.08
2.08
2.08
2.08
2.08
2.08
2.08
EFFECT
NE
NE
NC
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
Nu
RATIO STUDY
SUPRF
JFLD
0 . 3 JFLD
0 . 3 JFLD
JFLD
0 . 2 SUPRF
DAY
DAY
MCGEE
DAY
DAY
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 7 DAY
MLUUE=1U.
TEST
HA10
CT10
CT14
CT14
CT14
HA10
CR14
HA28
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
L CHEMCOUE=TO(J UNI
SAMPLE
MAO 5
1111
1111
1111
1111
OE04
CM17
CM17
BR7
CM17
CM17
BR5
BR3
BR6
SL04
SL04
SL04
SL04
CW01
CW01
CW01
CW01
CW05
CMOS
CW05
CW05
CM15
CM15
CM15
CM15
BR2
BR1
CW21
CW21
BR4
CW21
CW21
CW06
CW12
CW06
CW12
CW06
CW12
CW12
CW06
-02-RS15-01
-02-RS07-01
-02-AS07-01
-02-AS12-01
WTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
SURV
88
85
60
40
92
18
80
94
81
94
40
95
90
91
73
90
96
21
88
89
98
22
86
90
100
26
86
88
94
43
80
90
84
89
85
98
45
82
89
94
94
94
80
45
24
.30
.00
.00
.00
.50
.00
.00
.70
.30
.00
.00
.00
.00
.30
.30
.00
.70
.00
.00
.30
.00
.00
.70
.70
.00
.00
.70
.00
.00
.00
.00
.00
.00
.30
.00
.00
.00
.70
.30
.70
.70
.00
.00
.00
.00
TOXS
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
GROW
0
4
3
2
4
4
0
0
3
2
73
4
3
3
0
0
4
109
0
0
6
22
0
0
6
29
0
0
3
102
4
4
0
0
3
9
117
0
0
0
0
5
10
172
22
.18
.59
.76
.73
.17
.73
.46
.49
.82
.03
.00
.09
.99
.88
.50
.59
.41
.00
.38
.72
.87
.00
.33
.42
.17
.00
.50
.54
.30
.00
.12
.12
.58
.74
.96
.97
.00
.36
.52
.53
.70
.35
.12
.00
.00
TOXG
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
-------
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
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
.20
.22
.22
.22
.22
.34
.34
.34
.34
.34
.36
.40
.44
.44
.44
.44
.45
.45
.45
.45
.52
.52
.52
.52
.53
.59
.59
.59
.59
.63
.63
.63
.63
.65
.65
.65
.65
.68
.69
.69
.69
.69
.72
.72
.72
.72
.80
.90
.90
.90
.90
.90
NE
ME
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NC
NE
SG
NE
NE
SG
0.8
0.8
.
0.9
.
0.9
0.5
1.1
1.0
JFLD
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
MCGEE
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
JFLD
SUPRF
DAY
DAY
CT14
CR14
HA28
HS28
TT28
CR14
HA10
HA28
HS28
TT28
HA28
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
CT14
HA10
HA28
HS28
1111-02-RS14-01
CW22
CW22
CW22
CW22
CW24
CS04
CW24
CW24
CW24
CON2
1111-02-RS13-01
CW23
CW23
CW23
CW23
CW14
CW14
CW14
CW14
CW15
CW15
CW15
CW15
BR9
CW13
CW13
CW13
CW13
CW18
CW18
CW18
CW18
CW09
CW09
CW09
CW09
BR8
SL07
SL07
SL07
SL07
CMOS
CMOS
CMOS
CMOS
OE21
VS01
1111-02-AS09-01
MAO 6
VS01
VS01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
77.50
88.00
77.30
98.00
43.00
76.00
93.30
90.70
98.00
42.00
88.70
72.50
96.00
90.70
100.00
39.00
86.70
84.00
100.00
46.00
85.30
82.70
100.00
43.00
90.00
76.00
88.00
100.00
44.00
86.70
93.30
98.00
47.00
85.30
84.00
100.00
29.00
93.80
71.10
82.70
98.00
15.00
84.00
86.70
100.00
31.00
0.00
84.00
42.50
81.70
88.00
94.00
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
4.34
0.55
0.71
9.11
74.00
0.51
0.50
0.66
8.53
62.00
3.70
3.20
0.35
0.71
7.98
43.00
0.61
0.74
10.59
135.00
0.49
0.76
10.94
126.00
3.94
0.51
0.66
10.93
126.00
0.66
0.82
11.15
147.00
0.40
0.50
4.56
56.00
3.88
0.41
0.95
5.98
152.00
0.36
0.50
5.16
37.00
0.43
3.03
0.16
0.61
0.19
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NR
NT
TX
NT
NT
TX
-------
2
2
2
2
2
2
2
2
2
2
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
3
4
4
.90
.93
.93
.93
.93
.93
.93
.93
.93
.95
.05
.06
.06
.06
.20
.20
.25
.28
.28
.28
.28
.33
.33
.33
.33
.40
.40
.40
.40
.40
.40
.40
.48
.48
.48
.48
.50
.50
.50
.50
.50
.55
.63
.63
.63
.63
.81
.81
.81
.81
.30
.40
NB
NE
NE
NE
NB
NE
SG
NE
NC
NE
SG
NE
NE
NE
SG
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
**
NE
NE
NE
NE
NE
NE
NB
NE
SG
NE
NC
NE
NE
SG
SG
NE
NE
SG
NE
SG
SG
NE
SG
NE
NE
1
1
1
1
1
1
4
1
0
1
1
1
1
1
1
.0
.0
.1
.
.2
.
.2
.2
.8
.1
.6
.2
.3
.3
.3
.3
.3
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
JFLD
JFLD
DAY
DAY
DAY
JFLD
SOPRF
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
JFLD
SUPRF
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
JFLD
DAY
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CT14
CT14
CR14
HA28
HS28
CT14
HA10
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
CT10
HA10
HA10
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA10
HA28
HS28
TT28
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CT14
CR14
VS01
CW17
VS03
CW17
VS03
CW17
VS03
CW17
VS03
1111-02-RS11-01
1111-02-RS12-01
CW16
CW16
CW16
1111-02-AS08-01
MA09
1111-02-AS06-01
CM09
CM09
CM09
CM09
CM11
CM11
CM11
CM11
CM22
1111-02-AS03-01
MAO 7
MA13
CM22
CM22
CM22
CW03
CW03
CW03
CW03
SL02
OE10
SL02
SL02
SL02
1111-02-RS01-01
CM07
CM07
CM07
CM07
SL06
SL06
SL06
SL06
1111-02-AS05-01
VS07
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT'
BT
BT
BT
BT
BT
BT
BT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
26
89
89
86
97
94
90
43
21
90
52
90
89
100
17
78
82
75
93
90
44
72
96
100
45
82
82
88
71
93
100
37
80
90
100
22
77
16
89
98
16
60
82
85
89
31
76
78
98
19
75
78
.00
.30
.30
.70
.30
.00
.00
.00
.00
.00
.50
.70
.30
.00
.50
.30
.50
.30
.30
.00
.00
.00
.00
.00
.00
.70
.50
.30
.70
.30
.00
.00
.00
.00
.00
.00
.80
.00
.30
.00
.00
.00
.70
.60
.00
.00
.00
.70
.00
.00
.00
.70
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
30
0
0
0
0
10
0
154
22
4
1
0
0
10
0
0
4
0
0
3
113
0
0
4
91
0
3
0
0
0
4
150
0
0
5
15
0
3
0
3
147
4
0
0
4
123
0
0
4
131
5
0
.00
.64
.33
.87
.42
.40
.01
.00
.00
.64
.32
.65
.79
.58
.72
.17
.07
.46
.67
.39
.00
.39
.53
.15
.00
.42
.78
.23
.18
.87
.61
.00
.43
.66
.78
.00
.39
.16
.69
.15
.00
.44
.47
.74
.58
.00
.18
.58
.24
.00
.06
.29
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NR
-------
4.40
4.40
4.40
4.45
4.45
4.45
4.45
4.50
4.79
4.79
4.79
4.79
5.00
5.50
7.00
7.10
7.10
7.30
7.30
7.30
7.30
7.70
8.90
9.10
9.40
9.50
10.00
12.00
14.00
SG
SG
SG
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
SG
SG
SG
NE
NE
NE
NE
NE
SG
NE
SG
NE
NE
*
NE
1.5
1.6
1.5
0.8
0.9
1.2
1.2
1.2
1.5
1.6
2.0
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
DAY
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
DAY
DAY
DAY
DAY
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
VS07
VS07
VS07
CMOS
CM08
CMOS
CMOS
OE02
CM01
CM01
CM01
CM01
OE27
MA04
MA01
MA03
OE23
CM06
CM06
CM06
CM06
OE16
OE24
MAO 8
OE12
MA11
MA10
OE25
OE14
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
0.00
4.00
24.00
85.30
93.30
100.00
37.00
3.00
84.00
89.30
96.00
34.00
90.00
76.70
0.00
10.00
0.00
78.90
97.30
100.00
45.00
98.00
13.00
86.70
10.00
90.00
78.30
0.00
96.00
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
0.00
-0.08
7.00
0.42
0.67
5.42
102.00
3.20
0.31
0.56
5.07
102.00
3.87
0.16
0.40
0.63
6.54
96.00
4.27
3.63
0.14
3.43
0.16
0.14
4.98
NR
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NR
NR
NR
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NR
NT
-------
Appendix 6 Other published sediment effect concentrations (SECs; dry-weight concentrations)
used to evaluate the comparability of our calculated SECs. See Appendix 2c for a
description of the chemical name for each abbreviated CHEMCODE (ND = not
determined).
CODES UNITS*
ERL ng/g
ERM ng/g
TELm ng/g
PELm ng/g
AET1 ng/g
AET2 ng/g
AET3 ng/g
AET4 ng/g
SLC1 ng/g
SLC2 ng/g
EQP ng/g
TELf ng/g
PELf ng/g
AET5 ng/g
AET6 ng/g
*metals: ug/g
*iron: percent
ND = not determined
SOURCE
Long etai. (1995)
Long etal. (1995)
MacDonald et al. (1995) marine
MacDonald et al. (1995) marine
Barrick et al. (1988) amphipod marine
Barrick et al. (1988) oysters marine
Barrick et al. (1988) microtox marine
Barrick et al. (1988) benthos marine
Persaud et al. (1992) lowest effect level
Persaud et al. (1992) severe effect level (assumed 2%
total organic carbon; TOC)
USEPA (1988) and more recent (assume 2% TOC)
Smith et al. (1996) freshwater
Smith et al. (1996) freshwater
Batts and Cubbage (1995) Hyalella freshwater (assumed
2% TOC for PAHs and PCBs)
Batts and Cubbage (1995) Microtox freshwater
(assumed 2% TOC for PAHs and PCBs)
-------
GHEMCODE
PCB1016
PCB1221
PCB1232
PCB1242
PCB1248
PCB1254
PCB1260
PCB-T
DIMP
DIMBP
2FUOROBIP
NBNZ
BUTBNZPHT
2NOCTP
B2ETHXPHTH
ALDRIN
6CL-CHX-A
6CL-CHX-B
6CL-CHX-D
6CL-CHX-G
CHLORDAN-G
CHLORDAN-A
ODD
DDE
DDT
DIELDRIN ND
ENDOSLFN-A
ENDOSLFN-B
ENDOSLFN-S
ENDRIN
ENDRIN-ALD
HEPTACHLOR
HEPCLEPOX
TOXAPHENE
METHOXYCL
ERL
ND
ND
ND
ND
ND
ND
ND
22.7
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.2
1.58
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ERM
ND
ND
ND
ND
ND
ND
ND
180
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
27
46.1
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TELm
ND
ND
ND
ND
ND
ND
ND
21.6
ND
ND
ND
ND
ND
ND
182
ND
ND
ND
ND
ND
ND
ND
1.22
2.07
3.89
0.72
ND
ND
ND
ND
ND
ND
ND
ND
ND
PELm
ND
ND
ND
ND
ND
ND
ND
189
ND
ND
ND
ND
ND
ND
2647
ND
ND
ND
ND
ND
ND
ND
7.81
374
51.7
4.3
ND
ND
ND
ND
ND
ND
ND
ND
ND
AET1
ND
ND
ND
ND
ND
ND
ND
3100
1400
1400
ND
ND
900
2100
3100
ND
ND
ND
ND
ND
ND
ND
43
15
270
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AET2
ND
ND
ND
ND
ND
ND
ND
1100
160
1400
ND
ND
470
420
1900
ND
ND
ND
ND
ND
ND
ND
ND
ND
6
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AET3
ND
ND
ND
ND
ND
ND
ND
1000
1400
5100
ND
ND
900
6200
1300
ND
ND
ND
ND
ND
ND
ND
16
9
34
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AET4
ND
ND
ND
ND
ND
ND
ND
130
71
1400
ND
ND
63
ND
1900
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
SLC1
7
ND
ND
ND
30
60
5
70
ND
ND
ND
ND
ND
ND
ND
2
6
5
3
3
7
7
8
5
7
2
ND
ND
ND
3
ND
ND
5
ND
ND
SLC2
1060
ND
ND
ND
3000
680
480
EQP
ND
ND
ND
ND
ND
ND
ND
10600840
ND
ND
ND
ND
ND
ND
ND
160
200
420
240
20
120
120
120
380
240
1820
ND
ND
ND
2600
ND
ND
100
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TELf
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.5
ND
3.54
1.42
7
2.85
ND
ND
ND
2.67
ND
ND
0.6
ND
ND
PELf
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
8.9
ND
8.51
6.75
4450
6.67
ND
ND
ND
62.4
ND
ND
2.74
ND
ND
AET5
ND
ND
ND
ND
ND
360
ND
740
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
AET6
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CHEMCODE
SILVER
ARSENIC
CADMIUM
CHROMIUM-T
COPPER
IRON
MERCURY
MANGANESE
NICKEL
LEAD
SELENIUM
ZINC
14-2CLBNZ
12-2CLBNZ
13-2CLBNZ
NAPHTHALENE
2-METHNAP
ACENA
DIBNZFURAN
FLUORENE
PHENANTHRN
ANTHRACENE
FLUORANTHN
PYRENE
BAA
CHRYSENE
BBF
BKF
BAP
ICDP
BGHIP
BBKF
ACENAPTYLE
DBA
PAH-L
PAH-H
PAH-T
ERL
1.0
8.2
1.2
81
34
ND
0.15
ND
20.9
46.7
ND
150
ND
ND
ND
160
70
16
ND
19
240
85.3
600
665
261
384
ND
ND
430
ND
ND
ND
44
63.4
552
1700
4022
ERM
3.7
70
9.6
370
270
ND
0.71
ND
51.6
218
ND
410
ND
ND
ND
2100
670
500
ND
540
1500
1100
5100
2600
1600
2800
ND
ND
1600
ND
ND
ND
640
260
3160
9600
44792
TELm
0.73
7.24
0.68
52.3
18.7
ND
0.13
ND
15.9
30.2
ND
124
ND
ND
ND
34.6
20.2
6.71
ND
21.2
86.7
46.9
113
153
74.8
108
ND
ND
88.8
ND
ND
ND
5.87
6.22
312
655
1684
PELm
1.77
41.6
4.21
160
108
ND
0.7
ND
42.8
112
ND
271
ND
ND
ND
391
201
88.9
ND
144
544
245
1494
1398
693
846
ND
ND
763
ND
ND
ND
128
135
1442
6675
16770
AET1
6.1
93
6.7
270
1300
ND
2.1
ND
140
660
ND
960
120
110
170
2400
1900
2000
ND
3600
6900
13000
30000
16000
5100
9200
7800
7800
3000
1800
1400
ND
1300
540
24000
69000
ND
AET2
0.56
700
9.6
ND
390
ND
0.59
ND
ND
660
ND
1600
120
50
170
2100
670
500
ND
540
1500
960
2500
3300
1600
2800
3600
3600
1600
690
720
ND
560
230
5200
17000
ND
AET3
6.1
57
5.1
260
530
ND
2.1
ND
140
450
ND
410
110
50
170
2700
1400
730
ND
1000
5400
4400
24000
16000
5100
9200
9900
9900
3600
2600
2600
ND
1300
970
13000
69000
ND
AET4
0.56
700
9.6
ND
390
ND
0.41
ND
ND
530
ND
1600
110
35
170
2100
670
500
ND
540
1500
960
1700
2600
1300
1400
3200
3200
1600
600
670
ND
560
230
5200
12000
ND
SLC1
ND
6
0.6
26
16
2
0.2
460
16
31
ND
120
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2000
SLC2
ND
33
10
110
110
4
2
1100
75
250
ND
820
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
220000
EQP
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2400
ND
20400
26000
26000
ND
ND
ND
22000
ND
ND
ND
2800
ND
ND
ND
ND
TELf
ND
5.9
0.596
37.3
35.7
ND
0.147
ND
18
35
ND
123
ND
ND
ND
ND
ND
ND
ND
ND
41.9
ND
111
53
31.7
57.1
ND
ND
31.9
ND
ND
ND
ND
ND
ND
ND
34.1
PELf
ND
17
3.53
90
197
ND
0.486
ND
36
91.3
ND
315
ND
ND
ND
ND
ND
ND
ND
ND
515
ND
2355
875
385
862
ND
ND
782
ND
ND
ND
ND
ND
ND
ND
277
AET5 AET6
4.5 ND
150 40
12 7
280 ND
840 ND
ND ND
2.7 0.56
1800 ND
ND 31
720 260
ND ND
1100 490
ND ND
ND ND
ND ND
46000 6600
ND ND
68000 580
10200 ND
84000 600
182000 2200
34000 520
96000 3000
62000 3200
13000 1100
34000 1580
30000 2200
30000 2200
18200 1580
7600 660
18200 600
ND ND
1660 320
3200 200
420000 11000
220000 13000
640000 24000
-------
Appendix 4a Data grouped by chemical, test type, sample type, toxicity response, and sediment
concentrations normalized to dry weight (in ascending order). A value bracketed by
"—" indicate published SECs (see Appendix 5). See Appendix 2c for a description of
the chemical name for each abbreviated CHEMCODE. See Appendix 3a for
additional descriptions of the headings for the columns. If SECs for a particular
chemical are not reported (NR) for a test type and sample type in both Appendix 3 a
and Appendix 3b, then an ascending data table is not included in Appendix 4a for
those SECs. If SECs for a particular chemical are not reported for a test type and
sample type in Appendix 3a or in Appendix 3b, then these particular SECs for this
particular test type and sample type are not reported in the ascending data table.
Examples are included for copper and benzo[a]pyrene. The computer disk that
accompanies the report contains the electronic version of this entire appendix (file
name: "apdx4a.wp").
CONC Concentration.
EFFECT
NE Non-toxic sample.
NC No concordance (concentration of the chemical in a toxic sample was less than
the mean concentration of the chemical in the non-toxic samples at a site;
designated as no effect in the calculations of SECs).
SG Small gradient (concentration of the chemical in a toxic sample 1 to <2 times
the mean concentration of the chemical in the non-toxic samples at a site).
* Concentration of the chemical in a toxic sample 2 to <4 times the mean
concentration of the chemical in the non-toxic samples at a site.
** Concentration of the chemical in a toxic sample >4 the mean concentration of
the chemical in the non-toxic samples at a site.
RATIO Concentration of the chemical in the sample divided by the mean concentration
of the chemical in the non-toxic samples at a site.
SITE 1: Indiana Harbor, 2: Buffalo River, 3: Saginaw River (1st survey). 4: Saginaw
River (3rd survey), 5: Waukegan Harbor, 6: Upper Mississippi River, 7:
Milltown Reservoir of the Clark Fork River, 8: Clark Fork River, 9: Trinity
River, 10: Mobile Bay, 11: Tabbs Bay in Galveston Bay.
SAMPLE Sample identification code. CO: control, RE: reference.
CEN Censor. An @ indicates unreliable SEC (e.g., less than five of the samples
were designated as toxic for the chemical or the frequency of toxic samples
below the SEC was greater than the frequency of toxic samples above the
SEC).
TOXICALL Survival, growth, or maturation significantly less than the control response
(p<0.05).
SURV Percentage survival normalized to the control response.
NT Response not significantly less than the control response (p>0.05).
TX Response significantly less than the control response (p<0.05).
GROW Percentage growth normalized to the control response.
MATURE Percentage maturation normalized to the control response (Hyalella azteca
only).
ND Not determined.
MINTOX Minimum concentration in a toxic sample.
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=101 CHEM=Total Organic Carbon TEST=CR14 SAMPTYP=bottom sediment - total UNITS=%
CONC EFFECT RATIO SITE SAMPLE C
4 SR-3-06
7 MR-1-02
5 WH-l-CO
4 SR-3-CO
4 SR-3-01
3 SR-l-CO
3 SR-1-10
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
7 MR-l-CO
8 CF-1-05
8 CF-l-CO
4 SR-3-02
7 MR-1-19
4 SR-3-05
8 CF-1-03
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
8 CF-1-02
0.4 2 BR-1-08
0.4 2 BR-1-07
7 MR-1-17
0.5 2 BR-1-03
TEL-SR(ERL*NERM)
1.3 3 SR-1-06
2 BR-1-09
GL-TEL-SR(ERL*NERM)
7 MR-1-07
1.6 7 MR-1-11
ERL-15% EFFECT
4 SR-3-16
3 SR-1-03
8 CF-1-04
7 MR-1-25
5 WH-l-RE
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
4 SR-3-08
1.7 5 WH-1-01
GL-ERL-15% EFFECT
4 SR-3-24
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
5.6 1 IH-1-04
ERM-50% EFFECT
2.6 5 WH-1-02
GL-ERM-50% EFFECT
8 CF-1-06
8 CF-1-01
7.7 1 IH-1-03
8.8 1 IH-1-07
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
11.6 ** 11.6 1 IH-1-06
0.2
0.8
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.1
1.2
1.2
1.3
1.3
1.4
1.4
1.6
1.6
1.7
1.7
1.7
1.9
2.0
2.0
2.1
2.2
2.4
2.4
2.7
2.7
2.9
3 .0
3 .1
3.2
3.4
3.4
3.5
3.6
3.7
3.7
4.0
4.4
4.5
5.6
5.7
5.7
5.7
6.7
6.9
7.7
8.8
8.9
8.9
8.9
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NC
SG
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
* *
*
NE
NE
**
**
NE
JULLUJU seuxine
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
103
113
100
100
96
100
90
117
100
100
100
96
100
100
111
104
84
79
38
47
122
62
18
105
116
70
102
104
109
138
85
95
8
.3
.4
.0
.0
.7
.0
.3
.9
.0
.0
.0
.3
.0
.6
.9
.9
.0
.0
.0
.9
.4
.8
.7
.0
.4
.2
.7
.5
.9
.8
.7
.1
.6
iiu -
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
UULCU
GROW
11
11
ND
10
10
10
10
11
10
10
10
11
10
12
10
11
10
11
97
10
12
87
52
10
11
75
12
10
11
11
ND
11
ND
. urj j. A
TOXG
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
NT
ND
NT
ND
O — "6
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
102.2 NT 11
NT
TOX 2.0 TX ND ND
TOX 51.4 TX ND ND
NOT
NOT
TOX
TOX
NOT
TOX
107.4 NT
95.1 NT
2.7 TX
0.0 TX
67.8 NT
11
13
ND
ND
10
0.0 TX ND
NT
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND ND
ND ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=101 CHEM=Total Organic Carbon TEST=HA14 SAMPTYP=bottom sediment - total UNITS=%
CONC EFFECT RATIO SITE SAMPLE I
SR-3-06
TR-1-03
TR-1-Q2
TR-1-04
TR-1-01
WH-l-CO
TR-l-CO
SR-3-CO
SR-3-01
SR-l-CO
SR-1-10
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
SR-3-02
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
SR-3-05
BR-1-08
BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-03
SR-1-06
BR-1-09
SR-3-16
SR-1-03
NERH-85% NO EFFECT
WH-l-RE
GL-NERH-85% NO EFFECT
SR-3-08
WH-1-01
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-04
WH-1-02
IH-1-03
IH-1-07
BR-1-01
IH-1-06
0.2
0.3
0.3
0.4
0.5
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.3
1.3
1.3
1.4
1.7
1.7
1.7
1.7
2.0
2.1
2.2
2.9
3.0
3.2
3.4
3.4
3.6
3.7
3.9
4.0
4.0
4.0
4.0
4.7
4.7
5.6
5.7
7.7
8.8
8.9
11.6
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
SG
*
SG
*
NE
NE
NE
NE
SG
NE
* *
*
**
**
* *
**
4
9
9
9
9
5
9
4
4
3
3
1
2
'
4
.
0.7 4
1.7 2
1.7 2
.
2.0 2
1.3 3
2.2 2
4
3
5
.
4
1.7 5
4
,
.
5.6 1
2.6 5
7.7 1
8.8 1
8.9 2
11.6 1
•"w> l~ L, <->il
POXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
n iaGuxiiic
SURV
111.8
87.5
100.0
93.4
100. 0
100.0
100.0
100.0
116.2
100.0
101.6
100.0
100.0
105.9
104.5
113.7
86.4
77.3
12.5
83.4
111.8
115.6
100.0
110.4
35.0
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
I_U l_d.
GROW
94
ND
ND
ND
ND
10
ND
10
10
10
10
10
10
10
94
85
85
85
87
90
10
95
14
10
13
L U1N .L 1
TOXG
NT
ND
ND
ND
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
MATURE
74
ND
ND
ND
ND
ND
ND
10
12
10
33
10
10
51
22
22
0.
68
0.
0.
16
23
ND
61
ND
: TOXM
NT
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
NT
NT
ND
NT
ND
NOT 113.3 NT 10 NT
14
NT
TOX
TOX
TOX
TOX
TOX
TOX
0.0
40.0
1.4
0.0
100.0
1.4
TX
TX
TX
TX
NT
TX
ND
11
96
ND
85
68
ND
NT
NT
ND
TX
NT
ND
ND
0.
ND
0.
0.
ND
ND
NT
ND
TX
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=101 CHEM=Total Organic Carbon TEST=HA28 SAMPTYP=bottom sediment - 'otal UNITS=
CONC EFFECT RATIO SITE SAMPLE C
0.2
0.2
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.1
1.1
1.1
1.1
1.2
1.2
1.3
1.3
1.3
1.4
1.4
1.4
1.4
1.5
1.7
1.7
1.7
1.7
1.8
1.9
2.0
2.0
2.0
2.1
2.2
2.2
2.4
2.7
2.9
3.0
3.0
3.0
3.1
3.2
3.3
3.4
3.4
3.6
3.6
3.7
4.0
4.0
4.0
4.3
4.7
5.6
5.7
6.0
6.7
6.9
7.7
8.0
8.8
8.9
9.0
9.0
11.6
NC 0.3 11 TB-1-01
NE . 4 SR-3-06
NE . 9 TR-1-03
NE . 9 TR-1-02
NE . 9 TR-1-04
NE . 9 TR-1-01
NE . 11 TB-l-RE
NC 0.4 7 MR-1-02
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 9 TR-l-CO
NE . 4 SR-3-CO
NE . 4 SR-3-01
NE . 3 SR-l-CO
NG 1.0 3 SR-1-10
NC 0.5 7 MR-1-01
NE . 1 IH-l-CO
NE . 2 BR-l-CO
. . GL-NERM-50% NO EFFECT
NE . 7 MR-l-CO
NE . 11 TB-1-04
SG 1.4 11 TB-1-03
SG 1.4 11 TB-1-02
NE . 8 CF-1-05
NE . 8 CF-l-CO
NE . 4 SR-3-02
NC 0.6 7 MR-1-19
. . NERM-50% NO EFFECT
NE . 6 UM-l-RE
NE . 4 SR-3-05
NC 0.5 8 CF-1-03
. . GL-TEL-SR (ERL*NERM)
. . TEL-SR(ERL*NERM)
NE . 8 CF-1-02
NE . 2 BR-1-08
SG 1.3 2 BR-1-07
. . ERL-15% EFFECT
NE . 6 UM-1-02
NC 0.9 7 MR-1-17
NE . 10 MB-1-04
SG 1.5 2 BR-1-03
. . GL-ERL-15% EFFECT
* 2.1 3 SR-1-06
NE . 6 UM-1-03
SG 1.6 2 BR-1-09
SG 1.1 7 MR-1-07
SG 1.3 7 MR-1-11
NE . 4 SR-3-16
* 3.0 3 SR-1-03
NE . 10 MB-1-03
. . ERM-50% EFFECT
NE . 8 CF-1-04
NE . 7 MR-1-25
. PEL-SR(ERM*NERH)
NE . 5 WH-l-RE
. GL-NERH-85% NO EFFECT
NE . 4 SR-3-08
. . NERH-85% NO EFFECT
SG 1.7 5 WH-1-01
. . GL-PEL-SR(ERM*NERH)
NE . 4 SR-3-24
. GL-NEC-MAX NO EFFECT
NE . 6 UM-1-01
. . GL-ERM-50% EFFECT
** 5.6 1 IH-1-04
* 2.6 5 WH-1-02
NE . 10 MB-1-02
NE . 8 CF-1-06
* 2.5 8 CF-1-01
** 7.7 1 IH-1-03
NE . 10 MB-l-RE
** 8.8 1 IH-1-07
** 6.6 2 BR-1-01
NE . 10 MB-1-01
. NEC-MAX NO EFFECT
** 11.6 1 IH-1-06
JU U L.U1I
•oxic
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
.1 St£UJ.lU*:
SURV
0.0
100.0
98.6
100.0
82.9
81.4
100.0
109.3
100.0
100.0
100.0
100.0
97.4
100.0
100.0
108.1
100.0
100.0
100.0
93.2
52.3
11.4
114.9
100.0
103.8
114.0
86.5
96.1
123.0
102.7
97.4
80.3
117.9
115.1
95.5
79.0
10^3
114.9
88.2
91.9
90.7
96.1
96.2
95.5
128.4
109.3
109.5
88.3
71.7
102.6
119.3
0.0
36.5
97.0
120.3
64.9
1.4
100.0
0.0
89.5
75.8
suu -
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
TX
NT
TX
TX
NT
uuaj
-jROW
ND
92
ND
ND
ND
ND
10
92
10
ND
ND
10
94
10
97
79
10
10
10
10
97
72
98
10
10
89
ND
94
82
94
10
85
ND
92
ND
85
60
ND
92
91
58
10
91
ND
10
95
11
92
91
10
ND
ND
74
ND
10
73
96
ND
ND
96
ND
L UiN X j
TOXG
ND
NT
ND
ND
ND
ND
NT
TX
NT
ND
ND
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
ND
NT
TX
NT
NT
TX
ND
TX
ND
TX
TX
ND
NT
TX
TX
NT
TX
ND
NT
NT
NT
NT
NT
NT
ND
ND
TX
ND
NT
TX
NT
ND
ND
NT
ND
LO = "B
MATURE
ND
96
ND
ND
ND
ND
ND
95
ND
ND
ND
10
11
10
10
68
10
10
10
ND
ND
ND
77
10
10
63
ND
11
93
48
10
10
ND
65
ND
10
37
ND
10
31
24
95
10
ND
80
12
ND
95
ND
10
ND
ND
ND
ND
90
25
0.
ND
ND
10
ND
TOXM
ND
NT
ND
ND
ND
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
NT
ND
NT
TX
ND
NT
TX
TX
NT
NT
ND
NT
NT
ND
NT
ND
NT
ND
ND
ND
ND
NT
TX
NT
ND
ND
NT
ND
TOX
1.4 TX 68 NT
0.
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 4
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=102 CHEM=Acid Volatile Sulfides TEST=CR14 SAMPTYP=bottom sediment - total UNITS=um/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.0
0.0
0.0
0.0
0.0
0.0
0.3
0.6
1.2
1.5
1.5
2.5
2.6
3.2
3.3
3.3
3.7
4.4
5.1
5.2
5.7
5.8
5.8
6.0
6.0
6.7
7.2
7.8
8.3
8.9
9.8
12.6
13.0
13.0
14.2
15.5
15.5
15.5
15.6
15.7
19.1
20.9
23.3
33.5
33.5
33.5
52.6
71.4
161.0
161.0
161.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
* *
NE
* *
NE
NE
* *
* *
* *
NE
.
.
.
.
.
0.3
0.0
.
.
0.1
0.1
.
,
.
.
.
6.2
,
,
2616.7
.
5583.3
.
8766.7
11900
4
3
7
1
8
2
8
7
4
3
7
7
2
4
4
4
2
8
2
4
2
3
8
8
4
7
7
8
.
.
3
.
7
1
8
7
1
.
1
1
2
SR-3-CO
SR-l-CO
MR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
CF-1-01
MR-1-01
SR-3-06
SR-1-10
MR-1-19
MR-1-11
BR-1-08
SR-3-16
SR-3-02
GL-NERM-50% NO EFFECT
SR-3-05
NERM-50% NO EFFECT
BR-1-09
CF-1-03
BR-1-07
SR-3-08
BR-1-03
SR-1-03
GL-NERH-85% NO EFFECT
CF-1-06
GL-TEL-SR (ERL*NERM)
CF-1-05
TEL-SR (ERL*NERM)
SR-3-24
MR-1-07
MR-1-25
CF-1-04
NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
MR-1-02
IH-1-04
CF-1-02
PEL-SR (ERM*NERH)
MR-1-17
IH-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-06
IH-1-07
BR-1-01
NEC -MAX NO EFFECT @
GL-NEC-MAX NO EFFECT @
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
100
100
100
100
100
100
95
117
103
90
111
70
38
102
100
104
105
84
47
95
62
104
107
96
102
116
138
109
18
113
2
79
122
2
0
0
67
.0
.0
.0
.0
.0
.0
.1
.9
.3
.3
.9
.2
.0
.7
.6
.
.9
.0
.0
.9
.1
.8
.5
f
.4
.3
.2
.4
.8
.9
.7
.4
.0
.0
.4
.7
.
.0
.0
.8
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
NT
10
10
10
10
10
10
13
11
11
10
10
75
97
12
12
11
10
10
10
11
87
10
11
11
11
11
11
11
52
11
ND
11
12
ND
ND
ND
10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=102 CHEM=Acid Volatile Sulfides TEST=HA14 SAMPTYP=]
CONC EFFECT RATIO SITE SAMPLE CEN '
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-3-06
SR-1-10
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
BR-1-08
SR-3-16
SR-3-02
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
SR-3-05
BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-07
SR-3-08
BR-1-03
SR-1-03
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
SR-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-04
IH-1-03
IH-1-06
IH-1-07
BR-1-01
0
0
0
0
1
1
2
2
2
3
3
3
3
3
5
5
5
5
5
5
6
6
6
8
8
8
9
9
15
15
15
15
33
52
71
161
.0
.0
.0
.0
.2
.5
.4
.4
.6
.2
.3
.5
.5
.7
.1
.1
.1
.7
.8
.8
.0
.0
.0
.9
.9
.9
.7
.7
.5
.6
.6
.7
.5
.6
.4
.0
NE
NE
NE
NE
NE
NE
**
NE
NE
NC
**
* *
NE
**
NE
NE
**
**
#*
*•*
**
**
433
1
850
950
966
6
2616
5583
8766
.
.
.
.
.
.
.
.
.3
.
.
.0
.0
.0
.
.7
.
.2
.
.
.7
.3
.7
11900
26833
4
3
1
2
4
3
.
.
2
4
4
.
4
2
2
4
2
3
4
3
1
1
1
1
2
HJtuuia seu.j.iue
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
100
100
100
100
111
101
113
111
105
104
83
86
110
77
115
.0
.0
.0
.0
.8
.6
.7
.8
.9
.5
.4
.4
.4
.3
.6
JIL -
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
CUL.CL.
GROW
10
10
10
10
94
10
85
10
10
94
90
85
10
85
95
L U1MJ.1O-UIU/ y
TOXG MATURE TOXM
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
10
10
10
10
74
33
22
16
51
22
0.
0.
61
68
23
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
TX
NT
NT
NT
NOT
TOX
113.3 NT 10 NT
12.5 TX
87
NT
TOX 0.0 TX ND ND
TOX 1.4 TX 96 NT
TOX 1.4 TX 68 NT
TOX 0.0 TX ND ND
TOX 100.0 NT 85 TX
14
0.
ND
0.
0.
ND
0.
NT
NT
ND
NT
NT
ND
TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=102 CHEM=Acid Volatile Sulfides TEST=HA28 SAMPTYP=bottom sediment - total UNITS=um/g
CONC EFFECT RATIO SITE SAMPLE C
0.0
0.0
0.0
0.0
0.0
0.0
0.3
0.6
1.2
1.5
1.5
2.5
2.6
2.6
3.2
3.2
3.2
3.3
3.6
3.7
4
5
5
S
5
5
5
5.8
5.8
6.0
6.7
7.8
8.9
8.9
9
9
12
12
13
14.0
14.2
15.5
15.5
15.6
15.6
15.7
19.1
19.2
19.2
23.3
33.5
48.7
52.6
61.7
71.4
161.0
NE
NE
NE
NE
NE
NE
NC
NC
NE
**
NC
NC
NE
NE
NE
NE
NE
NC
* *
NE
NE
NE
NE
SG
NE
NE
SG
**
0.0
0.1
250.0
0.2
0.4
1.
2583.
* 2.5
** 2616.7
NE
NE
* 3.7
** 5583.3
** 4.3
** 8766.7
** 5.5
** 11900
** 123.6
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
8 CF-1-01
7 MR-1-01
4 SR-3-06
3 SR-1-10
7 MR-1-19
7 MR-1-11
2 BR-1-08
GL-NERM-50% NO EFFECT
11 TB-l-RE
4 SR-3-16
NERM-50% NO EFFECT
4 SR-3-02
GL-TEL-SR(ERL*NERM)
4 SR-3-05
TEL-SR(ERL*NERM)
3.9 2 BR-1-09
GL-ERL-15% EFFECT
0.6 8 CF-1-03
4.4 2 BR-1-07
ERL-15% EFFECT
4 SR-3-08
2 BR-1-03
GL-NERH-85% NO EFFECT
3 SR-1-03
8 CF-1-06
8 CF-1-05
4 SR-3-24
GL-NEC-MAX NO EFFECT
GL-PEL-SR(ERM*NERH)
7 MR-1-07
7 MR-1-25
NERH-85% NO EFFECT
8 CF-1-04
PEL-SR(ERM*NERH)
11 TB-1-01
3 SR-1-06
GL-ERM-50% EFFECT
7 MR-1-02
ERM-50% EFFECT
1 IH-1-04
8 CF-1-02
11 TB-1-04
NEC-MAX NO EFFECT
7 MR-1-17
1 IH-1-03
11 TB-1-02
1 IH-1-06
11 TB-1-03
1 IH-1-07
2 BR-1-01
4.5
1000.0
1.6
*\j i, I_,WIIL oc.iu.xiuc
TOXIC SURV
NOT
NO7
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
100.
100.
100.
100.
100.
100.
64.
108.
100.
100.
114.
90.
97.
100.
96.
103.
96.
88.
123.
80.
88.
79.
96.
120.
114.
102.
91.
109.
128.
0.
10.
109.
0.
102.
93.
115.
1.
11.
1.
52.
0.
89.
0
0
0
0
0
0
9
1
0
0
0
7
4
0
1
8
1
2
0
3
3
0
2
3
9
6
9
3
4
0
3
3
0
7
2
1
4
4
4
3
0
5
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
TX
TX
TX
TX
TX
TX
UU (_&.
GROW
10
10
10
10
10
10
73
79
92
97
89
58
10
10
10
10
94
92
82
85
92
85
91
10
98
10
91
95
10
ND
60
92
ND
94
10
92
96
72
68
97
ND
96
L \JVi J. i.
TOXG
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
NT
NT
NT
TX
NT
NT
ND
TX
TX
ND
NT
NT
TX
NT
TX
NT
NT
ND
NT
O-LUU/ y
MATURE
10
10
10
10
10
10
25
68
96
10
63
24
10
ND
95
10
11
10
93
10
95
10
10
90
77
10
31
12
80
ND
37
95
ND
48
ND
65
0.
ND
0.
ND
ND
10
TOXM
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
ND
TX
NT
ND
NT
ND
NT
NT
ND
NT
ND
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=105 CHEM=Sand TEST=CR14 SAMPTYP=bottom sediment - total UNITS=%
7.1
8.0
8.0
8.0
8.0
8.0
9.0
10.3
11.4
15.0
15.6
16.0
16.0
16.0
17.4
21.4
21.7
28.5
29.2
29.4
29.4
33.0
33.0
37.4
40.0
47.2
49.0
49.1
49.1
52.0
53.0
53.5
53.9
54.0
55.4
56.0
57.5
58.0
60.0
62.0
62.0
70.0
70.2
73.0
73.2
73.2
73.2
74.0
74.0
74.6
75.0
81.0
82.0
98.5
98.5
98.5
NC
NE
NE
NE
NE
NE
NE
NC
NE
NE
SG
*
*
NE
*
NE
SG
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
*
NE
*
NE
NE
NE
NE
0.3 2
5
4
3
1
2
8
0.4 2
3
7
2.0 1
2.0 1
2.2 1
2
3.6 1
.
4
,
.
1.3 2
0.8 7
4
7
8
7
„
2
7
4
7
4
5
8
1.9 5
7
8
4
7
3
.
.
2.2 5
8
2.4 3
8
4
8
4
BR-1-07
WH-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
CF-l-CO
BR-1-08
SR-1-03
MR-l-CO
IH-1-07
IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT @
IH-1-03
BR-1-09
GL-TEL-SR (ERL*NERM) @
IH-1-04
TEL-SR (ERL*NERM) @
SR-3-24
GL-NERM-50% NO EFFECT
GL-ERM-50% EFFECT @
ERM-50% EFFECT @
BR-1-03
MR-1-11
SR-3-16
MR-1-17
PEL-SR(ERM*NERH) @
GL-PEL-SR (ERM*NERH) @
CF-1-01
MR-1-07
NERM-50% NO EFFECT
BR-1-01
MR-1-02
SR-3-08
MR-1-25
SR-3-01
WH-l-RE
CF-1-04
WH-1-02
MR-1-19
CF-1-06
SR-3-05
MR-1-01
SR-1-10
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
WH-1-01
CF-1-03
SR-1-06
CF-1-02
SR-3-02
CF-1-05
SR-3-06
NEC-MAX NO EFFECT @
GL-NEC-MAX NO EFFECT @
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
47
100
100
100
100
100
100
38
104
100
0
0
2
105
2
102
62
70
102
122
95
116
67
113
95
138
96
85
109
51
111
107
104
117
90
8
84
18
79
100
96
103
.9
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.7
.0
.0
.2
.8
.2
.7
.4
.1
.4
.8
.4
.1
.8
.7
.7
.9
.4
.9
.4
.9
.9
.3
.
.6
.0
.7
.0
.6
.3
.3
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
10
ND
10
10
10
10
10
97
10
10
ND
ND
ND
10
ND
11
87
75
12
12
13
11
10
11
11
11
10
ND
11
ND
10
11
11
11
10
ND
10
52
11
12
11
11
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
«i
CONG J
7.1
8.0
8.0
8.0
8.0
8.0
8.0
10.3
11.4
15.6
15.6
15.6
16.0
17.4
21.4
21.4
25.6
28.5
29.4
29.4
33.0
33.0
37.4
38.0
42.0
46.0
46.5
47.2
49.1
52.0
53.9
55.4
56.0
57.5
58.0
62.0
65.6
70.2
73.2
73.2
74.0
74.6
81.0
98.5
98.5
JJW.VJJ
SFFEl
NC
NE
NE
NE
NE
NE
NE
SG
NE
SG
it
*
it
*
NE
* *
NE
NE
NE
NE
* *
NE
NE
NE
NE
SG
SG
NE
*
*
NE
NE
98.5
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=105 CHEM=Sand TEST=HA14 SAMPTYP=bottom sediment -
RATIO SITE SAMPLE C
0.9 2 BR-1-07
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
1.3 2 BR-1-08
3 SR-1-03
2.0 1 IH-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
2.0 1 IH-1-06
2.2 1 IH-1-03
2.7 2 BR-1-09
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
3.6 1 IH-1-04
4 SR-3-24
GL-NERM-50% NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
4.7 2 BR-1-03
9 TR-1-01
NERM-50% NO EFFECT
9 TR-1-02
PEL-SR(ERM*NERH)
4 SR-3-16
GL-PEL-SR (ERM*NERH)
9 TR-1-03
6.7 2 BR-1-01
4 SR-3-08
9 TR-1-04
4 SR-3-01
5 WH-l-RE
1.9 5 WH-1-02
NERH-85% NO EFFECT
1.3 4 SR-3-05
3 SR-1-10
GL-NERH-85% NO EFFECT
2.2 5 WH-1-01
2.4 3 SR-1-06
4 SR-3-02
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
:u.LiudiL - cot
POXIC SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
86.
100.
100.
100.
100.
100.
100.
113.
115.
0.
1.
1.
83.
0.
113.
77.
100.
100.
111.
87.
100.
110.
93.
116.
100.
40.
104.
101.
35.
12.
105.
111.
4
0
0
0
0
0
0
7
6
0
4
4
4
0
3
3
0
0
8
5
0
4
4
2
0
0
5
6
0
5
9
8
.ai u.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
N1T3-'
GROW
85
10
ND
10
10
10
10
85
95
ND
68
96
90
ND
10
85
ND
ND
10
ND
85
10
ND
10
14
11
94
10
13
87
10
94
6
TOXG
TX
NT
ND
NT
NT
NT
NT
TX
NT
ND
NT
NT
TX
ND
NT
TX
ND
ND
NT
ND
TX
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
MATURE TOXM
0.
ND
ND
10
10
10
10
22
23
ND
0.
0.
0.
ND
14
68
ND
ND
16
ND
0.
61
ND
12
ND
ND
22
33
ND
0.
51
74
TX
ND
ND
NT
NT
NT
NT
TX
NT
ND
NT
NT
TX
ND
NT
NT
ND
ND
NT
ND
TX
NT
ND
NT
ND
ND
TX
NT
ND
NT
NT
NT
-------
CONC I
2.5
7.1
8.0
8.0
8.0
8.0
8.0
8.0
8.0
9.0
10.3
11.4
15.0
15.6
15.6
16.0
16.7
17.4
18.5
21.4
21.4
27.5
28.1
28.5
29.4
29.4
33.0
37.4
38.0
40.0
46.0
47.0
47.2
47.2
48.1
49.0
49.0
52.0
52.0
52.0
53.0
53.5
53.5
53.9
54.0
55.4
56.0
56.0
57.5
58.0
60.0
61.3
62.0
62.0
70.0
70.2
70.2
70.2
72.0
73.0
73.2
74.0
74.0
74.6
75.0
81.0
82.0
84.5
98.5
98.5
98.5
JCt\r\Sl,
DFFE<
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
SG
*
*
NC
*
NE
*
NE
**
NE
SG
NE
NE
NE
NE
SG
NE
NE
NC
SG
NE
**
SG
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
*
**
*
SG
**
NE
NE
NE
*
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—} SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=105 CHEM=Sand TEST=HA28 SAMPTYP=bottom sediment - total UNITS=%
RATIO SITE SAMPLE C
0.1 11 TB-1-03
0.8 2 BR-1-07
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
8 CF-l-CO
2 BR-1-08
1.4 3 SR-1-03
7 MR-l-CO
2.0 1 IH-1-07
GL-ERL-15% EFFECT
2.0 1 IH-1-06
ERL-15% EFFECT
2.2 1 IH-1-03
0.5 11 TB-1-02
2.3 2 BR-1-09
GL-TEL-SR (ERL*NERM)
11 TB-1-04
TEL-SR(ERL*NERM)
3.6 1 IH-1-04
4 SR-3-24
GL-NERM-50% NO EFFECT
GL-ERM-50% EFFECT
4.1 2 BR-1-03
9 TR-1-01
1.1 7 MR-1-11
9 TR-1-02
6 UM-l-RE
4 SR-3-16
NERM-50% NO EFFECT
GL-PEL-SR(ERM*NERH)
6 UM-1-02
1.4 7 MR-1-17
6 UM-1-03
9 TR-1-03
0.9 8 CF-1-01
1.5 7 MR-1-07
ERM-50% EFFECT
11 TB-l-RE
5.9 2 BR-1-01
1.5 7 MR-1-02
4 SR-3-08
9 TR-1-04
7 MR-1-25
4 SR-3-01
5 WH-l-RE
8 CF-1-04
PEL-SR(ERM*NERH)
1.9 5 WH-1-02
1.7 7 MR-1-19
8 CF-1-06
4 SR-3-05
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
6 OM-1-01
2.1 7 MR-1-01
9.2 3 SR-1-10
2.2 5 WH-1-01
1.3 8 CF-1-03
9.3 3 SR-1-06
8 CF-1-02
4 SR-3-02
8 CF-1-05
2.1 11 TB-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
>aimer
'OXIC
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
it - cot
SURV
52.3
80.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
97.4
96.2
100.0
0.0
1.4
1.4
11.4
88.2
93.2
0.0
102.6
79.0
81.4
90.7
100.0
86.5
96.1
117.9
115.1
114.9
98.6
64.9
91.9
100.0
89.5
109.3
88.3
82.9
109.3
97.4
109.5
128.4
36.5
114.0
120.3
96.1
119.3
108.1
100.0
71.7
123.0
10.3
102.7
103.8
114.9
0.0
100.0
;ai ui
TOXS
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
M-LTb-l
GROW
97
85
10
ND
ND
10
10
10
10
10
10
91
10
ND
68
96
72
92
10
ND
10
85
ND
58
ND
ND
10
ND
92
ND
ND
73
91
10
96
92
92
ND
95
94
11
10
74 •
89
10
94
ND
79
97
91
82
60
94
10
98
ND
92
5
TOXG
NT
TX
NT
ND
ND
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
TX
NT
NT
ND
NT
TX
ND
TX
ND
ND
NT
ND
TX
ND
ND
TX
TX
NT
NT
TX
NT
ND
NT
NT
NT
NT
TX
TX
NT
NT
ND
TX
TX
NT
TX
TX
NT
NT
NT
ND
NT
MATURE
ND
10
ND
ND
ND
10
10
10
10
10
10
10
10
ND
0.
0.
ND
10
ND
ND
10
10
ND
24
ND
ND
95
ND
65
ND
ND
25
31
ND
10
95
95
ND
12
11
ND
80
ND
63
90
11
ND
68
10
ND
93
37
48
10
77
ND
96
TOXM
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
NT
ND
ND
NT
NT
ND
TX
ND
ND
NT
ND
NT
ND
ND
TX
TX
ND
NT
NT
NT
ND
NT
NT
ND
NT
ND
NT
NT
NT
ND
NT
NT
ND
NT
TX
NT
NT
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 10
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=106 CHEM=Water TEST=CR14 SAMPTYP=bottom sediment - total UNITS=%
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
29.0
29.8
30.0
33.0
35.0
35.0
36.0
36.0
37.0
39.0
39.0
39.0
39.0
39.0
39.0
40.0
40.8
41.7
41.7
41.7
42.0
42.9
42.9
44.0
44.1
44.1
44.1
44.8
45.0
45.9
46.3
46.7
46.7
47.3
48.0
48.7
50.5
52.1
53.5
54.0
54.0
54.4
55.1
55.2
56.0
56.0
61.3
61.3
63.0
64.0
64.0
67.0
67.0
76.4
76.4
76.4
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
NE
NE
NE
SG
SG
NE
SG
SG
NE
NE
NE
SG
NE
SG
NE
NE
NE
SG
NE
NE
SG
NE
NE
NE
NE
7
0.8 1
2
8
7
8
3
8
7
5
4
3
7
1
2
0.8 5
1.0 1
2
. .
.
8
8
1.2 2
.
1.1 1
7
1.2 2
1.2 1
.
4
8
4
1.4 2
4
.
1.3 7
7
4
4
1.2 3
7
4
.
1.2 5
3
5
8
4
. .
MR-l-CO
IH-1-06
BR-1-01
CF-1-05
MR-1-19
CF-l-CO
SR-1-03
CF-1-03
MR-1-01
WH-l-CO
SR-3-CO
SR-l-CO
MR-1-02
IH-l-CO
BR-l-CO
WH-1-01
IH-1-03
BR-1-09
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
CF-1-04
TEL-SR(ERL*NERM>
GL-TEL-SR (ERL*NERM)
CF-1-02
BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
IH-1-04
MR-1-25
BR-1-08
GL-ERM-50% EFFECT @
IH-1-07
ERM-50% EFFECT
SR-3-08
CF-1-06
SR-3-24
BR-1-03
SR-3-16
PEL-SR (ERM*NERH) @
MR-1-11
MR-1-07
GL-PEL-SR (ESM'NERH) S
SR-3-01
SR-3-02
SR-1-06
MR-1-17
SR-3-05
NERH-85% NO EFFECT
WH-1-02
SR-1-10
GL-NERH-85% NO EFFECT
WH-l-RE
CF-1-01
SR-3-06
NEC-MAX NO EFFECT @
GL-NEC-MAX NO EFFECT @
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
100
0
67
96
111
100
104
84
117
100
100
100
113
100
100
8
2
105
109
79
47
2
138
38
0
95
107
102
62
102
70
116
96
100
18
122
104
51
90
85
95
103
.0
.0
.8
.3
.9
.0
.5
.0
.9
.0
.0
.0
.4
.0
.0
.6
.7
.0
.
.9
.
.0
.9
.
.
.0
.8
.0
.
.0
.
.1
.4
.2
.8
.7
.2
.4
.7
.6
.7
.4
.9
.4
.3
.7
.1
.3
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
10
ND
10
11
10
10
10
10
11
ND
10
10
11
10
10
ND
ND
10
11
11
10
ND
11
97
ND
11
11
11
87
12
75
11
10
12
52
12
11
ND
10
ND
13
11
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
ND
NT
ND
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 11
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=106 CHEM=Water TEST=HA14 SAMPTYP=bottom sediment - total UNITS=%
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
29.8 NC 0.8 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
30.0 NC 0.8 2 BR-1-01 TOX 100.0 NT 85 TX 0. TX
36.0 NE . 3 SR-1-03 NOT 115.6 NT 95 NT 23 NT
36.2 NE . 9 TR-1-03 NOT 87.5 NT ND ND ND ND
37.7 NE . 9 TR-1-04 NOT 93.4 NT ND ND ND ND
39.0 NE . 5 WH-l-CO NOT 100.0 NT 10 NT ND ND
39.0 NE . 9 TR-l-CO NOT 100.0 NT ND ND ND ND
39.0 NE . 4 SR-3-CO NOT 100.0 NT 10 NT 10 NT
39.0 NE . 3 SR-l-CO NOT 100.0 NT 10 NT 10 NT
39.0 NE . 1 IH-l-CO NOT 100.0 NT 10 NT 10 NT
39.0 NE . 2 BR-l-CO NOT 100.0 NT 10 NT 10 NT
39.2 . . NERM-50% NO EFFECT
39.4 NE . 9 TR-1-01 NOT 100.0 NT ND ND ND ND
40.0 NC 0.8 5 WH-1-01 TOX 35.0 TX 13 NT ND ND
40.0 . . GL-NERM-50% NO EFFECT
40.4 . . TEL-SR(ERL*NERM)
40.8 SG 1.0 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
40.8 . GL-TEL-SR (ERL*NERM)
41.7 SG 1.1 2 BR-1-09 TOX 83.4 NT 90 TX 0. TX
41.7 . . GL-ERL-15% EFFECT
41.7 . . ERL-15% EFFECT
43.0 NE . 9 TR-1-02 NOT 100.0 NT ND ND ND ND
44.1 SG 1.1 2 BR-1-07 TOX 86.4 NT 85 TX 0. TX
44.8 SG 1.1 1 IH-1-04 TOX 0.0 TX ND ND ND ND
45.9 SG 1.2 2 BR-1-08 TOX 113.7 NT 85 TX 22 TX
46.3 . GL-ERM-50% EFFECT @
46.3 . . ERM-50% EFFECT @
46.7 SG 1.2 1 IH-1-07 TOX 0.0 TX ND ND ND ND
47.3 NE . 4 SR-3-08 NOT 110.4 NT 10 NT 61 NT
48.7 NE . 4 SR-3-24 NOT 113.3 NT 10 NT 14 NT
50.5 SG 1.3 2 BR-1-03 TOX 77.3 TX 85 TX 68 NT
50.6 . . PEL-SR(ERM*NERH) @
52.1 NE . 4 SR-3-16 NOT 111.8 NT 10 NT 16 NT
54.4 . . GL-PEL-SR (ERM*NERH) @
55.1 NE . 4 SR-3-01 NOT 116.2 NT 10 NT 12 NT
55.2 NE . 4 SR-3-02 NOT 105.9 NT 10 NT 51 NT
55.2 . NERH-85% NO EFFECT
56.0 SG 1.2 3 SR-1-06 TOX 12.5 TX 87 NT 0. NT
61.3 SG 1.1 4 SR-3-05 TOX 104.5 NT 94 NT 22 TX
63.0 SG 1.2 5 WH-1-02 TOX 40.0 TX 11 NT ND ND
64.0 NE . 3 SR-1-10 NOT 101.6 NT 10 NT 33 NT
64.0 . GL-NERH-85% NO EFFECT
67.0 NE . 5 WH-l-RE NOT 100.0 NT 14 NT ND ND
76.4 NE . 4 SR-3-06 NOT 111.8 NT 94 NT 74 NT
76.4 . . NEC-MAX NO EFFECT &
76.4 . . GL-NEC-MAX NO EFFECT @
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 12
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=106 CHEM=Water TEST=HA28 SAMPTYP=bottOltl sediment - total UNITS=%
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
24.2
29.0
29.8
30.0
33.0
35.0
35.0
36.0
36.0
36.2
37.0
37.7
39.0
39.0
39.0
39.0
39.0
39.0
39.0
39.0
39.4
40.0
40.8
40.9
41.7
41.7
42.0
42.0
42.4
42.9
43.0
44.0
44.1
44.1
44.1
44.8
45.0
45.9
46.7
47.3
48.0
48.6
48.7
50.5
51.0
52.1
53.2
53.6
54.0
54.0
54.0
54.6
54.6
55.1
55.2
55.2
56.0
56.0
56.0
56.0
61.3
61.3
63.0
63.0
64.0
67.0
67.0
76.4
76.4
85.0
85.0
NC
NE
NC
NC
NE
NC
NE
NC
NC
NE
NG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
SG
NC
NE
NE
NE
NE
SG
SG
NE
NE
SG
NE
NE
NE
SG
NE
NE
SG
NE
SG
SG
NE
NE
NE
NE
SG
SG
NE
SG
SG
SG
NE
SG
NE
NE
0.5
0.8
0.7
0.9
0.9
0.9
.
1.0
.
.
.
1.1
.
0.8
1.0
i!o
t
1.0
.
.
1.1
.
1.2
.
1.2
1.1
1.5
1.5
.
.
1.4
1.5
1.2
1.3
1.6
.
1.7
.
.
.
11
7
1
2
8
7
8
3
8
9
7
9
5
6
9
4
3
7
1
2
9
5
1
2
11
8
9
8
2
1
7
2
1
4
8
4
2
6
4
11
11
7
7
4
4
.
6
6
3
7
4
5
11
3
5
8
4
6
TB-1-01
MR-l-CO
IH-1-06
BR-1-01
CF-1-05
MR-1-19
CF-l-CO
SR-1-03
CF-1-03
TR-1-03
MR-1-01
TR-1-04
WH-l-CO
UM-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
MR-1-02
IH-l-CO
BR-l-CO
TR-1-01
WH-1-01
IH-1-03
NERM-50% NO EFFECT
BR-1-09
GL-NERM-50% NO EFFECT
TB-l-RE
CF-1-04
TEL-SR (ERL*NERM) @
GL-TEL-SR(ERL*NERM) @
TR-1-02
CF-1-02
BR-1-07
GL-ERL-15% EFFECT @
ERL-15% EFFECT
IH-1-04
MR-1-25
BR-1-08
IH-i-07
SR-3-08
CF-1-06
GL-ERM-50% EFFECT @
SR-3-24
BR-1-03
UM-l-RE
SR-3-16
TB-1-02
TB-1-04
MR-1-11
MR-1-07
ERM-50% EFFECT
GL-PEL-SR (ERM*NERH) @
PEL-SR (ERM*NERH)
SR-3-01
SR-3-02
NERH-85% NO EFFECT
UM-1-03
UM-1-02
SR-1-06
MR-1-17
SR-3-05
GL-NERH-85% NO EFFECT
WH-1-02
TB-1-03
SR-1-10
WH-l-RE
CF-1-01
SR-3-06
GL-NEC-MAX NO EFFECT @
UM-1-01
NEC -MAX NO EFFECT @
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
0
100
1
89
114
114
100
96
123
98
108
82
100
100
100
100
100
109
100
100
81
71
1
88
100
128
100
102
80
0
109
97
0
88
120
102
79
86
96
11
93
90
91
97
103
114
117
10
115
96
36
52
100
109
64
100
119
.0
.0
.4
.5
.9
.0
.0
.2
.0
.6
.1
.9
.0
.0
.0
.0
.0
.3
.0
.0
.4
.7
.4
.2
.
.0
.4
.
.0
.7
.3
.0
.3
.4
.0
.3
.3
.6
.0
.5
.1
.4
.2
.7
.9
.4
.8
.
.9
.9
.3
.1
.1
.5
.3
.0
.5
.9
.0
.3
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
NT
ND
10
68
96
98
89
10
91
82
ND
79
ND
10
ND
ND
10
10
92
10
10
ND
91
96
92
10
10
ND
94
85
ND
95
10
ND
92
10
10
85
ND
10
72
10
58
91
94
10
ND
ND
60
92
94
74
97
97
11
73
92
ND
ND
NT
NT
NT
NT
TX
NT
TX
TX
ND
TX
ND
NT
ND
ND
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
ND
NT
TX
ND
NT
NT
ND
NT
NT
NT
TX
ND
NT
TX
NT
TX
TX
NT
NT
ND
ND
TX
TX
NT
TX
NT
TX
NT
TX
NT
ND
ND
10
0.
10
77
63
10
10
93
ND
68
ND
ND
ND
ND
10
10
95
10
10
ND
ND
0.
10
ND
80
ND
48
10
ND
12
10
ND
95
90
10
10
ND
95
ND
ND
24
31
11
10
ND
ND
37
65
11
ND
ND
10
ND
25
96
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
NT
NT
ND
NT
ND
NT
NT
ND
NT
NT
ND
NT
NT
NT
NT
ND
NT
ND
ND
TX
TX
NT
NT
ND
ND
TX
NT
NT
ND
ND
NT
ND
TX
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=110 CHEM=Porewater ammonia TEST=HA14 SAMPTYP=bottoro sediment - total UNITS=mg/l
CONC EFFECT RATIO SITE SAMPLE C
SR-3-CO
SR-3-06
SR-3-05
SR-3-02
SR-3-01
SR-l-CO
IH-l-CO
BR-l-CO
BR-1-07
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
SR-3-08
BR-1-09
BR-1-08
BR-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-16
SR-1-10
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-1-03
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
IH-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-07
BR-1-01
SR-1-06
13
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
1
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.1
.1
.1
.1
.1
.3
.3
.3
.4
.4
.8
NE
NE
NC
NE
NE
NE
NE
NE
NG
NE
*
*
*
NE
NE
NE
NE
**
**
**
**
4
4
0.4 4
4
4
3
1
2
1.0 2
.
.
.
.
4
2.0 2
2.0 2
2.0 2
4
3
.
.
3
4
27.0 1
.
.
37.0 1
137.0 2
43.8 3
;oro seaiment
'OXIC SURV
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
100
111
104
105
116
100
100
100
86
110
83
113
77
111
101
115
113
.0
.8
.5
.9
.2
.0
.0
.0
.4
.4
.4
.7
.3
.8
.6
.6
.3
- toi
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
.aj. ui
GROW
10
94
94
10
10
10
10
10
85
10
90
85
85
10
10
95
10
TOXG MATURE
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
10
74
22
51
12
10
10
10
0.
61
0.
22
68
16
33
23
14
TOXM
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
TOX
1.4 TX 68
NT
0.
NT
TOX 0.0 TX ND ND
TOX 100.0 NT 85 TX
TOX 12.5 TX 87 NT
ND ND
0. TX
0. NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=110 CHEM=Porewater ammonia TEST=HA28 SAMPTYP=bottom sediment - total ONITS=mg/l
CONC EFFECT RATIO SITE SAMPLE C
14
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.1
0.1
0.2
0.2
1.1
NE . 8 CF-l-CO
NC 0.3 7 MR-1-11
NE . 7 MR-l-CO
NE . 8 CF-1-06
NC 0.2 8 CF-1-03
NE . 7 MR-1-25
NE . 4 SR-3-CO
NE . 4 SR-3-06
NE . 4 SR-3-05
NE . 4 SR-3-02
NE . 4 SR-3-01
NE . 3 SR-l-CO
NE . 1 IH-l-CO
NE . 2 BR-l-CO
NC 0.7 2 BR-1-07
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
* 2.3 7 MR-1-19
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
NE . 8 CF-1-05
NE . 4 SR-3-08
SG 1.3 2 BR-1-09
NE . 2 BR-1-08
SG 1.3 2 BR-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
** 4.7 7 MR-1-01
NE . 4 SR-3-16
** 5.0 7 MR-1-02
NE . 8 CF-1-04
GL-NERH-85% NO EFFECT
** 5.2 7 MR-1-17
NC 0.6 11 TB-1-02
** 4.0 3 SR-1-10
NE . 11 TB-l-RE
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
** 7.0 3 SR-1-03
GL-PEL-SR(ERM*NERH)
ERM-50% EFFECT
** 13.5 7 MR-1-07
NE . 11 TB-1-04
NE . 4 SR-3-24
GL-NEC-MAX NO EFFECT
NE . 8 CF-1-02
NEC-MAX NO EFFECT
* 2.2 11 TB-1-03
GL-ERM-50% EFFECT
8 CF-1-01
11 TB-1-01
1 IH-1-06
1 IH-1-07
2 BR-1-01
3 SR-1-06
5.8
4.0
27.0
37.0
91.3
175.0
TOXIC
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
\AJ.lM^li V.
SURV
100.
90.
100.
120.
123.
109.
100.
100.
96.
103.
97.
100.
100.
100.
80.
114.
114.
88.
88.
97.
79.
108.
96.
109.
128.
115.
11.
100.
100.
96.
91.
93.
102.
102.
52.
64.
0.
1.
0.
89.
10.
0
7
0
3
0
3
0
0
1
8
4
0
0
0
3
0
9
3
2
4
0
1
1
3
4
1
4
0
0
2
9
2
6
7
3
9
0
4
0
5
3
UU 1
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
TX
TX
TX
TX
TX
TX
-CI-L Ul
GROW
10
58
10
10
82
95
10
92
94
10
94
10
10
10
85
89
98
92
92
10
85
79
10
92
10
92
72
97
10
91
91
10
10
94
97
73
ND
68
ND
96
60
MX 1O— 1
TOXG
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
NT
TX
NT
TX
TX
TX
NT
TX
TX
NT
NT
NT
NT
TX
ND
NT
ND
NT
TX
MATURE
10
24
10
90
93
12
10
96
11
10
11
10
10
10
10
63
77
95
10
10
10
68
95
95
80
65
ND
10
ND
10
31
ND
10
48
ND
25
ND
0.
ND
10
37
TOXM
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
TX
ND
NT
NT
ND
TX
ND
NT
ND
NT
TX
-------
CONC EFFEC
2350000.
10600000.
13500000.
13500000.
16200000.
25519404.
39700000.
47630000.
47750000.
47750000.
47750000.
47750000.
47750000.
47750000.
48240000.
48730000.
49180000.
57450000.
58030000.
58030000.
58350000.
59220000.
59572012.
60020000.
60940000.
61155000.
61370000.
61750000.
62300000.
70640000.
73160000.
73160000.
0
0
0
0
0
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
3
0
0
0
0
0
0
0
0
0
NC
NE
SG
NE
*
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
SG
NC
NC
NC
NE
NE
NE
SG
SG
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=300 CHEM=Aluminum TEST=HA28 SAMPTYP=bottom sediment - total
GL-SECs NOT REPORTED
0.2 11 TB-1-01
11 TB-l-RE
1.0 11 TB-1-02
ERL-15% EFFECT
11 TB-1-04
TEL-SR(ERL*NERM)
3.0 11 TB-1-03
7 MR-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
0.8 7 MR-1-01
8 CF-1-06
1.0 7 MR-1-11
1.0 8 CF-1-01
ERM-50% EFFECT
1.0 7 MR-1-07
1.0 7 MR-1-02
PEL-SR(ERM'NERH)
1.0 7 MR-1-17
8 CF-1-04
NERH-85% NO EFFECT
8 CF-1-05
8 CF-1-02
1.0 7 MR-1-19
1.3 8 CF-1-03
7 MR-1-25
NEC-MAX NO EFFECT
15
sediment. - to
'OXIC SURV
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
0
100
11
93
52
100
100
100
100
100
100
100
108
120
90
64
91
109
115
128
114
102
114
123
109
.0
.0
.4
.2
.3
.0
.0
.0
.0
.0
.0
.0
.1
.3
.7
.9
.9
.3
.1
.4
.9
.7
.0
.0
.3
i-ai i
TOXS
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
JPi± 1Z> =
GROW
ND
10
72
10
97
10
ND
10
10
10
10
10
79
10
58
73
91
92
92
10
98
94
89
82
95
=ng/ g
TOXG
ND
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
TX
NT
NT
NT
TX
TX
NT
MATURE
ND
ND
ND
ND
ND
10
ND
10
10
10
10
10
68
90
24
25
31
95
65
80
77
48
63
93
12
TOXM
ND
ND
ND
ND
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC I
3600.0
3900.0
5100.0
5800.0
5900.0
6000.0
7240.0
7500.0
7900.0
8200.0
8900.0
8900.0
8900.0
8900.0
10500.0
10900.0
12000.0
12100.0
12100.0
13000.0
13050.0
13100.0
14400.0
14800.0
15200.0
16600.0
17000.0
20435.3
21762.4
25000.0
25600.0
32000.0
32000.0
32000.0
33000.0
34000.0
37200.0
40000.0
41100.0
41600.0
45600.0
47200.0
47200.0
47200.0
47200.0
47200.0
51200.0
51200.0
52000.0
53216.5
54000.0
54022.2
56500.0
57000.0
57000.0
60000.0
60000.0
65000.0
67800.0
70000.0
92900.0
92900.0
93000.0
93000.0
102000.0
150000.0
404000.0
404000.0
700000.0
700000.0
>UH=J
JFFEC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
NE
NE
NE
NG
NE
NE
* *
SG
NE
**
SG
NE
NE
**
NE
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=302 CHEM=Arsenic TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
0.4 3 SR-1-06
8 CF-1-06
3 SR-1-10
1 MR-1-01
—telf—
—slcl—
—telm—
7 MR-l-CO
8 CF-l-CO
—erl—
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
2 BR-1-09
8 CF-1-05
4 SR-3-08
0.7 2 BR-1-08
0.7 2 BR-1-07
0.7 2 BR-1-03
GL-NERM-50% NO EFFECT
3 SR-1-03
4 SR-3-24
NERM-50% NO EFFECT
4 SR-3-06
4 SR-3-05
—pelf—
GL-TEL-SR(ERL'NERM)
TEL-SR(ERL*NERM)
4 SR-3-02
7 MR-1-02
3.6 1 IH-1-04
GL-ERL-15% EFFECT
ERL-15% EFFECT
—slc2—
2 BR-1-01
7 MR-1-07
—aet6—
4 SR-3-01
—pelm—
8 CF-1-04
5 WH-l-RE
5 WH-l-CO
1.0 5 WH-1-01
7 MR-1-17
GL-NERH-85% NO EFFECT
7 MR-1-25
NERH-85% NO EFFECT
5.8 1 IH-1-06
GL-PEL-SR(ERM*NERH)
1.6 7 MR-1-11
PEL-SR(ERM*NERH)
7 MR-1-19
ERM-50% EFFECT
—aet3—
6.7 1 IH-1-03
GL-ERM-50% EFFECT
1.4 5 WH-1-02
8 CF-1-03
—erm—
4 SR-3-16
GL-NEC-MAX NO EFFECT
10.4 1 IH-1-07
—aetl—
8 CF-1-02
—aetS—
8 CF-1-01
NEC-MAX NO EFFECT
—aet4—
—aet2—
16
:UJ.illd.l L, — !_*_> U
'OXIC SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
18.
107.
90.
117.
100.
100.
100.
100.
100.
100.
105.
96.
95.
38.
47.
62.
104.
102.
103.
104.
100.
113.
2.
67.
116.
96.
109.
85.
100.
8.
122.
138.
0.
70.
111.
2.
51.
84.
102.
0.
79.
95.
7
4
3
9
0
0
0
0
0
0
0
3
1
0
9
8
5
2
3
9
6
4
0
8
4
7
9
7
0
6
4
8
0
2
9
7
4
0
7
0
0
1
CLJ. ur
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
TX
NT
NT
TX
NT
NT
GROW
52
11
10
11
10
10
10
10
10
10
10
11
11
97
10
87
10
11
11
11
12
11
ND
10
11
10
11
ND
ND
ND
12
11
ND
75
10
ND
ND
10
12
ND
11
13
ia/s
TOXG
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
ND
TX
NT
ND
ND
NT
NT
ND
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=302 CHEM=Arsenic TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG
17
3600.0
3650.0
4060.0
5100.0
5900.0
6000.0
7240.0
7340.0
8030.0
8200.0
8900.0
8900.0
8900.0
8900.0
8900.0
10450.0
10500.0
11244.8
12000.0
12100.0
12100.0
12100.0
12100.0
13000.0
13100.0
13200.0
14400.0
14400.0
15200.0
16600.0
17000.0
25000.0
32000.0
33000.0
33000.0
33000.0
34000.0
39466.4
39466.4
40000.0
41100.0
41600.0
47200.0
47200.0
47200.0
47200.0
47200.0
52000.0
57000.0
60000.0
65000.0
70000.0
92900.0
92900.0
92900.0
93000.0
93000.0
150000.0
700000.0
700000.0
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
SG
SG
SG
NE
NE
NE
NC
NE
*
*
NE
NE
NE
NG
*•*
* *
SG
NE
* *
0.4 3
9
9
3
.
9
9
.
9
4
3
1
2
.
1.2 2
4
1.4 2
1.4 2
1.5 2
3
4
4
0.6 4
.
4
3.6 1
,
.
.
3.8 2
.
.
4
5
5
1.0 5
.
„
5.8 1
.
6.7 1
1.4 5
.
4
. .
.
10.4 1
.
,
.
.
SR-l-06
TR-1-03
TR-1-04
SR-1-10
—telf—
— slcl —
— telm —
TR-1-01
TR-1-02
~erl—
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
BR-1-09
TEL-SR(ERL*NERM)
SR-3-08
BR-1-08
BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-03
SR-1-03
GL-TEL-SR(ERL*NERM)
SR-3-24
GL-NERM-50% NO EFFECT
SR-3-06
SR-3-05
— pelf~~
SR-3-02
IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
~-slc2 —
BR-1-01
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— aet6 —
SR-3-01
— pelm —
WH-l-RE
WH-l-CO
WH-1-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
IH-1-06
— aet3 —
IH-1-03
WH-1-02
— erm —
SR-3-16
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-07
— aetl —
— aetS—
— aet4 —
— aet2 —
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
12
87
93
101
100
100
100
100
100
100
100
83
110
113
86
77
115
113
111
104
105
0
100
116
100
100
35
1
1
40
111
0
.5
.5
.4
.6
.0
.0
.0
.0
.0
.0
.0
.
.4
.4
.7
.4
.
.3
.6
.3
.8
.5
.9
.0
.0
.2
.0
.0
.0
.
.4
.
.4
.0
.8
.0
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
TX
TX
NT
TX
87
ND
ND
10
ND
ND
ND
10
10
10
10
90
10
85
85
85
95
10
94
94
10
ND
85
10
14
10
13
68
96
11
10
ND
NT
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
ND
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
0.
ND
ND
33
ND
ND
ND
10
10
10
10
0.
61
22
0.
68
23
14
74
22
51
ND
0.
12
ND
ND
ND
0.
0.
ND
16
ND
NT
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
TX
NT
ND
TX
NT
ND
ND
ND
NT
NT
ND
NT
ND
-------
CONC I
0..8
i.o '
1.0
1.0
1.0
1.1
1.1
1.1
1.1
1.1
1.1
1.1
1.2
1.4
1.4
1.4
1.6
1.6
1.7
1.7
1.7
1.7
1.7
1.7
1.9
2.0
2.3
2.3
2.3
2.3
2.3
2.3
2.9
3.2
14.5
•- m
SFFEC
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
SG
NE
*
*
*
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=302 CHEM=Arsenic TEST=HA14 SAMPTYP=porewater
4 SR-3-02
0.8 3 SR-1-06
3 SR-1-03
0.9 1 IH-1-06
0.9 2 BR-1-08
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
1.1 2 BR-1-03
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-01
4 SR-3-06
NERH-85% NO EFFECT
3 SR-1-10
1.5 2 BR-1-09
1.5 2 BR-1-07
GL-NERH-85% NO EFFECT
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM'NERH)
GL-PEL-SR(ERM*NERH)
4 SR-3-08
2.1 1 IH-1-03
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
2.6 1 IH-1-04
2.9 1 IH-1-07
13.2 2 BR-1-01
18
newauer uwj.ia=ug/
'OXIC SURV TOXS
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
105
12
115
1
113
100
100
100
100
100
77
116
111
101
83
86
110
1
0
0
100
.9
.5
.6
.4
.7
.0
.0
.0
.0
.0
.3
.2
.8
.6
.4
.4
.4
.4
.0
.0
.0
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
x
GROW
10
87
95
68
85
ND
10
10
10
10
85
10
94
10
90
85
10
96
ND
ND
85
TOXG MATURE
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
ND
ND
TX
51
0.
23
0.
22
ND
10
10
10
10
68
12
74
33
0.
0.
61
0.
ND
ND
0.
TOXM
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
ND
ND
TX
-------
«Ui*l^A
CONC I
500.0
1200.0
1500.0
1500.0
1500.0
1500.0
1500.0
1500.0
1500.0
2100.0
2700.0
3331.7
5300.0
7400.0
7400.0
8300.0
9100.0
10800.0
10800.0
16365.8
23800.0
23800.0
24800.0
24800.0
29200.0
43400.0
202000.0
JUd-i
SFFEC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
SG
NE
NE
*
**
**
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (---) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=302 CHEM=Arsenic TEST=HA28 SAMPTYP=bottom sediment - sem UNITS=ng/g
GL-SECs NOT REPORTED
8 CF-1-06
0.2 7 MR-1-01
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
7 MR-l-CO
8 CF-1-05
TEL-SR(ERL*NERM)
1.0 7 MR-1-02
1.4 7 MR-1-17
ERL-15% EFFECT
7 MR-1-25
1.8 7 MR-1-07
8 CF-1-04
NERH-85% NO EFFECT
PEL-SR(ERM'NERH)
8 CF-1-02
NEC-MAX NO EFFECT
3.2 8 CF-1-03
ERM-50% EFFECT
5.6 7 MR-1-19
8.3 7 MR-1-11
25.7 8 CF-1-01
19
>eaimt
'OXIC
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
jut. -
su:
120
108
100
100
100
100
100
100
100
114
109
115
109
91
128
102
123
114
90
64
5S
RV
'-
. 1
.0
.0
.0
.0
.0
.0
.0
.9
.3
.1
.3
.9
.4
.7
.0
.0
.7
.9
m UIMJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
. 1O— Jit
GROW
10
79
ND
10
10
10
10
10
10
98
92
92
95
91
10
"94
82
89
58
73
jiy -
TOXG
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
TX
TX
TX
TX
MATURE
90
68
ND
10
10
10
10
10
10
77
95
65
12
31
80
48
93
63
24
25
TOXM
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
-------
rjujuui.
CONC I
3000.0
3600.0
3650.0
3900.0
4060.0
5000.0
5000.0
5000.0
5100.0
5800.0
5900.0
6000.0
7240.0
7340.0
7500.0
7900.0
8030.0
8200.0
8900.0
8900.0
8900.0
8900.0
8900.0
8900.0
10500.0
10797.7
10900.0
12000.0
12100.0
12100.0
13000.0
13000.0
13100.0
13100.0
13124.4
13250.0
14400.0
15200.0
16600.0
17000.0
25000.0
25600.0
30000.0
32000.0
33000.0
34000.0
34000.0
37200.0
40000.0
40060.0
41100.0
41600.0
45600.0
47200.0
47200.0
47200.0
47200.0
47200.0
47200.0
48385.1
49600.0
51200.0
52000.0
54000.0
56500.0
57000.0
60000.0
65000.0
67800.0
70000.0
92900.0
92900.0
93000.0
93000.0
102000.0
102000.0
150000.0
JU£i=J
SFFEC
NC
NC
NE
N3
NE
NE
NE
NG
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NG
NE
NE
NE
SG
SG
SG
NE
NE
NE
NE
NC
* *
*
*
SG
NE
NE
NE
NE
NG
SG
NE
* *
SG
SG
* *
SG
SG
NE
**
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL D; NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=302 CHEM=Arsenic TEST=HA28 SAMPTYP=bottom sediment - total
0.6 11 TB-1-01
0.4 3 SR-1-06
9 TR-1-03
8 CF-1-06
9 TR-1-04
11 TB-l-RE
11 TB-1-04
1.0 11 TB-1-02
0.6 3 SR-1-10
0.2 7 MR-1-01
—telf—
—slcl—
—telm—
9 TR-1-01
7 MR-l-CO
8 CF-l-CO
9 TR-1-02
—erl—
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
1.0 2 BR-1-09
TEL-SR (ERL*NERM)
8 CF-1-05
4 SR-3-08
2 BR-1-08
1.2 2 BR-1-07
1.2 2 BR-1-03
GL-ERL-15% EFFECT
1.5 3 SR-1-03
ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
GL-NERM-50% NO EFFECT
4 SR-3-24
4 SR-3-06
4 SR-3-05
--pelf—
4 SR-3-02
0.9 7 MR-1-02
6.0 11 TB-1-03
3.6 1 IH-1-04
~slc2 —
3.2 2 BR-1-01
GL-ERM-50% EFFECT
1.3 7 MR-1-07
—aet6—
GL-PEL-SR(ERM*NERH)
4 SR-3-01
—pelm—
8 CF-1-04
5 WH-l-RE
5 WH-l-CO
1.0 5 WH-1-01
1.6 7 MR-1-17
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
ERM-50% EFFECT
7 MR-1-25
5.8 1 IH-1-06
1.8 7 MR-1-11
1.9 7 MR-1-19
—aet3—
6.7 1 IH-1-03
1.4 5 WH-1-02
2.0 8 CF-1-03
—erm—
4 SR-3-16
GL-NEC-MAX NO EFFECT
10.4 1 IH-1-07
—aetl—
8 CF-1-02
NEC-MAX NO EFFECT
—aet5—
20
:U. J.illCJ.1 L. — l_(J UO.J. UD
?OXIC SURV TOXS
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
0.
10.
98.
120.
82.
100.
93.
11.
100.
108.
81.
100.
100.
100.
100.
100.
100.
100.
100.
88.
114.
88.
97.
80.
79.
96.
102.
100.
96.
103.
109.
52.
0.
89.
91.
97.
128.
109.
100.
71.
115.
109.
1.
90.
114.
1.
36.
123.
0
3
6
3
9
0
2
4
0
1
4
0
0
0
0
0
0
0
0
2
9
3
4
3
0
2
6
0
1
8
3
3
0
5
9
4
4
5
0
7
1
3
4
7
0
4
5
0
96.1
0.0
102.7
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
*j.io=r
GROW
ND
60
ND
10
ND
10
10
72
97
79
ND
10
10
ND
ND
10
10
10
10
92
98
92
10
85
85
91
10
92
94
10
92
97
ND
96
91
94
10
11
10
91
92
95
68
58
89
96
74
82
10
ND
94
ig/g
TOXG MATURE
ND
TX
ND
NT
ND
NT
NT
TX
TX
TX
ND
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
ND
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
TX
NT
ND
NT
ND
37
ND
90
ND
ND
ND
ND
10
68
ND
10
10
ND
ND
10
10
10
10
10
77
95
10
10
10
10
10
96
11
10
95
ND
ND
10
31
11
80
ND
ND
ND
65
12
0.
24
63
0.
ND
93
95
ND
48
TOXM
ND
TX
ND
NT
ND
ND
ND
ND
NT
NT
ND
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
TX
NT
NT
ND
ND
ND
NT
NT
NT
TX
NT
NT
ND
NT
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 21
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=302 CHEM=Arsenic TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
404000.0 ** 11.9 8 CF-1-01 TOX 64.9 TX 73 TX 25 TX
700000.0 . . —aet4—
700000.0 . . —aet2—
-------
CONC ]
0.8
1.0
1.0
1.0
1.0
1.1
1.1
1.1
1.1
1.1
1.1
1.1
1.1
1.2
1.4
1.4
1.4
1.6
1.6
1.7
1.7
1.7
1.7
1.7
1.8
2.0
2.3
2.3
2.3
2.6
2.9
2.9
3.2
6.5
6.8
7.1
10.1
10.6
14.5
15.7
16.5
20.7
22.8
25.0
29.1
53.7
53.7
57.2
72.2
168.0
EFFEI
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
SG
SG
NE
*
NE
*•
NE
*
SG
SG
NE
* *
*
*
NE
*
NE
NE
*
*
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NCJMCODE=302 CHEM=Arsenic TEST=HA28 SAMPTYP=porewater UNITS=ug/l
RATIO SITE SAMPLE C
4 SR-3-02
0.9 3 SR-1-06
0.9 3 SR-1-03
0.9 1 IH-1-06
2 BR-1-08
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
1.1 2 BR-1-03
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-01
4 SR-3-06
GL-NERH-85% NO EFFECT
1.5 3 SR-1-10
1.6 2 BR-1-09
1.6 2 BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-PEL-SR (ERM*NERH)
GL-ERM-50% EFFECT
4 SR-3-08
2.1 1 IH-1-03
GL-NEC-MAX NO EFFECT
7 MR-l-CO
2.6 1 IH-1-04
8 CF-1-06
2.9 1 IH-1-07
1.0 7 MR-1-07
ERM-50% EFFECT
1.1 7 MR-1-17
7 MR-1-25
PEL-SR(ERM*NERH)
13.8 2 BR-1-01
2.5 7 MR-1-01
NERH-85% NO EFFECT
3.3 7 MR-1-02
8 CF-1-05
3.9 7 MR-1-11
8 CF-1-04
8 CF-1-02
NEC-MAX NO EFFECT
2.6 8 CF-1-01
3.3 8 CF-1-03
26.5 7 MR-1-19
22
•/j-^wauc-L ui^.L ±
roxic SURV
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
103.
10.
96.
1.
97.
100.
100.
100.
100.
100.
100.
79.
97.
100.
100.
88.
80.
88.
1.
100.
0.
120.
0.
91.
115.
109.
89.
108.
109.
114.
90.
128.
102.
64.
123.
114.
8
3
2
4
4
0
0
0
0
0
0
0
4
0
0
2
3
3
4
0
0
3
0
9
1
3
5
1
3
9
7
4
7
9
0
0
o— uy
TOXS
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
TX
NT
TX
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
GROW
10
60
91
68
10
ND
10
10
10
10
10
85
94
92
97
92
85
92
96
10
ND
10
ND
91
92
95
96
79
92
98
58
10
94
73
82
89
TOXG
NT
TX
TX
NT
NT
ND
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
ND
NT
ND
TX
TX
NT
NT
TX
TX
NT
TX
NT
NT
TX
TX
TX
MATURE TOXM
10
37
10
0.
10
ND
10
10
10
10
10
10
11
96
10
10
10
95
0.
10
ND
90
ND
31
65
12
10
68
95
77
24
80
48
25
93
63
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
-------
CONC I
35.0
74.0
112.0
112.0
112.0
167.0
167.0
167.0
167.0
167.0
184.0
225.0
225.0
225.0
225.0
337.0
337.0
337.0
420.8
515.0
562.0
562.0
562.0
562.0
762.0
787.0
787.0
787.0
870.7
899.0
1349.0
1349.0
1349.0
1349.0
1349.0
1405.0
1461.0
1590.0
1690.0
1817.1
1930.0
2040.0
2350.0
2350.0
2460.0
3120.0
3597.0
3870.0
7490.0
31300.0
31300.0
*\JLIEi-
5FFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NC
NE
**
NE
* *
it *
NE
**
NE
NE
NE
NE
NE
NE
NE
**
NE
* *
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=CR14 SAMPTYP=bottom sediment - sem UNITS=ng/g
RATIO SITE SAMPLE C
7 MR-1-01
8 CF-1-06
4 SR-3-06
4 SR-3-02
3 SR-1-10
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
7 MR-l-CO
4 SR-3-05
3 SR-1-03
0.3 2 BR-1-08
GL-NERM-50% NO EFFECT
4 SR-3-24
0.5 2 BR-1-03
NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
4 SR-3-08
2 BR-1-09
0.8 2 BR-1-07
GL-NERH-85% NO EFFECT
8 CF-1-05
4.7 1 IH-1-04
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-PEL-SR(ERM*NERH)
4 SR-3-16
8.0 3 SR-1-06
8.1 1 IH-1-06
2 BR-1-01
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
8.7 1 IH-1-03
7 MR-1-02
8 CF-1-03
PEL-SRIERM*NERH)
8 CF-1-04
7 MR-1-07
7 MR-1-19
NERH-85% NO EFFECT
7 MR-1-17
8 CF-1-02
21.5 1 IH-1-07
7 MR-1-25
4.2 7 MR-1-11
8 CF-1-01
NEC-MAX NO EFFECT
23
>eaime
?OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
>nt - se
SURV
117.9
107.4
103.3
100.6
90.3
100.0
100.0
100.0
100.0
100.0
100.0
104.9
104.5
38.0
102.2
62.8
95.1
105.0
47.9
96.3
2.0
102.7
18.7
0.0
67.8
2.7
113.4
84.0
109.9
116.4
111.9
122.4
79.0
0.0
138.8
70.2
95.1
m UJNJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
LTi-nc
GROW
11
11
11
12
10
10
10
10
10
10
10
11
10
97
11
87
11
10
10
11
ND
12
52
ND
10
ND
11
10
11
11
10
12
11
ND
11
75
13
j/g —
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
NT
TX
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
24
jMUjai.
CONC
93.0
160.0
180.0
180.0
180.0
180.0
234.0
274.0
320.0
388.0
500.0
510.0
596.0
600.0
680.0
700.0
700.0
790.0
790.0
890.0
900.0
920.0
920.0
1050.0
1110.0
1200.0
1400.0
2000.0
2026.8
2400.0
2420.0
2500.0
2500.0
2740.0
2893.4
2930.0
3130.0
3530.0
3680.0
3750.0
3750.0
4000.0
4210.0
4220.0
5100.0
5200.0
5200.0
5208.2
6623.8
6680.0
6700.0
7000.0
8000.0
8000.0
9100.0
9100.0
9600.0
9600.0
9600.0
10000.0
10000.0
10850.0
11700.0
11700.0
12000.0
13300.0
24200.0
41100.0
41100.0
44500.0
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
* *
NE
NE
**
**
**
**
**
NE
**
RATIO SITE
7
3
4
3
1
2
8
8
5
7
4
4
.
2
0.4 2
4
4
0.6 2
3
8
4
0.9 2
4
,
7
8
0.6 5
8
4
7
7
7
2
8
28.9 1
. ,
7
.
5
.
50.6 1
.
.
23.8 3
65.0 1
.
4.6 7
134.4 1
8
.
10.7 5
jm Tcsl-CK.1.4 tfACUTxr^DOE
SAMPLE
MR-1-01
SR-1-10
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
CF-1-06
CF-l-CO
WH-l-CO
MR-l-CO
SR-3-06
SR-3-02
— telf—
— slcl —
— telm —
BR-1-09
BR-1-08
SR-3-01
GL-NERM-50% NO EFFECT
SR-3-05
BR-1-07
SR-1-03
NERM-50% NO EFFECT
CF-1-05
SR-3-24
— erl—
BR-1-03
SR-3-08
GL-TEL-SR (ERL*NERM)
MR-1-02
CF-1-03
WH-1-01
GL-NERH-85% NO EFFECT
CF-1-04
TEL-SR(ERL*NERM)
SR-3-16
MR-1-07
— pelf—
MR-1-19
MR-1-17
NERH-85% NO EFFECT
BR-1-01
— pelm —
CF-1-02
— aet3 —
IH-1-04
GL-ERL-15% EFFECT
GL-PEL-SR (ERM*NERH)
PEL-SR(ERM*NERH)
MR-1-25
— aetl —
— aet6 —
WH-l-RE
GL-NEC-MAX NO EFFECT
IH-1-03
ERL-15% EFFECT
— erm —
— aet4 —
— aet2 —
SR-1-06
— slc2 —
GL-ERM-50% EFFECT
IH-1-06
ERM- 50% EFFECT
— aet5 —
MR-1-11
IH-1-07
CF-1-01
NEC-MAX NO EFFECT
WH-1-02
;u.4.iuc*i <- uvj u
mic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
117
90
100
100
100
100
107
100
100
100
103
100
105
38
96
104
47
104
96
102
62
95
113
84
8
109
102
116
111
122
67
79
2
.9
.3
.0
.0
.0
.0
.4
.0
.0
.0
.3
.6
.0
.0
.7
.9
.9
.5
.3
.2
.8
.1
.4
.0
.6
.9
.7
.4
.9
.4
.8
.0
.0
O.J. Ui
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
N J. 4. w>— 1
GROW
11
10
10
10
10
10
11
10
ND
10
11
12
10
97
10
11
10
10
11
11
87
11
11
10
ND
11
12
11
10
12
10
11
ND
'U'U -
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
138.8 NT 11
85.7 NT
2.7 TX
ND
ND
18.7 TX 52
NT
ND
ND
TX
0.0 TX ND ND
70.2 TX
0.0 TX
95.1 NT
75
ND
13
TX
ND
NT
51.4 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
j^i
CONC EFFEI
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
1
1
1
1
2
2
3
14
.0
.0
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.1
.2
.2
.2
.2
.2
.2
.2
.2
.2
.2
.3
.3
.3
.4
.4
.5
.8
.0
.0
.1
.1
.6
.4
.4
.8
.3
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
NE
NE
NE
NE
* *
* *
* *
NE
NE
**
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=CR14 SAMPTYP=porewater
7 MR-1-02
7 MR-1-01
8 CF-1-06
8 CF-1-05
8 CF-1-04
3 SR-1-10
3 SR-1-03
7 MR-l-CO
2 BR-1-09
0.8 2 BR-1-08
0.8 2 BR-1-07
0.8 2 BR-1-03
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
2 BR-1-01
7 MR-1-07
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
7 MR-1-17
2.4 1 IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-08
4 SR-3-06
4 SR-3-02
4 SR-3-01
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
8 CF-1-03
NERH-85% NO EFFECT
7 MR-1-25
8 CF-1-02
GL-PEL-SR(ERM*NERH)
PEL-SR(ERM*NERH)
11.7 3 SR-1-06
12.5 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
13.8 1 IH-1-03
7 MR-1-19
8 CF-1-01
NEC-MAX NO EFFECT
11.6 7 MR-1-11
178.8 1 IH-1-07
25
jrewai
?OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
;er uiNii
SURV
113.4
117.9
107.4
96.3
109.9
90.3
104.5
100.0
105.0
38.0
47.9
62.8
100.0
100.0
100.0
100.0
100.0
67.8
116.4
122.4
0.0
95.1
103.3
100.6
96.7
84.0
138.8
79.0
18.7
2.0
2.7
111.9
95.1
70.2
0.0
s=ug,
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
TX
i j.
GROW
11
11
11
11
11
10
10
10
10
97
10
87
10
10
10
10
10
10
11
12
ND
11
11
12
10
10
11
11
52
ND
ND
10
13
75
ND
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
NT
TX
ND
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC EFFEC
112
112
112
167
167
167
167
167
167
167
225
225
225
237
237
337
337
337
337
562
562
562
562
562
774
774
787
899
899
899
1068
1068
1349
1349
1349
1461
3597
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.2
.0
.0
.0
.0
.0
.0
.0
.0
.0
.7
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
SG
NE
*
NE
it
*
* *
NE
* *
* *
**
**
**
APPENDIX 4--- ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
2 no effect [ NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=ng/g
4 SR-3-06
4 SR-3-02
3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
0.6 4 SR-3-05
3 SR-1-03
1.3 2 BR-1-08
TEL-SR (ERL*NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-24
2.0 2 BR-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-08
3.4 2 BR-1-09
3.4 2 BR-1-07
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
GL-PEL-SR(ERM*NERH)
4.7 1 IH-1-04
4 SR-3-16
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
8.0 3 SR-1-06
8.1 1 IH-1-06
8.1 2 BR-1-01
8.7 1 IH-1-03
21.5 1 IH-1-07
26
>cuj.ii(ciiu - se
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
111
105
101
100
100
100
100
100
104
115
113
113
77
110
83
86
0
111
12
1
100
1
0
.8
.9
.6
.0
.0
.0
.0
.0
.5
.6
.7
.3
.3
.4
.4
.4
.0
.8
.5
.4
.0
.4
.0
ill UWJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
TX
TX
L Id— I1C
GROW
94
10
10
ND
10
10
10
10
94
95
85
10
85
10
90
85
ND
10
87
68
85
96
ND
j/H --
TOXG
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
ND
NT
NT
NT
TX
NT
ND
MATURE
74
51
33
ND
10
10
10
10
22
23
22
14
68
61
0.
0.
ND
16
0.
0.
0.
0.
ND
TOXM
NT
NT
NT
ND
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
ND
NT
NT
NT
TX
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES {ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
27
160.0
180.0
180.0
180.0
180.0
180.0
243.0
320.0
384.0
446.0
500.0
500.0
510.0
550.0
591.6
596.0
600.0
650.0
674.5
680.0
700.0
700.0
700.0
700.0
790.0
890.0
900.0
920.0
1110.0
1200.0
1400.0
2000.0
2000.0
2500.0
2500.0
2930.0
3224.9
3530.0
3605.6
4000.0
4210.0
5100.0
5200.0
5200.0
5200.0
6700.0
7000.0
8000.0
8000.0
8000.0
9100.0
9600.0
9600.0
9600.0
10000.0
10000.0
11700.0
12000.0
24200.0
44500.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
*
NE
NC
* -it
NE
NE
* *
NE
NC
NE
**
**
NE
* *
**
* *
* *
* *
.
.
.
3.9
3.9
0.8
5.0
7.8
0.6
22.2
28.9
50.6
23.8
65.0
134.4
10.7
3
9
4
3
1
2
9
5
9
9
4
4
9
2
2
.
4
4
2
3
4
2
4
.
5
4
2
1
5
1
3
1
1
5
SR-1-10
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-01
WH-l-CO
TR-1-03
TR-1-02
SR-3-06
NERM-50% NO EFFECT
SR-3-02
TR-1-04
TEL-SR(ERL*NERM)
— telf—
— slcl—
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
— telm —
BR-1-09
BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-01
SR-3-05
BR-1-07
SR-1-03
SR-3-24
__erl—
BR-1-03
SR-3-08
NERH-85% NO EFFECT
WH-1-01
GL-NERH-85% NO EFFECT
SR-3-16
PEL-SR(ERM*NERH)
— pelf--
GL-PEL-SR(ERM'NERH)
BR-1-01
— pelm —
— aet3 —
IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
— aetl —
— aet6 —
WH-l-RE
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-03
— erm —
— aet4 —
— aet2 —
SR-1-06
— slc2~
IH-1-06
— aet5 —
IH-1-07
WH-1-02
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
101
100
100
100
100
100
100
100
87
100
111
105
93
83
113
116
104
86
115
113
77
110
35
111
100
0
100
1
12
1
0
40
.6
.0
.0
.0
.0
.0
.0
.0
.5
.0
.8
.9
.4
.4
.7
.2
.5
.4
.6
.3
.3
.4
.0
.8
.0
.0
.
.
.0
.4
.
.5
.4
.0
.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
TX
TX
TX
TX
TX
10
ND
10
10
10
10
ND
10
ND
ND
94
10
ND
90
85
10
94
85
95
10
85
10
13
10
85
ND
14
96
87
68
ND
11
NT
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
NT
ND
TX
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
ND
NT
NT
NT
NT
ND
NT
33
ND
10
10
10
10
ND
ND
ND
ND
74
51
ND
0.
22
12
22
0.
23
14
68
61
ND
16
0.
ND
ND
0.
0.
0.
ND
ND
NT
ND
NT
NT
NT
NT
ND
ND
ND
ND
NT
NT
ND
TX
TX
NT
TX
TX
NT
NT
NT
NT
ND
NT
TX
ND
ND
NT
NT
NT
ND
ND
-------
CONC EFFECT
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
1.
14.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
2
2
2
2
2
2
2
2
4
4
8
9
9
0
1
3
NE
NE
NC
NC
NC
NC
NE
NE
NE
NE
NE
SG
*
NE
NE
NE
NE
* *
* *
* *
* *
^\JLJCI— J u J \_ni
RATIO SIT!
3
3
0.9 2
0.9 2
0.9 2
0.9 2
9
4
3
1
2
.
1.3 2
.
2.4 1
4
4
4
4
.
. .
.
11.7 3
.
12.5 1
13.8 1
178.8 1
(rewater UWJ.T
'OXIC SURV
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
101.
115.
83.
113.
86.
77.
100.
100.
100.
100.
100.
6
6
4
7
4
3
0
0
0
0
0
s-ug/
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
±
GROW
10
95
90
85
85
85
ND
10
10
10
10
TOXG
NT
NT
TX
TX
TX
TX
ND
NT
NT
NT
NT
MATURE
33
23
0.
22
0.
68
ND
10
10
10
10
TOXM
NT
NT
TX
TX
TX
NT
ND
NT
NT
NT
NT
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
NUMCODE=303 CHEM=Cadtaiiuro TEST=HA14 SAMPTYP=porewater
SR-1-10
SR-1-03
BR-1-09
BR-1-08
BR-1-07
BR-1-03
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
BR-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
IH-1-06
SR-3-08
SR-3-06
SR-3-02
SR-3-01
NERH-85% NO EFFECT
NEC-MAX NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
SR-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-04
IH-1-03
IH-1-07
28
TOX 100.0 NT 85 TX
TOX 1.4 TX 68 NT
NOT 110.4 NT 10 NT
NOT 111.8 NT 94 NT
NOT 105.9 NT 10 NT
NOT 116.2 NT 10 NT
TOX
12. 5 TX 87
TOX 0.0 TX ND
TOX 1.4 TX 96
TOX 0.0 TX ND
NT
ND
NT
ND
0.
0.
ND
0.
ND
TX
0. NT
61 NT
74 NT
51 NT
12 NT
NT
ND
NT
ND
-------
IN urn
CONC I
35.0
74.0
112.0
112.0
112.0
167.0
167.0
167.0
167.0
167.0
167.0
167.0
175.5
184.0
225.0
225.0
225.0
237.2
314.1
337.0
337.0
337.0
562.0
562.0
562.0
562.0
562.0
762.0
774.7
787.0
899.0
899.0
1068.0
1349.0
1349.0
1349.0
1405.0
1461.0
1494.6
1590.0
1590.0
1690.0
1930.0
2040.0
2350.0
2460.0
3120.0
3597.0
3870.0
3870.0
7490.0
31300.0
_VLTJ-
3FFEC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
NE
*
*
NE
* *
NE
**
* *
* *
* *
NC
SG
NE
SG
SG
SG
NE
* *
NE
*
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=HA28 SAMPTYP=bottom sediment - sem
0.0 7 MR-1-01
8 CF-1-06
4 SR-3-06
4 SR-3-02
0.7 3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
7 MR-l-CO
4 SR-3-05
1.3 3 SR-1-03
2 BR-1-08
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
4 SR-3-24
1.7 2 BR-1-03
GL-ERL-15% EFFECT
4 SR-3-08
2.9 2 BR-1-09
2.9 2 BR-1-07
GL-NERH-85% NO EFFECT
ERL-15% EFFECT
8 CF-1-05
GL-PEL-SR(ERM*NERH)
4.7 1 IH-1-04
4 SR-3-16
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
8.1 3 SR-1-06
8.1 1 IH-1-06
6.9 2 BR-1-01
ERM-50% EFFECT
8.7 1 IH-1-03
PEL-SR(ERM*NERH)
0.8 7 MR-1-02
NERH-85% NO EFFECT
1.4 8 CF-1-03
8 CF-1-04
1.0 7 MR-1-07
1.2 7 MR-1-19
1.2 7 MR-1-17
8 CF-1-02
21.5 1 IH-1-07
7 MR-1-25
NEC-MAX NO EFFECT
3.7 7 MR-1-11
25.9 8 CF-1-01
29
ieaiment - se
TOXIC SURV
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
108
120
100
103
100
100
100
100
100
100
100
100
96
96
97
102
79
88
88
80
114
0
96
10
1
89
1
109
123
128
91
114
115
102
0
109
90
64
.1
.3
.0
.8
.0
.0
.0
.0
.0
.0
.0
.0
.1
.2
.4
.6
.0
.3
.2
.3
.9
.0
.1
.3
.4
.5
.4
.3
.0
.4
.9
.0
.1
.7
.0
.3
.7
.9
:m urj.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
TX
NT
TX
TX
TX
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
Lib-nt
GROW
79
10
92
10
97
ND
10
10
10
10
10
10
94
91
10
10
85
92
92
85
98
ND
10
60
68
96
96
92
82
10
91
89
92
94
ND
95
58
73
j/g —
TOXG
TX
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
ND
NT
TX
NT
NT
NT
TX
TX
NT
TX
TX
TX
NT
ND
NT
TX
TX
MATURE TOXM
68
90
96
10
10
ND
10
10
10
10
10
10
11
10
10
10
10
95
10
10
77
ND
95
37
0.
10
0.
95
93
80
31
63
65
48
ND
12
24
25
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
ND
NT
TX
TX
-------
JNUJfll_l.
CONC I
93.0
160.0
180.0
180.0
180.0
180.0
180.0
221.0
234.0
236.0
243.0
274.0
300.0
300.0
312.0
320.0
361.0
384.0
388.0
400.0
446.0
472.0
486.0
500.0
500.0
500.0
510.0
550.0
583.3
596.0
600.0
605.0
680.0
700.0
700.0
700.0
737.9
790.0
890.0
900.0
900.0
920.0
968.0
1050.0
1110.0
1130.0
1200.0
1400.0
2000.0
2040.0
2400.0
2420.0
2500.0
2500.0
2670.0
2720.0
2720.0
2740.0
2930.0
3130.0
3246.5
3530.0
3605.6
3680.0
3750.0
3875.0
4000.0
4210.0
4220.0
5100.0
5200.0
5200.0
6680.0
6700.0
7000.0
8000.0
8000.0
IUD-^
!FFEC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
*
* *
NE
NE
NE
NE
*
NE
NE
NC
SG
NC
NE
NE
NE
NE
NC
SG
SG
* *
NE
* *
NE
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=303 CHEM=Cadmium TEST=HA28 SAMPTYP=bottom sediment - total UNITS
RATIO SITE SAMPLE
0.0 7 MR-1-01
0.9 3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
10 MB-1-04
8 CF-1-06
6 UM-l-CO
9 TR-1-01
8 CF-l-CO
11 TB-l-RE
0.9 11 TB-1-01
6 UM-l-RE
5 WH-l-CO
10 MB-1-02
9 TR-1-03
7 MR-l-CO
11 TB-1-04
9 TR-1-02
10 MB-l-RE
NERM-50% NO EFFECT
1.4 11 TB-1-03
1.4 11 TB-1-02
4 SR-3-06
4 SR-3-02
9 TR-1-04
TEL-SR(ERL*NERM)
—telf—
—slcl—
GL-NERM-50% NO EFFECT
—telm—
1.6 2 BR-1-09
2 BR-1-08
ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
4 SR-3-01
4 SR-3-05
2.0 2 BR-1-07
GL-ERL-15% EFFECT
5.1 3 SR-1-03
10 MB-1-03
8 CF-1-05
4 SR-3-24
10 MB-1-01
—erl—
3.2 2 BR-1-03
4 SR-3-08
6 UM-1-02
0.7 7 MR-1-02
1.4 8 CF-1-03
0.6 5 WH-1-01
GL-NERH-85% NO EFFECT
6 UM-1-01
6 UM-1-03
NERH-85% NO EFFECT
8 CF-1-04
4 SR-3-16
0.9 7 MR-1-07
PEL-SR(ERM*NERH)
—pelf—
GL-PEL-SR(ERM*NERH)
1.0 7 MR-1-19
1.1 7 MR-1-17
ERM-50% EFFECT
9.1 2 BR-1-01
—pelm—
8 CF-1-02
—aet3—
28.9 1 IH-1-04
GL-ERM-50% EFFECT
7 MR-1-25
—aetl—
—aet6—
5 WH-l-RE
NEC-MAX NO EFFECT
30
;uj,iuci>
?OXIC
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
tu - v-wc
SURV
108.1
100.0
100.0
100.0
100.0
100.0
100.0
95.5
120.3
100.0
81.4
100.0
100.0
0.0
86.5
100.0
97.0
98.6
100.0
93.2
100.0
100.0
52.3
11.4
100.0
103.8
82.9
88.2
97.4
97.4
96.1
80.3
96 '.2
95.5
114.9
102.6
75.8
79.0
88.3
117.9
109.3
123.0
71.7
119.3
114.9
128.4
96.1
91.9
114.0
115.1
89.5
102.7
0.0
109.3
aj. ur
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
*X1 O-l,
GROW
79
97
ND
10
10
10
10
ND
10
ND
ND
10
10
ND
ND
10
ND
ND
10
10
ND
ND
97
72
92
10
ND
92
10
94
94
85
91
ND
98
10
ND
85
92
ND
92
82
91
ND
ND
10
10
91
89
92
96
94
ND
95
iS/y -
TOXG :
TX
TX
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
NT
ND
ND
NT
ND
ND
NT
NT
ND
ND
NT
TX
NT
NT
ND
NT
NT
NT
NT
TX
TX
ND
NT
NT
ND
TX
NT
ND
TX
TX
NT
ND
ND
NT
NT
TX
TX
TX
NT
NT
ND
NT
MATURE
68
10
ND
10
10
10
10
ND
90
ND
ND
10
ND
ND
ND
ND
ND
ND
10
ND
ND
ND
ND
ND
96
10
ND
10
10
11
11
10
10
ND
77
10
ND
10
95
ND
95
93
ND
ND
ND
80
95
31
63
65
10
48
ND
12
TOXM
NT
NT
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
NT
NT
ND
NT
NT
ND
ND
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
NOT
109.5 NT 11
NT
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEM=Cadmium TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
31
CONC EFFECT RATIO SITE SAMPLE
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
8000
9100
9600
9600
9600
10000
10000
11700
12000
13300
24200
41100
44500
.0
.0 **
.0
.0
.0
.0 **
.0
.0 **
.0
.0 *
.0 **
.0 **
.0 **
GL-NEC-MAX NO EFFECT
50
55
65
3
134
24
10
.6
.
.6
t
.0
.8
.4
.1
.7
1
3
1
7
1
8
S
IH-1-03
— erm —
— aet4 —
— aet2 —
SR-1-06
— slc2 —
IH-1-06
— aet5 —
MR-1-11
IH-1-07
CF-1-01
WH-1-02
TOX
TOX
TOX
TOX
TOX
TOX
TOX
1.4 TX 96
NT
0.
NT
TOX
TOX
TOX
TOX
TOX
TOX
10
1
90
0
64
36
.3
.4
.7
.0
.9
.5
TX
TX
NT
TX
TX
TX
60
68
58
ND
73
74
TX
NT
TX
ND
TX
TX
37
0.
24
ND
25
ND
TX
NT
TX
ND
TX
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
32
CONC I
0.0
0.0
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.3
0.3
0.4
0.4
0.4
0.5
0.8
0.9
1.0
1.1
1.1
1.6
2.4
3.8
14.3
3FFECT
NC
NC
NE
NE
NE
NC
NC
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
SG
NC
NC
*
NE
NE
NE
NE
*
NE
NE
•* it
* *
**
**
* *
**
**
\~\JlJCi— J U J
RATIO ;
0.1
0.1
.
.
.
0.8
0.9
0.9
.
0.9
0.9
.
.
.
1.3
.
0.6
0.8
2.4
.
.
.
.
2.2
.
.
10.5
,
12.5
13.8
8.2
19.6
19.4
178.8
i-nc.
SITE
7
7
8
8
8
3
3
7
2
2
2
2
9
4
3
1
8
2
.
2
7
7
1
4
4
4
4
8
7
8
3
1
1
7
8
7
1
fj=i~auiiu.uni lEidL-cut^o Dttinr
SAMPLE
MR-1-02
MR-1-01
CF-1-06
CF-1-05
CF-1-04
SR-1-10
SR-1-03
MR-l-CO
BR-1-09
BR-1-08
BR-1-07
BR-1-03
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
BR-1-01
GL-ERL-15% EFFECT
MR-1-07
TEL-SR (ERL*NERM)
MR-1-17
IH-1-06
ERL-15% EFFECT
SR-3-08
SR-3-06
SR-3-02
SR-3-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
CF-1-03
MR-1-25
CF-1-02
NEC -MAX NO EFFECT
GL-PEL-SR (ERM*NERH)
PEL-SR(ERM*NERH)
SR-1-06
GL-ERM-50% EFFECT
IH-1-04
ERM-50% EFFECT
IH-1-03
MR-1-19
CF-1-01
MR-1-11
IH-1-07
irewater UNIT
?OXIC SURV
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
109
108
120
114
128
100
96
100
88
97
80
79
100
100
100
100
100
100
89
91
115
1
88
100
103
97
123
109
102
10
0
1
114
64
90
0
.3
.1
.3
.9
.4
.0
.2
.0
.2
.4
.3
.0
.0
.0
.0
.0
.0
.0
.5
.9
.1
.4
.3
.0
.8
.4
.0
.3
.7
.3
.0
.4
.0
.9
.7
.0
s=ug,
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
TX
Fl
GROW
92
79
10
98
10
97
91
10
92
10
85
85
ND
10
10
10
10
10
96
91
92
68
92
92
10
94
82
95
94
60
ND
96
89
73
58
ND
TOXG
TX
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
ND
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
ND
NT
TX
TX
TX
ND
MATURE TOXM
95
68
90
77
80
10
10
10
10
10
10
10
ND
10
10
10
10
10
10
31
65
0.
95
96
10
11
93
12
48
37
ND
0.
63
25
24
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
TX
TX
ND
-------
CONC EFFEI
416
572
676
780
780
990
1248
1300
1352
1352
1352
1650
1650
1650
1650
1650
1720
1720
1820
1960
2184
2184
2210
2275
2370
2580
2620
2800
2900
3010
3010
3050
3328
3328
3860
4450
5414
6180
9471
10265
14975
14975
14975
21682
21682
22254
31665
41077
41077
60315
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.3
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.0
.7
.6
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NE
NE
NE
NE
* *
* *
* *
* *
259668.0
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chromium TEST=CR14 SAMPTYP=bottom sediment - Sero UNITS=ng/g
3 SR-1-10
4 SR-3-02
0.1 2 BR-1-08
4 SR-3-06
4 SR-3-05
7 MR-1-01
0.2 2 BR-1-07
2 BR-1-09
4 SR-3-24
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
8 CF-1-03
NERM-50% NO EFFECT
3 SR-1-03
7 MR-l-CO
4 SR-3-08
GL-NERH-85% NO EFFECT
7 MR-1-19
TEL-SR(ERL*NERM)
8 CF-1-06
7 MR-1-02
7 MR-1-17
7 MR-1-25
7 MR-1-07
1.3 7 MR-1-11
ERL-15% EFFECT
8 CF-1-02
0.6 2 BR-1-03
NERH-85% NO EFFECT
8 CF-1-04
8 CF-1-05
GL-TEL-SR(ERL*NERM)
8 CF-1-01
GL-PEL-SR(ERM*NERH)
PEL-SR(ERM*NERH)
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
16.7 3 SR-1-06
GL-ERL-15% EFFECT
13.5 1 IH-1-04
ERM-50% EFFECT
24.9 1 IH-1-03
GL-ERM-50% EFFECT
36.6 1 IH-1-06
157.4 1 IH-1-07
33
sediment. - 5
?OXIC SURV
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
90.
100.
38.
103.
104.
117.
47.
105.
102.
102.
100.
100.
100.
100.
100.
84.
104.
100.
95.
111.
107.
113.
122.
138.
116.
70.
79.
62.
109.
96.
3
6
0
3
9
9
9
0
2
7
0
0
0
0
0
0
5
0
1
9
4
4
4
8
4
2
0
8
9
3
em uj
TOXS
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
MJ.J.&-1
GROW
10
12
97
11
11
11
10
10
11
12
10
10
10
10
10
10
10
10
11
10
11
11
12
11
11
75
11
87
11
11
reg/g -
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
NOT
TOX
TOX
TOX
TOX
TOX
95.1 NT
67.8 NT
18.7 TX
2.0 TX
2.7 TX
0.0 TX
0.0 TX
13
10
52
ND
NT
NT
TX
ND
ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
iMun^wuc.— .
CONC EFFEI
23500
24700
24800
26000
27300
27800
27900
29200
29500
31600
34000
34500
34800
35000
35300
35500
37300
38500
38900
39300
39300
39796
40000
40300
40600
41000
42000
45300
52000
52000
52000
52000
52000
52300
56000
58000
59000
70000
70000
81000
90000
90000
92000
93500
95000
110000
113000
119365
159405
160000
195075
260000
270000
274000
274000
280000
312000
312000
312000
319000
363000
370000
407000
407000
572000
1132000
2610000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NC
* *
NE
* *
* *
**
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=304 CHEM=Chromium TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
5 WH-l-CO
4 SR-3-02
8 CF-1-06
—slcl—
8 CF-1-03
8 CF-1-02
7 MR-1-01
8 CF-1-05
5 WH-l-RE
7 MR-1-02
4 SR-3-05
8 CF-1-01
4 SR-3-06
7 MR-1-07
7 MR-1-17
7 MR-1-19
—telf—
1.5 5 WH-1-01
7 MR-l-CO
1.1 7 MR-1-11
ERL-15% EFFECT
TEL-SR(ERL'NERM)
3 SR-1-10
NERM-50% NO EFFECT
7 MR-1-25
8 CF-l-CO
4 SR-3-01
8 CF-1-04
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
GL-NERM-50% NO EFFECT
—telm—
2 BR-1-09
4 SR-3-16
4 SR-3-24
0.5 2 BR-1-08
NERH-85% NO EFFECT
~erl—
3 SR-1-03
--pelf—
0.7 2 BR-1-07
GL-NERH-85% NO EFFECT
4 SR-3-08
—Slc2~
0.8 2 BR-1-03
GL-TEL-SR (ERL*NERM)
PEL-SR (ERM*NERH)
—pelm—
GL-PEL-SR (ERM*NERH)
—aet3—
—aetl—
10.3 5 WH-1-02
GL-ERL-15% EFFECT
—aet5—
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
5.3 3 SR-1-06
ERM-50% EFFECT
—erm—
7.8 1 IH-1-04
GL-ERM-50% EFFECT
11.0 1 IH-1-03
21.8 1 IH-1-06
50.2 1 IH-1-07
34
?dt^llit
roxic
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
-li>_ UV.
SURV
100.0
100.6
107.4
84.0
79.0
117.9
96.3
85.7
113.4
104.9
95.1
103.3
116.4
122.4
111.9
8.6
100.0
70.2
90.3
138.8
100.0
96.7
109.9
100.0
100.0
100.0
100.0
105.0
102.7
102.2
38.0
104.5
47.9
95.1
62.8
JUCL-L I
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
GROW
ND
12
11
10
11
11
11
ND
11
11
13
11
11
12
10
ND
10
75
10
11
10
10
11
10
10
10
10
10
12
11
97
10
10
11
87
-ny / y
TOXG
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX 51.4 TX ND ND
NOT 67.8 NT 10 NT
TOX
TOX
TOX
TOX
TOX
18.7 TX
52
TX
2.0 TX ND ND
2.7 TX ND ND
0.0 TX ND ND
0.0 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
35
CONC
0.2
0.3
0.3
0.3
0.4
0.4
0.4
0.4
0.4
0.4
0.4
0.4
0.4
0.5
0.5
0.5
0.5
0.6
0.6
0.6
0.7
0.7
0.7
0.7
0.7
0.7
0.7
0.7
0.7
0.8
0.8
0.9
1.3
1.9
1.9
2.5
2.5
2.5
2.5
2.5
2.5
3.9
6.8
13.2
18.8
24.4
24.4
27.3
350.0
WUMU
EFFECT
NC
NE
NC
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
*
NE
NE
**
* *
**
**
ULI£i=JU^
RATIO
0.2
0.3
1.0
.
.
.
.
.
.
.
.
.
.
.
,
.
.
.
0.6
3.7
19.7
.
40.7
40.7
522.4
i until
SITE
2
2
2
3
7
7
7
7
7
7
7
7
8
8
8
8
8
4
3
1
8
2
8
4
2
3
4
4
1
.
4
2
1
3
1
1
i-unromium rasi-UKJ.^ s/im.
SAMPLE
BR-1-08
BR-1-09
BR-1-07
SR-1-10
MR-l-CO
MR-1-25
MR-1-19
MR-1-17
MR-1-11
MR-1-07
MR-1-02
MR-1-01
ERL-15% EFFECT
CF-1-03
CF-1-01
TEL-SR(ERL*NERM)
CF-1-04
CF-1-06
NERM-50% NO EFFECT
CF-1-02
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
GL-NERM-50% NO EFFECT
CF-1-05
SR-3-01
BR-1-03
SR-1-03
NERH-85% NO EFFECT
SR-3-02
GL-TEL-SR(ERL*NERM)
SR-3-06
GL-NERH-85% NO EFFECT
IH-1-06
GL-ERL-15% EFFECT
SR-3-08
BR-1-01
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
IH-1-03
ERM-50% EFFECT
SR-1-06
GL-ERM-50% EFFECT
IH-1-04
IH-1-07
HJL ewe
'OXIC
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
auei.
SU
38
105
47
90
100
138
111
122
70
116
113
117
84
95
109
107
79
100
100
100
100
100
96
96
62
104
100
103
0
95
67
U1NJ.
RV
.0
.0
.9
.3
.0
.8
.9
.4
.2
.4
.4
.9
.0
.1
.9
.4
.0
.0
.0
.0
.0
.0
.3
.7
.8
.5
.6
.3
.0
.1
.8
1O-U*
TOXS
TX
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
i/ i --
GROW
97
10
10
10
10
11
10
12
75
11
11
11
10
13
11
11
11
10
10
10
10
10
11
10
87
10
12
11
ND
11
10
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
ND
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX 2.7 TX ND ND ND ND
TOX 18.7 TX 52 TX ND ND
TOX 2.0 TX ND ND ND ND
TOX 0.0 TX ND ND ND ND
-------
CONC EFFEC
416.
572.
676.
780.
780.
1248.
1300.
1352.
1352.
1352.
1352.
1650.
1650.
1650.
1650.
1650.
1650.
1650.
1820.
2184.
2184.
2184.
3328.
4499.
4499.
6059.
6059.
14975.
14975.
14975.
21682.
22254.
22254.
22254.
41077.
60315.
259668.
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
6
6
6
6
0
0
0
0
0
0
0
0
0
0
NE
NE
NC
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
* *
* *
* if
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chromium TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=ng/g
3 SR-1-10
4 SR-3-02
0.4 2 BR-1-08
4 SR-3-06
0.6 4 SR-3-05
0.8 2 BR-1-07
0.8 2 BR-1-09
4 SR-3-24
4 SR-3-16
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
3 SR-1-03
4 SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
2.0 2 BR-1-03
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM'NERH)
9.1 2 BR-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
16.7 3 SR-1-06
13.5 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
24.9 1 IH-1-03
36.6 1 IH-1-06
157.4 1 IH-1-07
36
acuxutciit. a
'OXIC SURV
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
101
105
113
111
104
86
83
113
111
100
100
100
100
100
115
110
.6
.9
.7
.8
.5
.4
.4
.3
.8
.0
.0
.0
.0
.0
.6
.4
trill ur
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
n j. 10— i
GROW
10
10
85
94
94
85
90
10
10
ND
10
10
10
10
95
10
jy/y -
TOXG
NT
NT
TX
NT
NT
TX
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
MATURE
33
51
22
74
22
0.
0.
14
16
ND
10
10
10
10
23
61
TOXM
NT
NT
TX
NT
TX
TX
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
TOX
77.3 TX
85
TOX 100.0 NT 85
TX
TX
68
0.
NT
TX
TOX
TOX
TOX
TOX
TOX
12.
0,
1.
1,
0,
,5
.0
.4
.4
.0
TX
TX
TX
TX
TX
87
ND
96
68
ND
NT
ND
NT
NT
ND
0.
ND
0.
0.
ND
NT
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chromium TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
37
16900.0
17400.0
18800.0
22800.0
23500.0
24700.0
26000.0
29500.0
34000.0
34800.0
37300.0
38500.0
40000.0
41000.0
42000.0
47916.6
52000.0
52000.0
52000.0
52000.0
52000.0
52000.0
52300.0
53963.0
56000.0
56000.0
56000.0
58000.0
58500.0
59000.0
59000.0
70000.0
81000.0
90000.0
90000.0
92000.0
95000.0
95000.0
95000.0
110000.0
113000.0
130921.7
131480.0
160000.0
260000.0
270000.0
274000.0
280000.0
293000.0
293000.0
312000.0
319000.0
370000.0
407000.0
572000.0
1132000.0
2610000.0
NE
NE
NE
NE
NE
NE
NE
NC
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
NE
SG
NE
*
* *
**
* *
* *
* *
* *
* *
.
.
0.7
.
1.5
.
1.1
.
.
1.3
.
.
1.8
.
.
.
.
2.2
.
10.3
.
6.0
5.3
7.8
11.0
21.8
50.2
9
9
9
9
5
4
5
4
4
5
3
4
9
4
3
1
2
2
4
4
2
3
2
4
.
2
5
2
3
1
1
1
1
TR-1-01
TR-1-03
TR-1-04
TR-1-02
WH-l-CO
SR-3-02
— slcl—
WH-l-RE
SR-3-05
SR-3-06
— telf—
WH-1-01
SR-1-10
NERM-50% NO EFFECT
SR-3-01
TEL-SR(ERL*NERM)
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
GL-NERM-50% NO EFFECT
— telm —
GL-TEL-SR (ERL*NERM)
BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-16
NERH-85% NO EFFECT
SR-3-24
GL-NERH-85% NO EFFECT
BR-1-08
— erl—
SR-1-03
— pelf—
BR-1-07
SR-3-08
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— Slc2 —
BR-1-03
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— pelm —
— aet3 —
— aetl —
WH-1-02
— aetS —
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-01
SR-1-06
— erm —
IH-1-04
IH-1-03
IH-1-06
IH-1-07
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
100.0
87.5
93.4
100.0
100.0
105.9
100.0
104.5
111.8
35.0
101.6
.
116.2
100.0
100.0
100.0
100.0
100.0
.
83.4
.
111.8
113.3
113.7
115.6
86.4
110.4
77.3
.
40.0
.
.
.
100.0
12.5
.
0.0
1.4
1.4
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
TX
ND
ND
ND
ND
10
10
14
94
94
13
10
10
ND
10
10
10
10
90
10
10
85
95
85
10
85
11
85
87
ND
96
68
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
TX
NT
TX
NT
ND
NT
NT
ND
ND
ND
ND
ND
ND
51
ND
22
74
ND
33
12
ND
10
10
10
10
0.
16
14
22
23
0.
61
68
ND
0.
0.
ND
0.
0.
ND
ND
ND
ND
ND
ND
NT
ND
TX
NT
ND
NT
NT
ND
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
ND
TX
NT
ND
NT
NT
ND
-------
CONC EFFEC
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
1.
1.
1.
2.
2.
2.
2.
2.
2.
2.
3.
5.
13.
13.
13.
24.
27.
350.
2
3
3
3
7
7
7
7
7
7
7
7
7
8
9
9
3
3
9
9
5
5
5
5
5
5
5
4
0
2
2
2
4
3
0
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
NE
*
* *
* *
* *
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chromium TEST=HA14 SAMPTYP=porewater UNITS=ug/l
0.3 2 BR-1-08
0.4 2 BR-1-09
0.4 2 BR-1-07
3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
4 SR-3-01
1.0 2 BR-1-03
3 SR-1-03
4 SR-3-02
NERH-85% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-06
GL-NERH-85% NO EFFECT
3.7 1 IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-08
3.7 2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM'NERH)
GL-PEL-SR (ERM*NERH)
19.7 1 IH-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
40.7 3 SR-1-06
40.7 1 IH-1-04
522.4 1 IH-1-07
38
'U.L ewa LC.L U«.L
'OXIC SURV
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
113
83
86
101
100
100
100
100
100
116
77
115
105
.7
.4
.4
.6
.0
.0
.0
.0
.0
.2
.3
.6
.9
J.O — Ut
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
j/ J. -•
GROW
85
90
85
10
ND
10
10
10
10
10
85
95
10
TOXG
TX
TX
TX
NT
ND
NT
NT
NT
NT
NT
TX
NT
NT
MATURE TOXM
22
0.
0.
33
ND
10
10
10
10
12
68
23
51
TX
TX
TX
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NOT 111.8 NT 94 NT
TOX 1.4 TX 68 NT
NOT 110.4 NT 10
TOX 100.0 NT 85
NT
TX
TOX
1.4 TX 96 NT
TOX 12.5 TX
TOX 0.0 TX
TOX 0.0 TX
87 NT
ND ND
ND ND
74
0.
61
0.
0.
0.
ND
ND
NT
NT
NT
TX
NT
NT
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
39
INUl'H^VU.Cj— J
CONC EFFECT
416
572
676
780
780
990
1248
1300
1300
1325
1352
1352
1352
1650
1650
1650
1650
1650
1650
1650
1650
1720
1732
1820
1820
1960
2184
2184
2210
2370
2580
2620
2800
2800
2900
3010
3050
3052
3328
3328
3860
4450
4450
5499
6180
14975
18328
21682
22254
41077
60315
259668
.0
.0
.0
.0
.0
.0
.0
.0
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.0
.3
.0
.0
.5
.0
.0
.0
.0
.0
NC
NE
NE
NE
NE
NC
SG
SG
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
NE
NE
NC
NE
SG
SG
NE
SG
SG
NE
*
NE
NE
*
**
**
**
**
* *
**
u *± i,n£ii*i— i— U.A. u
RATIO SITE
0.
0,
1.
1.
0,
1.
0.
1.
1.
1
1.
2.
2,
12.
13.
13.
24.
36,
157.
.3
.4
.1
.1
.6
.1
.9
.1
.1
.2
.3
.9
.0
.9
.1
.5
.9
.6
.4
3
4
2
4
4
7
2
2
4
4
9
4
3
1
8
2
.
8
3
7
4
7
8
7
7
7
7
7
8
2
8
8
.
8
2
3
1
1
1
1
UU.LUU j.£ik3 j.— nA^o o/Min nr— jji
SAMPLE
SR-1-10
SR-3-02
BR-1-08
SR-3-06
SR-3-05
MR-1-01
BR-1-07
BR-1-09
GL-ERL-15% EFFECT
GL-TEL- SR ( ERL*NERM)
SR-3-24
SR-3-16
GL-NERM-50% NO EFFECT
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
CF-1-03
TEL-SR (ERL*NERM)
SR-1-03
ERL-15% EFFECT
MR-l-CO
SR-3-08
GL-NEC-MAX NO EFFECT
MR-1-19
CF-1-06
MR-1-02
MR-1-17
MR-1-25
NERH-85% NO EFFECT
MR-1-07
MR-1-11
CF-1-02
PEL-SR(ERM*NERH)
BR-1-03
ERM-50% EFFECT
CF-1-04
CF-1-05
NEC-MAX NO EFFECT
GL-PEL-SR (ERM*NERH)
CF-1-01
BR-1-01
GL-ERM-50% EFFECT
SR-1-06
IH-1-04
IH-1-03
IH-1-06
IH-1-07
£9t=UJLJUejJU t>
?OXIC SURV
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
100
103
97
100
96
108
80
88
102
96
100
100
100
100
100
100
123
96
100
88
114
120
109
115
109
91
90
102
79
128
114
64
89
10
0
1
1
0
.0
.8
.4
.0
.1
.1
.3
.2
.6
.1
.0
.0
.0
.0
.0
.0
.0
.2
.0
.3
.0
.3
.3
.1
.3
.9
.7
.7
.0
.4
.9
.9
.5
.3
.0
.4
.4
.0
*SJU Ul
TOXS
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
TX
TX
TX
TX
TX
* J. JL O— 1
GROW
97
10
10
92
94
79
85
92
10
10
ND
10
10
10
10
10
82
91
10
92
89
10
92
92
95
91
58
94
85
10
98
73
96
60
ND
96
68
ND
iy/U
TOXG
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
TX
NT
TX
TX
NT
TX
NT
NT
TX
NT
TX
ND
NT
NT
ND
MATURE TOXM
10
10
10
96
11
68
10
10
10
95
ND
10
10
10
10
10
93
10
10
95
63
90
95
65
12
31
24
48
10
80
77
25
10
37
ND
0.
0.
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
TX
ND
NT
NT
ND
-------
CONC EFFE(
3000
12000
15000
15000
16900
17400
18400
18800
22000
22800
23500
24700
24800
26000
27300
27500
27800
27900
29200
29500
30300
31600
31600
31800
34000
34200
34200
34200
34500
34800
35000
35300
35500
36286
37300
38500
38500
38600
38900
39300
40000
40600
41000
42000
43000
45300
52000
52000
52000
52000
52000
52000
52000
52300
56000
58000
59000
59000
60800
68410
70000
81000
90000
90000
90000
92000
95000
95000
95000
110000
113000
119365
135676
160000
260000
270000
274000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.4
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.0
.0
.0
.0
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
NE
NC
NC
NC
SG
NE
NE
NC
NC
NE
NE
NE
*
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
SG
SG
NE
SG
**
APPENDIX 4a: ASCENDING DATA T^LES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES K.,S AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chromium TEST=HA28 SAMPTYP=t>ottom sediment - total UNITS=ng/g
40
0.2
0.9
0.8
0.7
0.8
1.0
0.9
0.9
0.9
1.5
1.0
0.8
2.5
0.9
11 TB
11 TB
UM
TB
TR
TR
UM
TR
6
11
9
9
6
9
11 TB
9 TR
5 WH
4 SR
8 CF-
1-01
l-RE
l-CO
1-02
1-01
1-03
l-RE
1-04
1-04
1-02
l-CO
3-02
1-06
8 CF-1-03
10 MB-l-RE
8 CF-1-02
7 MR-1-01
8 CF-1-05
5 WH-l-RE
6 UM-1-02
7 MR-1-02
10 MB-1-04
10 MB-1-03
4 SR-3-05
6 UM-1-03
10 MB-1-02
NERM-50% NO EFFECT
8 CF-1-01
4 SR-3-06
7 MR-1-07
7 MR-1-17
7 MR-1-19
TEL-SR(ERL*NERM)
— telf—
5 WH-1-01
ERL-15% EFFECT
10 MB-1-01
7 MR-l-CO
7 MR-1-11
3 SR-1-10
7 MR-1-25
8 CF-l-CO
4 SR-3-01
11 TB-1-03
8 CF-1-04
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERM-50% NO EFFECT
— telm —
2 BR-1-09
4 SR-3-16
4 SR-3-24
GL-NERH-85% NO EFFECT
6 UM-1-01
GL-TEL-SR (ERL*NERM)
2 BR-1-08
~erl—
1.7 3 SR-1-03
GL-ERL-15% EFFECT
—pelf—
1.5 2 BR-1-07
4 SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
~~slc2~~
1.9 2 BR-1-03
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM'NERH)
— pelm —
— aet3 —
~~aetl~~
10.3 5 WH-1-02
>^VAiii«
X3XIC
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
;ti\_ u*.
SURV
0.0
100.0
100.0
11.4
81.4
98.6
86.5
82.9
93.2
100.0
100.0
103.8
120.3
123.0
100.0
102.7
108.1
114.9
109.5
117.9
109.3
95.5
95.5
96.1
114.9
97.0
64.9
100.0
91.9
115.1
114.0
71.7
7s!s
100.0
90.7
100.0
109.3
100.0
97.4
52.3
128.4
100.0
100.0
100.0
100.0
100.0
88.2
96.1
102.6
119.3
97.4
96.2
80.3
88.3
JUO.J. I
TOXS
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
JIM J. 1 O
GROW
ND
10
ND
72
ND
ND
ND
ND
10
ND
10
10
10
82
ND
94
79
98
11
ND
92
ND
ND
94
ND
ND
73
92
91
92
89
91
ND
10
58
97
95
10
94
97
10
ND
10
10
10
10
92
10
10
ND
10
91
85
92
-UH / u
TOXG
ND
NT
ND
TX
ND
ND
ND
ND
NT
ND
NT
NT
NT
TX
ND
NT
TX
NT
NT
ND
TX
ND
ND
NT
ND
ND
TX
NT
TX
TX
TX
NT
ND
NT
TX
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
TX
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
90
93
ND
48
68
77
ND
ND
95
ND
ND
11
ND
ND
25
96
31
65
63
ND
ND
10
24
10
12
10
11
ND
80
ND
10
10
10
10
10
95
10
ND .
10
10
10
95
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
ND
NT
NT
NT
ND
ND
NT
ND
ND
NT
ND
ND
TX
NT
TX
NT
NT
ND
ND
NT
TX
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
TOX
TOX
79.0 TX
85
TX
36.5 TX 74 TX
10
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=304 CHEM=Chroiniuin TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE C
41
274000
280000
312000
312000
319000
370000
407000
572000
1132000
2610000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
* *
**
**
**
**
**
5
6
7
11
21
50
,
.
.1
.1
.8
.0
.8
.2
2
3
1
1
1
1
ERM-50% EFFECT
— aet5 —
BR-1-01
GL-ERM-50% EFFECT
SR-1-06
— erm —
IH-1-04
IH-1-03
IH-1-06
IH-1-07
TOX
TOX
TOX
TOX
TOX
TOX
i sea.une.nt. -
'OXIC SURV
TOX
TOX
TOX
TOX
TOX
TOX
89.
10.
0.
1.
1.
0.
.5
,3
.0
A
.4
.0
tOCdJ
TOXS
TX
TX
TX
TX
TX
TX
L U1MXJ
GROW
96
60
ND
96
68
ND
LO=ng/
TOXG
NT
TX
ND
NT
NT
ND
g
MATURE
10
37
ND
0.
0.
ND
TOXM
NT
TX
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 42
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=304 CHEM=Chromium TEST=HA28 SAMPTYP=porewater UNITS=ug/l
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.2 NE . 2 BR-1-08 NOT 97.4 NT 10 NT 10 NT
0.3 NC 0.6 2 BR-1-09 TOX 88.2 TX 92 NT 10 NT
0.3 NC 0.7 2 BR-1-07 TOX 80.3 TX 85 TX 10 NT
0.3 NC 0.5 3 SR-1-10 TOX 100.0 NT 97 TX 10 NT
0.4 NE . 7 MR-l-CO NOT 100.0 NT 10 NT 10 NT
0.4 NE .7 MR-1-25 NOT 109.3 NT 95 NT 12 NT
0.4 NG 1.0 7 MR-1-19 TOX 114.0 NT 89 TX 63 NT
0.4 NG 1.0 7 MR-1-17 TOX 115.1 NT 92 TX 65 NT
0.4 NG 1.0 7 MR-1-11 TOX 90.7 NT 58 TX 24 TX
0.4 NG 1.0 7 MR-1-07 TOX 91.9 TX 91 TX 31 TX
0.4 NG 1.0 7 MR-1-02 TOX 109.3 NT 92 TX 95 NT
0.4 NG 1.0 7 MR-1-01 TOX 108.1 NT 79 TX 68 NT
0.5 NC 0.8 8 CF-1-03 TOX 123.0 NT 82 TX 93 NT
0.5 NC 0.8 8 CF-1-01 TOX 64.9 TX 73 TX 25 TX
0.5 . . NERM-50% NO EFFECT
0.5 NE . 8 CF-1-04 NOT 128.4 NT 10 NT 80 NT
0.6 NE . 8 CF-1-06 NOT 120.3 NT 10 NT 90 NT
0.6 NE . 8 CF-1-02 NOT 102.7 NT 94 NT 48 NT
0.6 . TEL-SR(ERL*NERM) @
0.7 NE . 9 TR-l-CO NOT 100.0 NT ND ND ND ND
0.7 NE . 4 SR-3-CO NOT 100.0 NT 10 NT 10 NT
0.7 NE . 3 SR-l-CO NOT 100.0 NT 10 NT 10 NT
0.7 NE . 1 IH-l-CO NOT 100.0 NT 10 NT 10 NT
0.7 NE . 8 CF-l-CO NOT 100.0 NT 10 NT 10 NT
0.7 NE . 2 BR-l-CO NOT 100.0 NT 10 NT 10 NT
0.7 . . GL-NERM-50% NO EFFECT
0.7 NE . 8 CF-1-05 NOT 114.9 NT 98 NT 77 NT
0.7 . . NERH-85% NO EFFECT
0.7 NE . 4 SR-3-01 NOT 97.4 NT 94 NT 11 NT
0.7 SG 1.6 2 BR-1-03 TOX 79.0 TX 85 TX 10 NT
0.7 . . GL-TEL-SR(ERL*NERM)
0.8 SG 1.2 3 SR-1-03 TOX 96.2 NT 91 TX 10 NT
0.8 . GL-ERL-15% EFFECT
0.8 . . ERL-15% EFFECT
0.9 NE . 4 SR-3-02 NOT 103.8 NT 10 NT 10 NT
1.9 NE . 4 SR-3-06 NOT 100.0 NT 92 NT 96 NT
1.9 . . GL-NERH-85% NO EFFECT
2.3 . . PEL-SR(ERM*NERH)
2.5 * 3.7 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
2.5 NE . 4 SR-3-08 NOT 88.3 NT 92 NT 95 NT
2.5 ** 5.7 2 BR-1-01 TOX 89.5 TX 96 NT 10 NT
2.5 . NEC-MAX NO EFFECT
2.5 . . GL-NEC-MAX NO EFFECT
3.9 . GL-PEL-SR (ERM*NERH)
7.9 . . GL-ERM-50% EFFECT
7.9 . ERM-50% EFFECT
13.2 ** 19.7 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
24.4 ** 36.4 3 SR-1-06 TOX 10.3 TX 60 TX 37 TX
27.3 ** 40.7 1 IH-1-04 TOX 0.0 TX ND ND ND ND
350.0 ** 522.4 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
43
NUMCODE=305 CHEM=Copper TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
ONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
9500.0
10400.0
16000.0
16000.0
16000.0
18300.0
18700.0
19000.0
19000.0
19000.0
19000.0
19500.0
20300.0
24000.0
26500.0
28550.0
29900.0
32800.0
33100.0
34000.0
35700.0
41300.0
45600.0
47150.0
48700.0
49000.0
49800.0
51900.0
52488.8
53350.0
54800.0
67000.0
67453 .5
96500.0
96500.0
96500.0
99882.2
108000.0
110000.0
128000.0
148000.0
148000.0
182000.0
187000.0
187000.0
197000.0
206500.0
226000.0
266000.0
270000.0
287000.0
291327.1
364000.0
379000.0
390000.0
390000.0
410000.0
411000.0
411000.0
459000.0
478000.0
480000.0
530000.0
583000.0
840000.0
878000.0
1300000.0
7820000.0
7820000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NC
**
NE
NE
**
**
**
NE
**
NE
**
NE
NE
NE
NE
NE
NE
*
NE
2.0
.
.
0.7
0.7
1.0
9.7
.
9.6
6.7
11.9
.
.
15.1
.
.
19.9
t
3.1
.
5
5
3
8
4
4
3
1
2
5
4
4
8
7
7
4
.
2
2
2
3
4
4
4
2
5
,
8
2
.
1
3
1
7
1
.
7
1
.
7
7
7
8
8
8
7
8
WH-l-RE
WH-l-CO
SR-1-10
CF-1-06
— slcl —
SR-3-06
— telm —
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
WH-1-01
SR-3-01
SR-3-02
CF-l-CO
GL-NERM-50% NO EFFECT
MR-1-01
MR-l-CO
SR-3-05
— erl—
— telf—
BR-1-09
BR-1-08
NERM-50% NO EFFECT
BR-1-07
SR-1-03
SR-3-24
SR-3-16
GL-TEL-SR (ERL'NERM)
GL-NERH-85% NO EFFECT
SR-3-08
BR-1-03
TEL-SR(ERL*NERM)
WH-1-02
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-PEL-SR (ERM*NERH)
— pelm —
— slc2—
CF-1-05
BR-1-01
GL-NEC-MAX NO EFFECT
IH-1-04
SR-1-06
GL-ERM-50% EFFECT
— pelf—
ERM-50% EFFECT
IH-1-03
MR-1-02
— erm —
IH-1-07
PEL-SR(ERM*NERH) @
MR-1-19
IH-1-06
— aet4—
— aet2 —
MR-1-25
MR-1-07
NERH-85% NO EFFECT
MR-1-17
CF-1-04
CF-1-03
— aet3 —
CF-1-02
— aet5 —
MR-1-11
— aetl —
CF-1-01
NEC -MAX NO EFFECT @
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
85.7
100.0
90.3
107.4
103.3
100.0
100.0
100.0
100.0
8.6
96.7
100.6
100.0
117.9
100.0
104.9
105.0
38.0
47.9
104.5
102.2
102.7
.
.
95.1
62.8
.
51.4
.
.
.
.
.
96.3
67.8
.
2.0
18.7
.
.
.
2.7
113.4
0.0
111.9
0.0
138.8
116.4
122.4
109.9
84.0
.
79.0
.
70.2
95.1
.
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
10
11
11
10
10
10
10
ND
10
12
10
11
10
11
"10
97
10
10
11
12
11
87
ND
11
10
ND
52
ND
11
ND
10
ND
11
11
12
11
10
11
75
13
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
ND
TX
ND
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC 1
0.6
1.1
1.3
1.5
1.7
1.7
1.9
2.3
2.6
2.7
2.7
3.0
3.0
3.3
3.7
3.8
4.7
4.7
4.7
4.7
4.7
4.7
4.7
4.7
5.0
5.3
5.3
5.3
5.4
8.7
8.8
9.5
9.6
14.8
15.1
15.1
16.4
17.6
19.1
19.8
19.8
20.6
21.4
35.6
79.4
89.9
102.0
102.0
126.3
3FFEC
NE
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
**
* *
* *
NE
NE
* *
NE
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=305 CHEM=Copper TEST=CR14 SAMPTYP=porewater UNITS=ug/l
44
0.4
0.5
0.5
.
.
.
.
1.1
r
4.1
7.6
.
4.6
,
4.1
!7.0
3
4
2
8
2
2
7
2
3
4
4
4
2
7
4
3
1
8
2
.
.
.
1
.
.
7
8
8
7
.
7
7
8
1
3
.
1
8
8
7
7
1
SR-1-03
SR-3-02
BR-1-03
CF-1-06
BR-1-08
BR-1-07
MR-1-01
BR-1-09
SR-1-10
SR-3-01
GL-NERM-50% NO EFFECT
SR-3-08
SR-3-06
BR-1-01
MR-1-02
GL-TEL-SR (ERL*NERM)
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
GL -NEC -MAX NO EFFECT
TEL-SR(ERL*NERM)
IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
MR-l-CO
CF-1-05
CF-1-04
MR-1-07
GL-PEL-SR(ERM*NERH)
MR-1-17
MR-1-25
NERH-85% NO EFFECT
CF-1-03
PEL-SR(ERM*NERH)
IH-1-04
SR-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-03
CF-1-02
CF-1-01
MR-1-11
MR-1-19
NEC-MAX NO EFFECT
IH-1-07
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
104.
100.
62.
107.
38.
47.
117.
105.
90.
96.
95.
103.
67.
113.
100.
100.
100.
100.
100.
.
0.
.
.
100.
96.
109.
116.
122.
138.
84.
.
2.
18.
.
2.
79.
95.
70.
111.
.
0.
5
6
8
4
0
9
9
0
3
7
1
3
8
4
0
0
0
0
0
0
0
3
9
4
4
8
0
0
7
7
0
1
2
9
0
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
NT
TX
10
12
87
11
97
10
11
10
10
10
11
11
10
11
10
10
10
10
10
ND
10
11
11
11
12
11
10
ND
52
ND
11
13
75
10
ND
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
TX
ND
NT
NT
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
IMUWl-UI^C,-
CONC EFFEC
8800
9500
9600
10200
10400
10400
16000
16000
18300
18700
19000
19000
19000
19000
19000
19000
19000
19500
20300
24000
28012
28012
33100
34000
35700
41300
41300
41300
45600
48700
49000
49400
49800
49800
51900
54800
54800
54800
67000
77712
78026
96500
108000
110000
122250
122250
148000
182000
187000
197000
226000
270000
287000
379000
390000
390000
530000
840000
1300000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.5
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NC
*
*
*
NE
NE
NE
NE
*
* *
* *
* *
* *
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=305 CHEM=Copper TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
45
2
1
2
2
2
3
9
7
9
6
11
15
19
.
.
.
.
.
.0
.
.
.0
.
.
.2
.
.4
.6
.
.
.
.
.
.5
.7
.
.8
.6
.7
.
.9
.1
.9
.
.
9
5
9
9
5
9
3
4
9
4
3
1
2
5
4
4
4
2
2
2
3
t
4
4
4
2
5
2
1
3
1
1
1
.
TR-1-03
WH-l-RE
TR-1-04
TR-1-01
WH-l-CO
TR-1-02
SR-1-10
— slcl—
SR-3-06
— telm —
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
WH-1-01
SR-3-01
SR-3-02
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
SR-3-05
— erl—
—telf—
BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-08
BR-1-07
SR-1-03
NERH-85% NO EFFECT
SR-3-24
GL-NERH-85% NO EFFECT
SR-3-16
SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
BR-1-03
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
WH-1-02
— pelm —
— slc2 —
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-01
IH-1-04
SR-1-06
— pelf—
IH-1-03
— erm —
IH-1-07
IH-1-06
— aet4 —
— aet2 —
— aet3 —
— aetS —
— aetl— -
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
87
100
93
100
100
100
101
111
100
100
100
100
100
35
116
105
104
83
113
86
115
113
111
110
77
40
100
0
12
1
0
1
.5
.0
.4
.0
.0
.0
.6
.
.8
.0
.0
.0
.0
.0
.0
.2
.9
.5
.4
.7
.4
.6
.3
.8
.4
.3
.0
.0
.0
.5
.4
.0
.4
.
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
'NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
TX
ND
14
ND
ND
10
ND
10
94
ND
10
10
10
10
13
10
10
94
90
85
85
95
10
10
10
85
11
85
ND
87
96
ND
68
ND
NT
ND
ND
NT
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
TX
ND
NT
NT
ND
NT
ND
ND
ND
ND
ND
ND
33
74
ND
10
10
10
10
ND
12
51
22
0.
22
0.
23
14
16
61
68
ND
0.
ND
0.
0.
ND
0.
ND
ND
ND
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
ND
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
ND
TX
ND
NT
NT
ND
NT
-------
CONG I
0.6
1.1
1.3
1.7
1.7
2.3
2.6
2.7
2.7
2.9
3.0
3.0
3.3
3.8
3.9
4.7
4.7
4.7
4.7
4.7
4.7
4.7
4.7
4.7
5.3
5.3
5.3
9.6
9.6
19.1
19.8
19.8
19.8
21.4
126.3
SFFE<
NE
NE
NC
NC
NC
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
**
**
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=305 CHEM=Copper TEST=HA14 SAMPTYP=porewater
46
0.3
0.4
0.4
0.5
0.7
3 SR-1-03
4 SR-3-02
2 BR-1-03
2 BR-1-08
2 BR-1-07
2 BR-1-09
3 SR-1-10
4 SR-3-01
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
4 SR-3-08
4 SR-3-06
2 BR-1-01
GL-TEL-SR (ERL*NERM)
TEL-SR (ERL*NERM)
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
NEC -MAX NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
1.1 1 IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
4.1 1 IH-1-04
7.6 3 SR-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
1 IH-1-03
1 IH-1-07
>x.eweii
'OXIC
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
-er uiNj.j
SURV
115.6
105.9
77.3
113.7
86.4
83.4
101.6
116.2
110.4
111.8
100.0
100.0
100.0
100.0
100.0
100.0
is-ug/
TOXS
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
r j.
GROW
95
10
85
85
85
90
10
10
10
94
85
ND
10
10
10
10
TOXG
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
MATURE
23
51
68
22
0.
0.
33
12
61
74
0.
ND
10
10
10
10
TOXM
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
TOX
1.4 TX 68
4.6
27.0
TOX 0.0 TX ND
TOX 12.5 TX 87
TOX 1.4 TX 96
TOX 0.0 TX ND
NT
ND
NT
NT
ND
0.
NT
ND ND
0. NT
0. NT
ND ND
-------
iN
CON
890.
1017.
1144.
1334.
1843.
1843.
2224.
2796.
2923.
2986.
3050.
3177.
3939.
4384.
5042.
5700.
6989.
9248.
10600.
12000.
12000.
12000.
12000.
12000.
12000.
12000.
12000.
15694.
16965.
16965.
17791.
50079.
77000.
141000.
178000.
185000.
209000.
233000.
251000.
287000.
325000.
325000.
354000.
607000.
6971000.
Una.
C I
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
7
0
0
0
0
0
0
0
0
0
0
0
0
0
9
0
0
0
0
0
0
0
0
0
0
0
0
0
,\JUCt-
SFFEC
NC
NE
NC
NE
NE
NC
NE
NE
NE
NC
NE
NC
NC
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
NE
SG
NE
*
*
NE
*
NE
*
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect j NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=305 CHEM=Copper TEST=HA28 SAMPTYP=bottom sediment - sem UNITS=ng/g
GL-SECs NOT REPORTED
0.1 3 SR-1-10
4 SR-3-06
0.1 3 SR-1-06
4 SR-3-02
4 SR-3-05
0.3 2 BR-1-09
2 BR-1-08
4 SR-3-24
4 SR-3-16
0.4 2 BR-1-07
4 SR-3-08
0.3 3 SR-1-03
0.6 2 BR-1-01
0.6 2 BR-1-03
NERM-50% NO EFFECT
7 MR-l-CO
0.6 1 IH-1-06
TEL-SR(ERL*NERM)
0.1 7 MR-1-01
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
NERH-85% NO EFFECT
1.3 1 IH-1-04
1.4 1 IH-1-07
ERL-15% EFFECT
1.5 1 IH-1-03
PEL-SR(ERM*NERH)
8 CF-1-05
1.5 7 MR-1-02
7 MR-1-25
2.0 7 MR-1-17
ERM-50% EFFECT
2.5 7 MR-1-07
8 CF-1-04
2.1 8 CF-1-03
8 CF-1-02
NEC-MAX NO EFFECT
3.9 7 MR-1-19
6.6 7 MR-1-11
51.5 8 CF-1-01
47
sediment - se
?oxic SURV
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
100
100
10
103
96
88
97
102
96
80
88
96
89
79
100
1
108
100
100
100
100
100
120
100
0
0
1
114
109
109
115
91
128
123
102
114
90
64
.0
.0
.3
.8
.1
.2
.4
.6
.1
.3
.3
.2
.5
.0
.0
.4
.1
.0
.0
.0
.0
.0
.3
.0
.0
.0
.4
.9
.3
.3
.1
.9
.4
.0
.7
.0
.7
.9
m UJNJ
TOXS
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
LTS=nc
GROW
97
92
60
10
94
92
10
10
10
85
92
91
96
85
10
68
79
ND
10
10
10
10
10
10
ND
ND
96
98
92
95
92
91
10
82
94
89
58
73
j/g --
TOXG
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
TX
TX
NT
TX
NT
TX
TX
TX
MATURE TOXM
10
96
37
10
11
10
10
10
95
10
95
10
10
10
10
0.
68
ND
10
10
10
10
90
10
ND
ND
0.
77
95
12
65
31
80
93
48
63
24
25
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
-------
wurav
CONC I
1700.0
7300.0
8800.0
9500.0
9600.0
10200.0
10400.0
10400.0
11000.0
13000.0
16000.0
16000.0
16000.0
18000.0
18300.0
18700.0
19000.0
19000.0
19000.0
19000.0
19000.0
19000.0
19000.0
19500.0
20300.0
24000.0
26500.0
28012.5
28012.5
29900.0
32800.0
33100.0
34000.0
35700.0
41300.0
41300.0
41300.0
45600.0
48700.0
49000.0
49800.0
49800.0
51900.0
54800.0
54800.0
54800.0
67000.0
78026.0
96500.0
101230.4
108000.0
110000.0
122250.0
128000.0
148000.0
182000.0
187000.0
187000.0
197000.0
226000.0
266000.0
270000.0
287000.0
364000.0
379000.0
390000.0
390000.0
410000.0
411000.0
459000.0
478000.0
480000.0
530000.0
583000.0
583000.0
840000.0
878000.0
_uun=
3FFEC
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
NE
NE
SG
NE
SG
*
NE
NE
NE
*
**
NE
* *
* *
**
**
SG
**
SG
**
NE
SG
*
NE
SG
NE
*
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=305 CHEM=Copper TEST=HA28 SAMPTYP=bottora sediment - total UNITS=ng/g
0.2 11 TB-1-01
11 TB-l-RE
9 TR-1-03
5 WH-l-RE
9 TR-1-04
9 TR-1-01
5 WH-l-CO
9 TR-1-02
1.1 11 TB-1-02
11 TB-1-04
0.8 3 SR-1-10
8 CF-1-06
—slcl—
1.8 11 TB-1-03
4 SR-3-06
—telm—
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
2.0 5 WH-1-01
4 SR-3-01
4 SR-3-02
8 CF-l-CO
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
0.1 7 MR-1-01
7 MR-l-CO
4 SR-3-05
—erl—
—telf—
1.3 2 BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
2 BR-1-08
1.5 2 BR-1-07
2.6 3 SR-1-03
4 SR-3-24
GL-NERH-85% NO EFFECT
4 SR-3-16
4 SR-3-08
NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
2.1 2 BR-1-03
GL-PEL-SR(ERM*NERH)
9.7 5 WH-1-02
PEL-SR(ERM*NERH)
—pelm—
—slc2—
GL-ERM-50% EFFECT
8 CF-1-05
4.6 2 BR-1-01
9.6 1 IH-1-04
9.8 3 SR-1-06
ERM-50% EFFECT
—pelf--
11.9 1 IH-1-03
1.2 7 MR-1-02
—erm—
15.1 1 IH-1-07
1.6 7 MR-1-19
19.9 1 IH-1-06
—aet4—
—aet2—
7 MR-1-25
1.9 7 MR-1-07
2.1 7 MR-1-17
8 CF-1-04
1.9 8 CF-1-03
—aet3—
8 CF-1-02
NEC-MAX NO EFFECT
—aet5-~
4.0 7 MR-1-11
48
:uimenu - cou
?OXIC SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
0.
100.
98.
109.
82.
81.
100.
100.
11.
93.
100.
120.
52.
100.
100.
100.
100.
100.
100.
71.
97.
103.
100.
108.
100.
96.
88.
97.
80.
96.
102.
96.
88.
79.
36.
114.
89.
0.
10.
1.
109.
0.
114.
1.
109.
91.
115.
128.
123.
0
0
6
5
9
4
0
0
4
2
0
3
3
0
0
0
0
0
0
7
4
8
0
1
0
1
2
4
3
2
6
1
3
0
5
9
5
0
3
4
3
0
0
4
3
9
1
4
0
ax ur
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
NT
TX
NT
TX
NT
TX
NT
NT
NT
nj.rs=r
GROW
ND
10
ND
11
ND
ND
10
ND
72
10
97
10
97
92
ND
10
10
10
10
91
94
10
10
79
10
94
92
10
85
91
10
10
92
85
74
98
96
ND
60
96
92
ND
89
68
95
91
92
10
82
ig/g
TOXG MATURE
ND
NT
ND
NT
ND
ND
NT
ND
TX
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
NT
NT
ND
TX
NT
TX
ND
TX
NT
NT
TX
TX
NT
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
90
ND
96
ND
10
10
10
10
ND
11
10
10
68
10
11
10
10
10
10
10
95
95
10
ND
77
10
ND
37
0.
95
ND
63
0.
12
31
65
80
93
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
TX
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
NOT
TOX
102.7 NT 94
90.7 NT
58
NT
TX
48
24
NT
TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 49
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
1300000.0 . . —aetl—
7820000.0 ** 31.7 8 CF-1-01 TOX 64.9 TX 73 TX 25 TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 50
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=305 CHEM=Copper TEST=HA28 SAMPTYP=porewater UNITS=ug/l
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.6 NC 0.1 3 SR-1-03 TOX 96.2 NT 91 TX 10 NT
1.1 NE . 4 SR-3-02 NOT 103.8 NT 10 NT 10 NT
1.3 NC 0.4 2 BR-1-03 TOX 79.0 TX 85 TX 10 NT
1.5 NE . 8 CF-1-06 NOT 120.3 NT 10 NT 90 NT
1.7 NE . 2 BR-1-08 NOT 97.4 NT 10 NT 10 NT
1.7 NC 0.5 2 BR-1-07 TOX 80.3 TX 85 TX 10 NT
1.9 NC 0.2 7 MR-1-01 TOX 108.1 NT 79 TX 68 NT
2.3 NC 0.7 2 BR-1-09 TOX 88.2 TX 92 NT 10 NT
2.6 NC 0.6 3 SR-1-10 TOX 100.0 NT 97 TX 10 NT
2.7 . GL-NERM-50% NO EFFECT
2.7 NE . 4 SR-3-01 NOT 97.4 NT 94 NT 11 NT
3.0 . . GL-TEL-SR(ERL*NERM) @
3.0 NE . 4 SR-3-08 NOT 88.3 NT 92 NT 95 NT
3.0 NE . 4 SR-3-06 NOT 100.0 NT 92 NT 96 NT
3.3 SG 1.0 2 BR-1-01 TOX 89.5 TX 96 NT 10 NT
3.3 . . GL-ERL-15% EFFECT
3.7 NC 0.4 7 MR-1-02 TOX 109.3 NT 92 TX 95 NT
3.7 . . NERM-50% NO EFFECT
4.4 . . TEL-SR(ERL*NERM) @
4.7 NE . 9 TR-l-CO NOT 100.0 NT ND ND ND ND
4.7 NE . 4 SR-3-CO NOT 100.0 NT 10 NT 10 NT
4.7 NE . 3 SR-l-CO NOT 100.0 NT 10 NT 10 NT
4.7 NE . 1 IH-l-CO NOT 100.0 NT 10 NT 10 NT
4.7 NE . 8 CF-l-CO NOT 100.0 NT 10 NT 10 NT
4.7 NE . 2 BR-l-CO NOT 100.0 NT 10 NT 10 NT
4.7 . . GL-NERH-85% NO EFFECT
4.7 . GL-NEC-MAX NO EFFECT
5.3 SG 1.1 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
5.3 . ERL-15% EFFECT
5.4 NE . 7 MR-l-CO NOT 100.0 NT 10 NT 10 NT
8.7 NE . 8 CF-1-05 NOT 114.9 NT 98 NT 77 NT
8.8 NE . 8 CF-1-04 NOT 128.4 NT 10 NT 80 NT
8.8 . NERH-85% NO EFFECT
9.5 NC 0.9 7 MR-1-07 TOX 91.9 TX 91 TX 31 TX
9.5 . . GL-PEL-SR(ERM*NERH)
13.2 . . PEL-SR(ERM'NERH)
14.8 SG 1.4 7 MR-1-17 TOX 115.1 NT 92 TX 65 NT
15.1 NE . 7 MR-1-25 NOT 109.3 NT 95 NT 12 NT
16.4 SG 1.4 8 CF-1-03 TOX 123.0 NT 82 TX 93 NT
19.1 ** 4.1 1 IH-1-04 TOX 0.0 TX ND ND ND ND
19.5 . GL-ERM-50% EFFECT
19.8 ** 4.2 3 SR-1-06 TOX 10.3 TX 60 TX 37 TX
19.8 . . ERM-50% EFFECT
21.4 ** 4.6 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
35.6 NE . 8 CF-1-02 NOT 102.7 NT 94 NT 48 NT
35.6 . . NEC-MAX NO EFFECT
79.4 ** 6.7 8 CF-1-01 TOX 64.9 TX 73 TX 25 TX
89.9 ** 8.8 7 MR-1-11 TOX 90.7 NT 58 TX 24 TX
102.0 ** 10.0 7 MR-1-19 TOX 114.0 NT 89 TX 63 NT
126.3 ** 27.0 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
ixuiawj
CONC EFFE(
0.
0.
0.
0.
1.
1.
1.
2.
2.
2.
2.
2.
2.
2.
2.
2.
3.
3.
3.
3.
3.
3.
4.
5.
5.
5.
5.
5.
5.
6.
7.
7.
8.
8.
11.
15.
18.
18.
4
7
8
9
2
2
5
3
3
5
7
7
7
7
7
7
3
6
6
7
8
9
6
2
3
3
8
8
8
1
0
3
5
5
7
8
5
5
NE
NC
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
*
NE
NE
NE
it
It
**
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=306 CHEM=Iron TEST=CR14 SAMPTYP=bottom sediment - sem
GL-SECs NOT REPORTED
3 SR-1-10
0.3 2 BR-1-08
0.5 3 SR-1-06
2 BR-1-09
0.5 2 BR-1-07
0.5 2 BR-1-03
3 SR-1-03
8 CF-1-05
8 CF-1-06
7 MR-1-01
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
7 MR-l-CO
7 MR-1-19
2 BR-1-01
8 CF-1-03
TEL-SR(ERL*NERM)
7 MR-1-02
7 MR-1-07
7 MR-1-17
1.9 1 IH-1-04
ERL-15% EFFECT
2.1 1 IH-1-06
7 MR-1-25
NERH-85% NO EFFECT
8 CF-1-04
PEL-SR(ERM*NERH)
8 CF-1-02
3.1 1 IH-1-03
ERM-50% EFFECT
2.8 7 MR-1-11
5.8 1 IH-1-07
8 CF-1-01
NEC-MAX NO EFFECT
51
ieaiment - se
'OXIC SURV
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
90
38.
18.
105.
47.
62.
104.
96.
107.
117.
100.
100.
100.
100.
100,
100.
111.
67.
84.
113.
116.
122.
2
0.
138.
109.
79.
2,
70.
0,
95.
.3
.0
.7
.0
.9
.8
.5
.3
.4
.9
.0
.0
.0
.0
.0
.0
.9
.8
.0
.4
.4
.4
.0
.0
.8
.9
.0
.7
.2
.0
.1
:m UJM.
TOXS
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
TX
NT
LTS-^
GROW
10
97
52
10
10
87
10
11
11
11
10
10
10
10
10
10
10
10
10
11
11
12
ND
ND
11
11
11
ND
75
ND
13
TOXG
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
ND
TX
ND
NT
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
- NUMCODE=306 CHEM=Iron TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=%
52
CONC EFFECT RATIO SITE SAMPLE
0.4
0.7
0.8
0.9
1.2
1.2
1.2
1.3
1.5
2.1
2.2
2.7
2.7
2.7
2.7
2.7
2.7
2.7
2.7
2.7
3.6
3.6
3.6
4.0
4.0
5.3
5.8
5.8
5.8
8.5
15.8
NE
NC
NC
NC
NC
NC
NE
NE
NE
NE
NE
NE
SG
SG
*
*
* *
0
0
0
0
0
1
1
2
3
5
.3
.5
.3
.4
.4
.
.
.
.3
.
.
.9
.1
.1
.8
3
2
3
2
2
2
3
9
4
3
1
2
.
2
.
1
1
1
1
SR-1-10
BR-1-08
SR-1-06
BR-1-09
BR-1-07
BR-1-03
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
SR-1-03
GL-TEL-SR (ERL*NERM)
TEL-SR(ERL'NERM}
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERH-85% NO EFFECT
NEC-MAX NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
BR-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
IH-1-04
IH-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-03
IH-1-07
ad-L^Licii L, Ac
roxic SURV
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
101
113
12
83
86
77
115
100
100
100
100
100
.6
.7
.5
.4
.4
.3
.6
.0
.0
.0
.0
.0
Ml \Ji\ .
TOXS
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
no— -c
GROW
10
85
87
90
85
85
95
ND
10
10
10
10
TOXG
NT
TX
NT
TX
TX
TX
NT
ND
NT
NT
NT
NT
MATURE TOXM
33
22
0.
0.
0.
68
23
ND
10
10
10
10
NT
TX
NT
TX
TX
NT
NT
ND
NT
NT
NT
NT
TOX 100.0 NT 85 TX
TOX 0.0 TX ND ND
TOX 1.4 TX 68 NT
0.
TX
TOX
TOX
1.4 TX 96 NT
0.0 TX ND ND
ND ND
0. NT
0. NT
ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 53
INCLUDES NBS AND OTHER (--) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=306 CHEM=Iron TEST=HA28 SAMPTYP=bottom sediment - sem UNITS=%
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.4
0.7
0.8
0.9
1.2
1.2
1.2
1.5
2.1
2.3
2.3
2.5
2.7
2.7
2.7
2.7
2.7
2.7
2.7
2.7
2.7
3.3
3.6
3.6
3.6
3.7
3.8
3.9
4.0
4.6
4.6
5.2
5.2
5.3
5.7
5.8
5.8
5.8
6.1
7.1
7.3
7.3
8.5
11.7
15.8
18.5
NC
NE
NC
NC
NC
NC
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
*
NC
NC
NC
SG
SG
*
NE
NE
NE
*
*
* *
**
0
0
0
0
0
0
0
0
2
0
0
1
1
1
2
3
2
5
4
.2
.
.3
.5
.7
.7
.5
.6
.
.
.
.
.
.8
.1
.9
.9
.0
.1
.9
.
.1
.1
.5
.8
.5
3
2
3
2
2
2
3
8
8
7
9
4
3
1
8
2
7
7
2
.
8
7
7
7
1
1
7
8
.
8
1
7
1
8
SR-1-10
BR-1-08
SR-1-06
BR-1-09
BR-1-07
BR-1-03
GL-NERM-50% NO EFFECT
SR-1-03
GL-TEL-SR (ERL*NERM) @
CF-1-05
CF-1-06
MR-1-01
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT @
MR-l-CO
MR-1-19
BR-1-01
GL-ERL-15% EFFECT
CF-1-03
TEL-SR(ERL*NERM)
MR-1-02
GL-PEL-SR ( ERM*NERH )
MR-1-07
NERH-85% NO EFFECT
MR-1-17
ERL-15% EFFECT
IH-1-04
PEL-SR (ERM*NERH)
IH-1-06
GL-ERM-50% EFFECT
MR-1-25
CF-1-04
ERM-50% EFFECT
CF-1-02
NEC -MAX NO EFFECT
IH-1-03
MR-1-11
IH-1-07
CF-1-01
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
100.0
97.4
10.3
88.2
80.3
79.0
.
96.2
114.9
120.3
108.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
114.0
89.5
123.0
109.3
91.9
115.1
0.0
1.4
109.3
128.4
102.7
1.4
90.7
0.0
64.9
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
TX
NT
NT
NT
TX
NT
TX
TX
97
10
60
92
85
85
91
98
10
79
ND
10
10
10
10
10
10
89
96
82
92
91
92
ND
68
95
10
94
96
58
ND
73
TX
NT
TX
NT
TX
TX
TX
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
ND
NT
NT
NT
NT
NT
TX
ND
TX
10
10
37
10
10
10
10
77
90
68
ND
10
10
10
10
10
10
63
10
93
95
31
65
ND
0.
12
80
48
0.
24
ND
25
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
TX
ND
TX
-------
IMUnv-VUJ
CONC EFFE(
1
1
2
3
3
3
3
4
4
4
5
10
12
13
13
14
15
17
18
18
18
18
18
18
18
18
18
19
19
20
20
21
21
21
22
22
23
24
26
28
28
28
29
29
33
38
.2
.5
.0
.1
.2
.4
.7
.0
.1
.4
.5
.3
.5
.7
.9
.4
.4
.9
.0
.1
.3
.3
.3
.3
.3
.3
.8
.7
.1
.5
.6
.0
.9
.9
.3
.8
.5
.8
.6
.0
.0
.8
.0
.0
.1
.0
NC
NC
NC
NC
NC
NE
NC
NC
NC
NE
NE
NE
SG
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
SG
NC
NE
NC
NC
SG
NC
NE
NE
*
SG
NE
SG
SG
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=306 CHEM=Iron TEST=HA28 SAMPTYP=bottom sediment - total UNITS=
RATIO SITE SAMPLE C
GL-SECs NOT REPORTED
0.1 3 SR-1-10
0.1 3 SR-1-06
—slcl—
0.2 3 SR-1-03
0.2 11 TB-1-01
0.3 2 BR-1-09
2 BR-1-08
—slc2 —
0.4 2 BR-1-07
0.4 2 BR-1-03
0.5 2 BR-1-01
11 TB-l-RE
8 CF-1-06
8 CF-1-05
1.1 11 TB-1-02
0.8 1 IH-1-04
11 TB-1-04
1.0 1 IH-1-06
NERM-50% NO EFFECT
0.8 7 MR-1-02
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
TEL-SR(ERL'NERM)
1.1 1 IH-1-03
ERL-15% EFFECT
0.9 7 MR-1-19
7 MR-l-CO
0.9 7 MR-1-07
0.9 7 MR-1-01
NERH-85% NO EFFECT
1.1 8 CF-1-03
1.0 7 MR-1-17
8 CF-1-04
PEL-SR(ERM*NERH)
7 MR-1-25
2.2 11 TB-1-03
ERM-50% EFFECT
1.6 1 IH-1-07
8 CF-1-02
NEC-MAX NO EFFECT
1.4 7 MR-1-11
2.0 8 CF-1-01
54
;u.j.iuc:i
roxic
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
1U UUl
SURV
100.0
10.3
96.2
0.0
88.2
97.4
80.3
79.0
89.5
100.0
120.3
114.9
11.4
0.0
93.2
1.4
109.3
100.0
100.0
100.0
100.0
100.0
100.0
1.4
114.0
100.0
91.9
108.1
123.0
115.1
128.4
109.3
52.3
0.0
102.7
90.7
64.9
-ax ui
TOXS
NT
TX
NT
TX
TX
NT
TX
TX
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
MX 1 £> — 1
GROW
97
60
91
ND
92
10
85
85
96
10
10
98
72
ND
10
68
92
ND
10
10
10
10
10
96
89
10
91
79
82
92
10
95
97
ND
94
58
73
i -'
TOXG
TX
TX
TX
ND
NT
NT
TX
TX
NT
NT
NT
NT
TX
ND
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
NT
NT
NT
ND
NT
TX
TX
MATURE
10
37
10
ND
10
10
10
10
10
ND
90
77
ND
ND
ND
0.
95
ND
10
10
10
10
10
0.
63
10
31
68
93
65
80
12
ND
ND
48
24
25
TOXM
NT
TX
NT
ND
NT
NT
NT
NT
NT
ND
NT
NT
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
ND
NT
TX
TX
-------
CONC I
68000.0
99000.0
250000.0
293000.0
304000.0
305000.0
334000.0
373000.0
379000.0
397000.0
460000.0
473000.0
492000.0
549000.0
685000.0
685000.0
696000.0
696000.0
696000.0
696000.0
696000.0
696000.0
726000.0
726000.0
731000.0
794000.0
805000.0
819000.0
839000.0
939000.0
982000.0
982000.0
1079077.4
1100000.0
1386000.0
1538382.3
1673000.0
1673000.0
1800000.0
1844000.0
1970000.0
2410000.0
2410000.0
2420000.0
3280000.0
3389000.0
4460000.0
4460000.0
Ci — J U<
3FFEI
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
*
*
* *
NE
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=308 CHEM=Manganese TEST=CR14 SAMPTYP=bottom sediment - total
GL-SECs NOT REPORTED
8 CF-1-06
4 SR-3-06
8 CF-1-05
4 SR-3-02
4 SR-3-01
3 SR-1-10
0.6 3 SR-1-06
7 MR-1-01
4 SR-3-05
4 SR-3-08
—slcl—
7 MR-1-02
4 SR-3-16
4 SR-3-24
8 CF-1-03
0.7 2 BR-1-03
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
2 BR-1-09
0.8 2 BR-1-07
0.8 2 BR-1-08
7 MR-1-17
7 MR-1-07
3 SR-1-03
8 CF-1-04
7 MR-1-25
7 MR-1-19
NERH-85% NO EFFECT
TEL-SR(ERL*NERM)
—slc2—
2 BR-1-01
PEL-SR(ERM*NERH)
1.9 7 MR-1-11
ERL-15% EFFECT
—aet5~-
7 MR-l-CO
2.8 1 IH-1-04
3.5 1 IH-1-06
ERM-50% EFFECT
3.5 1 IH-1-03
4.7 1 IH-1-07
8 CF-1-01
8 CF-1-02
NEC-MAX NO EFFECT
55
sediment; - tc
roxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
107
103
96
100
96
90
18
117
104
95
113
102
102
84
62
100
100
100
100
100
105
47
38
122
116
104
109
138
111
67
70
100
2
0
2
0
95
79
.4
.3
.3
.6
.7
.3
.7
.9
.9
.1
.4
.7
.2
.0
.8
.0
.0
.0
.0
.0
.0
.9
.0
.4
.4
.5
.9
.8
.9
.8
.2
.0
.0
.0
.7
.0
.1
.0
itai UMj.ii
TOXS GROW
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
NT
NT
11
11
11
12
10
10
52
11
11
11
11
12
11
10
87
10
10
10
10
10
10
10
97
12
11
10
11
11
10
10
75
10
ND
ND
ND
ND
13
11
-ng/g
TOXG
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
ND
ND
NT
NT
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
i\iura»-uun=j'
CONC EFFEl
99000
293000
304000
305000
334000
379000
397000
460000
492000
492000
520500
549000
597655
614721
685000
696000
696000
696000
696000
696000
696000
696000
726000
726000
726000
726000
731000
819000
819000
819000
1080688
1080688
1100000
1386000
1678000
1678000
1800000
1970000
2410000
2420000
3280000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.4
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.7
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
SG
SG
NE
SG
*
*
*
**
> CVU J.1UCII U ~ U U
'OXIC SURV
NOT
NOT
NOT
NOT
TOX
TOX
NOT
111
105
116
101
12
104
110
.8
.9
.2
.6
.5
.5
.4
UdJ. L
TOXS
NT
NT
NT
NT
TX
NT
NT
JINX 10-
GROW
94
10
10
10
87
94
10
-ug/g
TOXG MATURE TOXM
NT
NT
NT
NT
NT
NT
NT
74
51
12
33
0.
22
61
NT
NT
NT
NT
NT
TX
NT
NOT 111.8 NT 10 NT 16 NT
NOT 113.3 NT 10 NT 14 NT
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
308 CHEM=Manganese TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
4 SR-3-06
4 SR-3-02
4 SR-3-01
3 SR-1-10
0.6 3 SR-1-06
0.9 4 SR-3-05
4 SR-3-08
—slcl—
4 SR-3-16
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
4 SR-3-24
GL-TEL-SR(ERL*NERM)
TEL-SR (ERL*NERM)
1.0 2 BR-1-03
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
1.0 2 BR-1-09
1.0 2 BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
1.1 2 BR-1-08
3 SR-1-03
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
— Slc2 —
2.0 2 BR-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
—aet5~
2.8 1 IH-1-04
3.5 1 IH-1-06
3.5 1 IH-1-03
4.7 1 IH-1-07
56
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
77
100
100
100
100
100
83
86
113
115
.3
.0
.0
.0
.0
.0
.4
.4
.7
.6
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
85
ND
10
10
10
10
90
85
85
95
TX
ND
NT
NT
NT
NT
TX
TX
TX
NT
68
ND
10
10
10
10
0.
0.
22
23
NT
ND
NT
NT
NT
NT
TX
TX
TX
NT
TOX 100.0 NT 85 TX 0. TX
TOX 0.0 TX ND ND ND ND
TOX 1.4 TX 68 NT 0. NT
TOX 1.4 TX 96 NT 0. NT
TOX 0.0 TX ND ND ND ND
-------
CONC I
29100.0
68000.0
99000.0
153000.0
194000.0
250000.0
293000.0
304000.0
305000.0
307000.0
312000.0
334000.0
373000.0
379000.0
397000.0
460000.0
473000.0
492000.0
492000.0
549000.0
549000.0
597655.4
631327.2
685000.0
685000.0
696000.0
696000.0
696000.0
696000.0
696000.0
696000.0
696000.0
726000.0
726000.0
726000.0
726000.0
731000.0
731000.0
794000.0
805000.0
819000.0
839000.0
839000.0
939000.0
982000.0
1080688.7
1100000.0
1184756.1
1386000.0
1673000.0
1673000.0
1678000.0
1800000.0
1844000.0
1970000.0
2410000.0
2420000.0
3280000.0
3389000.0
4460000.0
4460000.0
JLt— J 1
3FFE<
NC
NE
NE
NC
NE
NE
NE
NE
NC
SG
NE
NC
NC
NE
NE
NC
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
SG
SG
NE
NC
NC
SG
NE
NE
NC
SG
SG
NE
*
*
*
* *
*
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( — ) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=308 CHEM=Manganese TEST=HA28 SAMPTYP=bottom sediment - total
RATIO SITE SAMPLE C
57
0.1
0.6
0.4
1.2
0.5
0.3
0.3
0.5
1.0
1.0
1.0
0.6
0.6
1.2
0.7
1.9
1.2
2.8
3.5
3.5
4.7
2.7
11 TB
8 CF
4 SR
11 TB
11 TB
8 CF
4 SR
4 SR
SR
TB
TB
SR
MR
SR
SR
3
11
11
3
7
4
4
1-01
1-06
3-06
1-02
l-RE
1-05
3-02
3-01
1-10
1-03
1-04
1-06
1-01
3-05
3-08
7 MR-1-02
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-24
NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
TEL-SR(ERL*NERM)
8 CF-1-03
2 BR-1-03
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
GL-NERH-85% NO EFFECT
2 BR-1-09
2 BR-1-07
GL-ERL-15% EFFECT
ERL-15% EFFECT
2 BR-1-08
GL-NEC-MAX NO EFFECT
7 MR-1-17
7 MR-1-07
3 SR-1-03
8 CF-1-04
NERH-85% NO EFFECT
7 MR-1-25
7 MR-1-19
GL-PEL-SR (ERM*NERH)
— Slc2—
PEL-SR (ERM*NERH)
2 BR-1-01
7 MR-1-11
ERM-50% EFFECT
GL-ERM-50% EFFECT
— aet5—
7 MR-l-CO
1 IH-1-04
1 IH-1-06
1 IH-1-03
1 IH-1-07
8 CF-1-01
8 CF-1-02
NEC-MAX NO EFFECT
leuiiusiiL - to
'OXIC SURV
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
0
120
100
11
100
114
103
97
100
52
93
10
108
96
88
109
96
102
123
79
100
100
100
100
100
100
88
80
97
115
91
96
128
109
114
89
90
100
0
1
1
0
64
102
.0
.3
.0
.4
.0
.9
.8
.4
.0
.3
.2
.3
.1
.1
.3
.3
.1
.6
.0
.0
.0
.0
.0
.0
.0
.0
.2
.3
.4
.1
.9
.2
.4
.3
.0
.5
.7
.0
.0
.4
.4
.0
.9
.7
taj. I
TOXS
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
TX
TX
TX
NT
JMJ.TQ:
GROW
ND
10
92
72
10
98
10
94
97
97
10
60
79
94
92
92
10
10
82
85
ND
10
10
10
10
10
92
85
10
92
91
91
10
95
89
96
58
10
ND
68
96
ND
73
94
=ng/g
TOXG
ND
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
NT
TX
TX
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
TX
NT
TX
NT
ND
NT
NT
ND
TX
NT
MATURE
ND
90
96
ND
ND
77
10
11
10
ND
ND
37
68
11
95
95
95
10
93
10
ND
10
10
10
10
10
10
10
10
65
31
10
80
12
63
10
24
10
ND
0.
0.
ND
25
48
TOXM
ND
NT
NT
ND
ND
NT
NT
NT
NT
ND
ND
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
ND
TX
NT
-------
CONC EFFE(
352
528
587
1115
1115
1174
1233
1350
1526
1720
1761
2340
2460
2525
2583
3290
3347
3405
3530
3790
4038
4060
4090
4150
4170
4170
4170
4170
4170
4190
4190
4330
4873
4873
5230
5419
6517
6693
7010
7010
8160
8160
9041
13092
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
SG
NE
*
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
ME no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=CR14 SAMPTYP=bottom sediment - sem UNITS=ng/g
GL-SECs NOT REPORTED
4 SR-3-06
3 SR-1-10
4 SR-3-02
4 SR-3-05
3 SR-1-03
4 SR-3-24
4 SR-3-16
0.3 2 BR-1-08
4 SR-3-08
7 MR-1-01
0.4 2 BR-1-03
8 CF-1-03
8 CF-1-06
0.6 2 BR-1-07
2 BR-1-09
8 CF-1-05
NERM-50% NO EFFECT
0.8 1 IH-1-04
7 MR-1-19
7 MR-1-02
TEL-SR (ERL'NERM)
7 MR-1-07
7 MR-1-25
8 CF-1-02
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
8 CF-1-04
NERH-85% NO EFFECT
7 MR-1-17
1.2 1 IH-1-03
ERL-15% EFFECT
7 MR-l-CO
PEL-SR(ERM*NERH)
2 BR-1-01
1.6 1 IH-1-06
1.8 7 MR-1-11
ERM-50% EFFECT
8 CF-1-01
NEC-MAX NO EFFECT
2.2 1 IH-1-07
6.8 3 SR-1-06
58
>eaime
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
snt - se
SURV
103.3
90.3
100.6
104.9
104.5
102.2
102.7
38.0
95.1
117.9
62.8
84.0
107.4
47.9
105.0
96.3
2.0
111.9
113.4
116.4
138.8
79.0
100.0
100.0
100.0
100.0
100.0
109.9
122.4
2.7
100.0
67.8
0.0
70.2
95 ll
0.0
18.7
:m UiM
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
TX
irs-nc
GROW
11
10
12
11
10
11
12
97
11
11
87
10
11
10
10
11
ND
10
.11
11
11
11
10
10
10
10
10
11
12
ND
10
10
ND
75
13
ND
52
j/g —
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
TX
NT
ND
TX
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
COI
7100.
8300.
9000.
11100.
11800.
13000.
13800.
14000.
15000.
15300.
15700.
15700.
15900.
16000.
16000.
16200.
16800.
16900.
17700.
18000.
18500.
18500.
19400.
19400.
19400.
19400.
20300.
20900.
21200.
23500.
23800.
26608.
28500.
29300.
29544.
30900.
31000.
31500.
31500.
36000.
37000.
37900.
37900.
38681.
39600.
40000.
40000.
42800.
43000.
43000.
43531.
44400.
45000.
47500.
50000.
50000.
50000.
51600.
57000.
57000.
57000.
58000.
75000.
103000.
140000.
140000.
157000.
MUl'lt
rc i
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
,0
.0
.0
,0
.0
.0
,0
.0
.0
,0
,0
,0
,0
.0
.0
,0
.0
.0
.0
.0
,3
.0
.0
.9
,0
,0
.0
.0
.0
.0
.0
,0
.4
,0
,0
.0
.0
,0
.0
.6
.0
.0
.0
.0
,0
,0
,0
,0
.0
,0
,0
,0
,0
.0
,0
,0
*\JLJCi-
SFFEI
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
SG
*
*
NE
*
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 ' * 2-4 | **>4
=309 CHEM=Nickel TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
4 SR-3-06
8 CF-1-05
8 CF-1-02
8 CF-1-03
7 MR-1-19
0.5 5 WH-1-01
7 MR-1-02
3 SR-1-10
4 SR-3-02
8 CF-1-04
8 CF-1-01
—telm—
7 MR-1-07
—slcl—
7 MR-1-01
8 CF-l-CO
7 MR-1-25
NERM-50% NO EFFECT
—telf—
4 SR-3-01
7 MR-1-17
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
GL-NERM-50% NO EFFECT
—erl—
5 WH-l-CO
7 MR-l-CO
1.4 7 MR-1-11
TEL-SR (ERL*NERM)
4 SR-3-05
4 SR-3-24
GL-TEL-SR (ERL*NERM)
4 SR-3-16
—aet6—
5 WH-l-RE
NERH-85% NO EFFECT
—pelf—
3 SR-1-03
4 SR-3-08
GL-NERH-85% NO EFFECT
PEL-SR(ERM'NERH)
2 BR-1-09
1.5 5 WH-1-02
ERL-15% EFFECT
—pelm—
1.1 2 BR-1-08
GL-ERL-15% EFFECT
GL-PEL-SR (ERM*NERH)
1.1 2 BR-1-07
1.2 2 BR-1-03
ERM-50% EFFECT
2.6 1 IH-1-04
2.6 1 IH-1-03
GL-ERM-50% EFFECT
—erm—
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
3.0 1 IH-1-07
~slc2 —
5.3 1 IH-1-06
—aet3~
—aetl—
6.6 3 SR-1-06
59
saijnent. - uot
:oxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
107
103
96
79
84
111
8
113
90
100
109
95
116
117
100
138
96
122
100
100
100
100
100
100
70
104
102
102
85
104
95
105
51
38
47
62
2
2
67
0
0
.4
.3
.3
.0
.0
.9
.6
.4
.3
.6
.9
.1
.4
.9
.0
.8
.7
.4
.0
.0
.0
.0
.0
.0
.2
.9
.2
.7
.7
.5
.1
.0
.4
.0
.9
.8
.0
.7
.8
.0
.0
.ax uj
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
TX
NT
TX
TX
,MJ.i;S=I
GROW
11
11
11
11
10
10
ND
11
10
12
11
13
11
11
10
11
10
12
10
10
10
10
ND
10
75
11
11
12
ND
10
11
10
ND
97
10
87
ND
ND
10
ND
ND
ug/g -
TOXG
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
ND
NT
NT
NT
ND
NT
NT
TX
ND
ND
NT
ND
ND
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
18.7 TX
52
TX
ND
ND
-------
CONC EFFE<
1
1
1
2
2
2
2
2
3
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5
5
5
5
6
7
7
10
10
10
20
20
97
171
.8
.8
.9
.0
.0
.2
.3
.4
.2
.2
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.5
.7
.7
.7
.7
.7
.7
.8
.8
.9
.9
.9
.9
.1
.8
.8
.8
.9
.1
.0
.1
.4
.4
.4
.3
.3
.8
.4
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
*
NE
* *
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NtMCODE=309 CHEM=Nickel TEST=CR14 SAMPTYP=porewater UNITS=ug/l
7 MR-1-17
7 MR-1-02
7 MR-1-25
7 MR-1-07
8 CF-1-03
0.7 7 MR-1-11
7 MR-1-19
8 CF-1-06
4 SR-3-02
4 SR-3-01
8 CF-1-05
3 SR-1-10
. 3 SR-1-03
2 BR-1-09
0.9 2 BR-1-08
0.9 2 BR-1-07
0.9 2 BR-1-03
2 BR-1-01
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
8 CF-1-02
8 CF-1-04
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
GL-NERH-85% NO EFFECT
TEL-SR (ERL*NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-08
4 SR-3-06
NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
7 MR-1-01
1.2 1 IH-1-04
GL-ERL-15% EFFECT
ERL-15% EFFECT
1.3 1 IH-1-06
7 MR-l-CO
GL-PEL-SR (ERM*NERH)
PEL-SR (ERM'NERH)
2.2 1 IH-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
8 CF-1-01
NEC-MAX NO EFFECT
23.1 3 SR-1-06
36.5 1 IH-1-07
60
'iCWQV
'OXIC
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
..Gi U
su
122
113
138
116
84
70
111
107
100
96
96
90
104
105
38
47
62
67
79
109
100
100
100
100
100
95
103
117
2
0
100
IN .LI
RV
.4
.4
.8
.4
.0
.2
.9
.4
.6
.7
.3
.3
.5
.0
.0
.9
.8
.8
.0
.9
.0
.0
.0
.0
.0
.1
.3
.9
.0
.0
.0
o— uy /
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
GROW
12
11
11
11
10
75
10
11
12
10
11
10
10
10
97
10
87
10
11
11
10
10
10
10
10
11
11
11
ND
ND
10
TOXG
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
NOT
2.7 TX
95.1 NT
ND ND
13
TOX 18.7 TX 52
TOX 0.0 TX ND
NT
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC EFFEI
352
528
587
1115
1115
1174
1233
1350
1526
1526
1643
1761
2525
2583
2726
2830
3405
4170
4170
4170
4170
4170
4170
4170
4170
4170
4873
4873
4873
5283
5283
6517
6693
6693
6693
9041
13092
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NC
NE
NE
NE
NC
NE
NC
NC
NC
NC
NE
NE
NE
NE
NE
SG
SG
SG
*
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=ng/g
4 SR-3-06
3 SR-1-10
4 SR-3-02
0.7 4 SR-3-05
3 SR-1-03
4 SR-3-24
4 SR-3-16
0.3 2 BR-1-08
4 SR-3-08
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
0.4 2 BR-1-03
0.6 2 BR-1-07
0.6 2 BR-1-09
GL-TEL-SR (ERL*NERM)
TEL-SR(ERL*NERM)
0.8 1 IH-1-04
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
NEC-MAX NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
1.2 1 IH-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
1.6 2 BR-1-01
1.6 1 IH-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
2.2 1 IH-1-07
6.8 3 SR-1-06
61
sediment. - se
70XIC SURV
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
111
101
105
104
115
113
111
113
110
77
86
83
0
100
100
100
100
100
.8
.6
.9
.5
.6
.3
.8
.7
.4
.3
.4
.4
.0
.0
.0
.0
.0
.0
:m un.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
LTS>-n<
GROW
94
10
10
94
95
10
10
85
10
85
85
90
ND
ND
10
10
10
10
j/g —
TOXG
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
ND
ND
NT
NT
NT
NT
MATURE TOXM
74
33
51
22
23
14
16
22
61
68
0.
0.
ND
ND
10
10
10
10
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
TX
ND
ND
NT
NT
NT
NT
TOX
1.4 TX
96 NT
0.
NT
TOX
TOX
TOX
TOX
100.0
1.4
0.0
12.5
NT
TX
TX
TX
85
68
ND
87
TX
NT
ND
NT
0.
0.
ND
0.
TX
NT
ND
NT
-------
CONC EFFEC
8300.
11500.
11900.
13800.
15000.
15300.
15900.
16000.
16000.
18000.
18500.
19400.
19400.
19400.
19400.
19400.
19400.
19400.
19500.
20900.
21200.
27717.
27717.
28500.
29300.
30900.
31000.
31200.
31500.
31500.
36000.
37000.
37900.
37900.
37900.
38496.
38681.
39600.
39600.
39600.
40000.
42800.
43000.
44400.
45000.
47500.
47500.
50000.
50000.
51600.
57000.
58000.
75000.
103000.
140000.
140000.
157000.
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
1
0
0
0
0
0
0
0
0
0
0
0
0
8
4
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
*
SG
*
*
*
*
*
*
*
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORHALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
62
0.5
1.3
2.0
1.5
2.2
2.3
2.3
2.6
2.6
2.9
3.0
5.3
6.6
SR-3-06
TR-1-04
TR-1-03
WH-1-01
SR-1-10
SR-3-02
— telm —
TR-1-01
—telf—
SR-3-01
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
TR-1-02
— erl—
WH-l-CO
TEL-SR(ERL*NERM)
GL-TEL-SR (ERL*NERM)
SR-3-05
SR-3-24
SR-3-16
— aet6 —
NERH-85% NO EFFECT
WH-l-RE
GL-NERH-85% NO EFFECT
— pelf—
SR-1-03
SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM'NERH)
BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
WH-1-02
— pelm —
BR-1-08
BR-1-07
BR-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-04
IH-1-03
— erm —
BR-1-01
IH-1-07
— slc2-~
IH-1-06
— aet3 —
— aetl —
SR-1-06
;u.Liut:£
?OXIC
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
it - tOT
SURV
111.8
93.4
87.5
35.0
101.6
105.9
100.0
116.2
100.0
100.0
100.0
100.0
100.0
100.0
100.0
104.5
113.3
111.8
100.0
115.6
110.4
.al UI
TOXS
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Mllb-I
GROW
94
ND
ND
13
10
10
ND
10
ND
10
10
10
10
ND
10
94
10
10
14
95
10
ig/g •
TOXG
NT
ND
ND
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
MATURE
74
ND
ND
ND
33
51
ND
12
ND
10
10
10
10
ND
ND
22
14
16
ND
23
61
TOXM
NT
ND
ND
ND
NT
NT
ND
NT
ND
NT
NT
NT
NT
ND
ND
TX
NT
NT
ND
NT
NT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
83.4 NT
90
40.0 TX 11
113.7 NT
86.4 NT
77.3 TX
85
85
85
TX
NT
TX
TX
TX
1.4 TX
68
NT
0.
ND
22
0.
68
12.5 TX 87 NT
0.
0.
TX
ND
TX
TX
NT
TOX
TOX
TOX
TOX
0.0
1.4
100.0
0.0
TX
TX
NT
TX
ND
96
85
ND
ND
NT
TX
ND
ND
0.
0.
ND
ND
NT
TX
ND
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE n<5 effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
63
J
CONC EFFEI
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5
5
5
7
7
10
10
10
97
171
.2
.2
.0
.0
.0
.0
.0
.0
.0
.0
.0
.7
.7
.7
.7
.7
.7
.7
.8
.8
.9
.9
.9
.9
.8
.8
.8
.9
.0
.0
.4
.4
.4
.8
.4
NE
NE
NE
NE
NC
NC
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
SG
*
* *
* *
NUMCODE=309 CHEM=Nickel TEST=HA14 SAMPTYP=porewater UNITS=ug/l
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
4 SR-3-02
4 SR-3-01
3 SR-1-10
3 SR-1-03
0.9 2 BR-1-09
0.9 2 BR-1-08
0.9 2 BR-1-07
0.9 2 BR-1-03
0.9 2 BR-1-01
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
TEL-SR(ERL'NERM)
GL-TEL-SR (ERL*NERM)
4 SR-3-08
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
1.2 1 IH-1-04
GL-ERL-15% EFFECT
ERL-15% EFFECT
1.3 1 IH-1-06
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
2.2 1 IH-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
23.1 3 SR-1-06
36.5 1 IH-1-07
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
105.
116,
101.
115.
83.
113,
86.
77.
100.
.9
.2
.6
.6
.4
.7
.4
.3
.0
NT
NT
NT
NT
NT
NT
NT
TX
NT
10
10
10
95
90
85
85
85
85
NT
NT
NT
NT
TX
TX
TX
TX
TX
51
12
33
23
0.
22
0.
68
0.
NT
NT
NT
NT
TX
TX
TX
NT
TX
NOT 100.0 NT ND ND ND
NOT 100.0 NT 10 NT 10
NOT 100.0 NT 10 NT 10
NOT 100.0 NT 10 NT 10
NOT 100.0 NT 10 NT 10
ND
NT
NT
NT
NT
NOT 110.4 NT 10 NT 61 NT
NOT 111.8 NT 94 NT 74 NT
TOX 0.0 TX ND ND ND ND
TOX 1.4 TX 68 NT 0. NT
TOX 1.4 TX 96 NT 0. NT
TOX 12.5 TX 87 NT 0. NT
TOX 0.0 TX ND ND ND ND
-------
CONC !
352.0
528.0
587.0
1115.0
1115.0
1174.0
1233.0
1350.0
1526.0
1526.0
1720.0
1761.0
2340.0
2460.0
2525.0
2583.0
2726.9
3290.0
3290.0
3405.0
3530.0
3790.0
4060.0
4090.0
4150.0
4170.0
4170.0
4170.0
4170.0
4170.0
4170.0
4170.0
4170.0
4170.0
4190.0
4330.0
4630.4
4873.0
4873.0
5230.0
5230.0
5283.0
5406.6
6517.0
6517.0
6693.0
6693.0
7010.0
7010.0
8160.0
9041.0
13092.0
'1UUUJ
3FFE<
NE
NC
NE
NE
NC
NE
NE
NE
NE
NC
NC
NC
NE
NC
NC
NE
NC
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
NE
*
SG
SG
*
*
*
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA28 SAMPTYP=bottom sediment - sem UNITS=:
RATIO SITE SAMPLE C
4 SR-3-06
0.1 3 SR-1-10
4 SR-3-02
4 SR-3-05
0.3 3 SR-1-03
4 SR-3-24
4 SR-3-16
2 BR-1-08
4 SR-3-08
GL-NERM-50% NO EFFECT
0.4 7 MR-1-01
0.6 2 BR-1-03
0.6 8 CF-1-03
8 CF-1-06
0.9 2 BR-1-07
0.9 2 BR-1-09
GL-TEL-SR(ERL*NERM)
8 CF-1-05
NERM-50% NO EFFECT
0.8 1 IH-1-04
0.8 7 MR-1-19
0.8 7 MR-1-02
0.9 7 MR-1-07
7 MR-1-25
8 CF-1-02
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
8 CF-1-04
0.9 7 MR-1-17
TEL-SR(ERL*NERM)
1.2 1 IH-1-03
GL-ERL-15% EFFECT
7 MR-l-CO
NEC-MAX NO EFFECT
GL-PEL-SR (ERM'NERH)
PEL-SR(ERM*NERH)
2.4 2 BR-1-01
ERL-15% EFFECT
1.6 1 IH-1-06
GL-ERM-50% EFFECT
1.5 7 MR-1-11
ERM-50% EFFECT
2.2 8 CF-1-01
2.2 1 IH-1-07
3.1 3 SR-1-06
64
ICU.J.ULC
'OXIC
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
:ni_
SUR
100.
100.
103.
96.
96.
102.
96.
97.
88.
108.
79.
123.
120.
80.
88.
114.
0.
114.
109.
91.
109.
102.
100.
100.
100.
100.
100.
100.
128.
115.
1.
100.
89.
1.
90.
64.
0.
10.
&«
V
0
0
8
1
2
6
1
4
3
1
0
0
3
3
2
9
0
0
3
9
3
7
0
0
0
0
0
0
4
1
4
0
5
4
7
9
0
3
m uwj
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
TX
TX
TX
L i a— ii^
GROW
92
97
10
94
91
10
10
10
92
79
85
82
10
85
92
98
ND
89
92
91
95
94
ND
10
10
10
10
10
10
92
96
10
96
68
58
73
ND
60
j/g —
TOXG
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
NT
ND
TX
TX
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
ND
TX
MATURE
96
10
10
11
10
10
95
10
95
68
10
93
90
10
10
77
ND
63
95
31
12
48
ND
10
10
10
10
10
80
65
0.
10
10
0.
24
25
ND
37
TOXM
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
ND
TX
-------
CONC 1
2000.0
7100.0
8300.0
9000.0
9600.0
10300.0
11000.0
11100.0
11300.0
11500.0
11800.0
11900.0
13000.0
13000.0
13400.0
13800.0
14000.0
14600.0
14600.0
15000.0
15300.0
15700.0
15700.0
15900.0
15900.0
16000.0
16000.0
16000.0
16000.0
16200.0
16800.0
16900.0
18000.0
18300.0
18500.0
18500.0
19400.0
19400.0
19400.0
19400.0
19400.0
19400.0
19500.0
19514.1
20000.0
20900.0
21200.0
23000.0
23500.0
23800.0
23800.0
24100.0
24100.0
27717.1
28500.0
29300.0
30900.0
31000.0
31500.0
31500.0
32821.8
36000.0
36900.0
37000.0
37900.0
39600.0
39600.0
39686.3
40000.0
42800.0
43000.0
43000.0
43000.0
44400.0
44700.0
45000.0
50000.0
2FFEC
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NC
NE
NC
NC
NE
NE
NC
NE
NE
SG
NE
NE
NC
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
SG
SG
NE
SG
SG
*
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA28 SAMPTYP=bottom sediment - total
0.2 11 TB-1-01
8 CF-1-06
4 SR-3-06
8 CF-1-05
11 TB-l-RE
10 MB-l-RE
1.0 11 TB-1-02
8 CF-1-02
6 DM-l-RE
9 TR-1-04
1.0 8 CF-1-03
9 TR-1-03
11 TB-1-04
0.6 7 MR-1-19
10 MB-1-01
0.5 5 WH-1-01
0.7 7 MR-1-02
10 MB-1-03
10 MB-1-02
0.8 3 SR-1-10
4 SR-3-02
8 CF-1-04
1.3 8 CF-1-01
10 MB-1-04
—telm—
9 TR-1-01
0.8 7 MR-1-07
NERM-50% NO EFFECT
—slcl—
0.8 7 MR-1-01
8 CF-l-CO
7 MR-1-25
— telf—
6 UM-l-CO
4 SR-3-01
0.9 7 MR-1-17
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
GL-NERM-50% NO EFFECT
9 TR-1-02
TEL-SR (ERL*NERM)
1.8 11 TB-1-03
—erl—
5 WH-l-CO
6 UM-1-02
7 MR-l-CO
1.2 7 MR-1-11
ERL-15% EFFECT
6 UM-1-03
NERH-85% NO EFFECT
GL-TEL-SR(ERL*NERM)
4 SR-3-05
4 SR-3-24
4 SR-3-16
—aet6—
5 WH-l-RE
GL-NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
—pelf—
6 UM-1-01
1.9 3 SR-1-03
4 SR-3-08
1.3 2 BR-1-09
GL-ERL-15% EFFECT
GL-PEL-SR(ERM'NERH)
1.5 5 WH-1-02
—pelm—
2 BR-1-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
1.4 2 BR-1-07
ERM-50% EFFECT
1.4 2 BR-1-03
2.6 1 IH-1-04
65
sciimei
fOXIC
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
1C - COt
SURV
0.0
120.3
100.0
114.9
100.0
100.0
11.4
102.7
86.5
82.9
123.0
98.6
93.2
114.0
75.8
71.7
109.3
95.5
97.0
100.0
103.8
128.4
64.9
95.5
81.4
91.9
108.1
100.0
109.3
100.0
97.4
115.1
100.0
100.0
100.0
100.0
100.0
100.0
52.3
100.0
117.9
100.0
90.7
114.9
96.1
102.6
96.1
109.5
119.3
96.2
88.3
88.2
36.5
97.4
80.3
79.0
0.0
,ai uj
TOXS
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
NJ.T£>=]
GROW
ND
10
92
98
10
ND
72
94
ND
ND
82
ND
10
89
ND
91
92
ND
ND
97
10
10
73
ND
ND
91
79
10
95
ND
94
92
ND
10
10
10
10
ND
97
10
ND
10
58
ND
94
10
10
11
ND
91
92
92
74
10
85
85
ND
ng/g -
TOXG
ND
NT
NT
NT
NT
ND
TX
NT
ND
ND
TX
ND
NT
TX
ND
NT
TX
ND
ND
TX
NT
NT
TX
ND
ND
TX
TX
NT
NT
ND
NT
TX
ND
NT
NT
NT
NT
ND
NT
NT
ND
NT
TX
ND
NT
NT
NT
NT
ND
TX
NT
NT
TX
NT
TX
TX
ND
MATURE
ND
90
96
77
ND
ND
ND
48
ND
ND
93
ND
ND
63
ND
ND
95
ND
ND
10
10
80
25
ND
ND
31
68
10
12
ND
11
65
ND
10
10
10
10
ND
ND
ND
ND
10
24
ND
11
10
95
ND
ND
10
95
10
ND
10
10
10
ND
: TOXM
ND
NT
NT
NT
ND
ND
ND
NT
ND
ND
NT
ND
ND
NT
ND
ND
NT
ND
ND
NT
NT
NT
TX
ND
ND
TX
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
NT
ND
ND
ND
ND
NT
TX
ND
NT
NT
NT
ND
ND
NT
NT
NT
ND
NT
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 66
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT
50000
50000
51600
57000
58000
75000
103000
140000
140000
157000
.0 *
.0
.0
.0 SG
.0 *
.0
.0 **
.0
.0
.0 **
RATIO SITE SAMPLE CEN TOXIC
2.
1.
3.
5.
8.
6
8
0
3
1
1
2
1
1
3
IH-1-03
GL-ERM-50% EFFECT
— erm —
BR-1-01
IH-1-07
— slc2-~
IH-1-06
— aet3 —
— aetl —
SR-1-06
TOX
TOX
TOX
TOX
TOX
SURV
1.4
89.5
0.0
1.4
10.3
TOXS
TX
TX
TX
TX
TX
GROW
96
96
ND
68
60
TOXG
NT
NT
ND
NT
TX
MATURE TOX]
0.
10
ND
0.
37
NT
NT
ND
NT
TX
-------
CONC EFFEC
1
1
1
2
2
2
2
2
3
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5
5
5
5
6
6
7
7
10
10
10
20
97
171
.8
.8
.9
.0
.0
.2
.3
.4
.2
.2
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.5
.7
.7
.7
.7
.7
.7
.7
.7
.8
.8
.9
.9
.9
.1
.8
.8
.8
.9
.1
.1
.0
.0
.4
.4
.4
.3
.8
.4
NC
NC
NE
NC
NC
NC
NC
NE
NE
NE
NE
NC
NC
NC
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
NE
*
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=309 CHEM=Nickel TEST=HA28 SAMPTYP=porewater
0.5 7 MR-1-17
0.5 7 MR-1-02
7 MR-1-25
0.5 7 MR-1-07
0.5 8 CF-1-03
0.6 7 MR-1-11
0.6 7 MR-1-19
8 CF-1-06
4 SR-3-02
4 SR-3-01
8 CF-1-05
0.9 3 SR-1-10
0.9 3 SR-1-03
0.9 2 BR-1-09
2 BR-1-08
0.9 2 BR-1-07
0.9 2 BR-1-03
0.9 2 BR-1-01
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
8 CF-1-02
8 CF-1-04
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
4 SR-3-08
4 SR-3-06
GL-NEC-MAX NO EFFECT
1.3 7 MR-1-01
1.2 1 IH-1-04
GL-ERL-15% EFFECT
ERL-15% EFFECT
1.3 1 IH-1-06
7 MR-l-CO
NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM'NERH)
2.2 1 IH-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
5.2 8 CF-1-01
20.8 3 SR-1-06
36.5 1 IH-1-07
67
>£.ewaL.e£ ui>u.i
'OXIC SURV
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
115
109
109
91
123
90
114
120
103
97
114
100
96
88
97
80
79
89
102
128
100
100
100
100
100
100
88
100
108
0
1
100
.1
.3
.3
.9
.0
.7
.0
.3
.8
.4
.9
.0
.2
.2
.4
.3
.0
.5
.7
.4
.0
.0
.0
.0
.0
.0
.3
.0
.1
.0
.4
.0
a=uy i
TOXS
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
GROW
92
92
95
91
82
58
89
10
10
94
98
97
91
92
10
85
85
96
94
10
ND
10
10
10
10
10
92
92
79
ND
68
10
TOXG
TX
TX
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
MATURE
65
95
12
31
93
24
63
90
10
11
77
10
10
10
10
10
10
10
48
80
ND
10
10
10
10
10
95
96
68
ND
0.
10
TOXM
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
TOX
1.4 TX 96
TOX 64.9 TX 73
TOX 10.3 TX 60
TOX 0.0 TX ND
NT
TX
TX
ND
0.
25
37
ND
NT
TX
TX
ND
-------
IMU
CONC I
2279.0
2279.0
3500.0
3937.0
4351.0
5387.0
6060.0
7459.0
7459.0
7666.0
8702.0
8702.0
8909.0
9116.0
9494.9
10360.0
10360.0
10360.0
11009.6
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
11900.0
13882.0
19400.0
32000.0
34605.2
36700.0
39159.0
39159.0
45700.0
46300.0
48600.0
48600.0
50200.0
55000,0
56300.0
59878.0
62400.0
62786.9
81115.0
102352.0
102352.0
106703.0
260023.0
569000.0
569000.0
nii_uL
SFFEC
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
**
NE
* *
* *
* *
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=CR14 SAMPTYP=bottom sediment - sem UNITS=ng/g
4 SR-3-06
3 SR-1-10
8 CF-1-06
4 SR-3-02
4 SR-3-05
0.3 2 BR-1-08
7 MR-1-01
4 SR-3-16
0.4 2 BR-1-07
2 BR-1-09
4 SR-3-24
GL-NERM-50% NO EFFECT
4 SR-3-08
3 SR-1-03
GL-TEL-SR{ERL*NERM)
1.3 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
TEL-SR(ERL'NERM)
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
7 MR-l-CO
0.7 2 BR-1-03
8 CF-1-05
7 MR-1-02
GL-PEL-SR (ERM*NERH)
7 MR-1-25
2 BR-1-01
GL-NEC-MAX NO EFFECT
7 MR-1-07
7 MR-1-17
7 MR-1-19
NERH-85% NO EFFECT
8 CF-1-04
8 CF-1-03
1.7 7 MR-1-11
5.1 1 IH-1-04
8 CF-1-02
PEL-SR (ERM*NERH)
ERM-50% EFFECT
8.7 1 IH-1-03
GL-ERM-50% EFFECT
9.1 1 IH-1-06
22.2 1 IH-1-07
8 CF-1-01
NEC-MAX NO EFFECT
68
"aimer
'OXIC
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
1C - ;
SU]
103
90
107
100
104
38
117
102
47
105
102
95
104
18
100
100
100
100
100
100
62
96
113
138
67
116
122
111
109
84
70
2
79
2
0
0
95
sem
RV
.3
.3
.4
.6
.9
.0
.9
.7
.9
.0
.2
.1
.5
.7
.0
.0
.0
.0
.0
.0
.8
.3
.4
.8
.8
.4
.4
.9
.9
.0
.2
.0
.0
.7
.0
.0
.1
UWJ.U
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
NT
,i>-ng/
GROW
11
10
11
12
11
97
11
12
10
10
11
11
10
52
10
10
10
10
10
10
87
11
11
11
10
11
12
10
11
10
75
ND
11
ND
ND
ND
13
g
TOXG :
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
ND
ND
ND
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC ]
14000.0
14900.0
16900.0
19000.0
19600.0
19600.0
19600.0
19600.0
23200.0
25200.0
26400.0
29800.0
30200.0
31000.0
32400.0
32400.0
32400.0
32400.0
34200.0
35000.0
38500.0
46700.0
49000.0
49000.0
51000.0
52786.4
55000.0
58000.0
63200.0
67700.0
68700.0
68700.0
69649.1
70000.0
82600.0
85500.0
85600.0
86000.0
86000.0
88600.0
91300.0
92900.0
92900.0
98700.0
99000.0
99000.0
107000.0
112000.0
113000.0
183942.2
191803.0
218000.0
250000.0
251000.0
260000.0
286000.0
286000.0
396000.0
396000.0
450000.0
492500.0
530000.0
589000.0
660000.0
660000.0
679000.0
679000.0
720000.0
878000.0
1354000.0
•lV_Wt/J
2FFEI
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NG
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
*
NE
NE
NE
SG
NC
NE
* *
NE
* *
**
NE
**
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
7 MR-1-01
4 SR-3-06
3 SR-1-10
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
8 CF-l-CO
4 SR-3-01
7 MR-l-CO
4 SR-3-02
—telm—
—slcl—
5 WH-l-RE
5 WH-l-CO
1.0 5 WH-1-01
GL-NERM-50% NO EFFECT
4 SR-3-05
—telf—
8 CF-1-05
—erl—
2 BR-1-09
NERM-50% NO EFFECT
0.4 2 BR-1-08
GL-TEL-SR(ERL*NERM)
3 SR-1-03
4 SR-3-16
7 MR-1-02
4 SR-3-24
4 SR-3-08
GL-NERH-85% NO EFFECT
TEL-SR(ERL*NERM)
0.6 2 BR-1-07
7 MR-1-07
8 CF-1-04
7 MR-1-25
2.8 3 SR-1-06
GL-ERL-15% EFFECT
7 MR-1-17
—pelf—
7 MR-1-19
NERH-85% NO EFFECT
8 CF-1-03
1.5 7 MR-1-11
ERL-15% EFFECT
0.9 2 BR-1-03
—pelm—
8 CF-1-02
GL-PEL-SR(ERM*NERH)
PEL-SR(ERM*NERH)
—erm—
—slc2—
7.7 5 WH-1-02
—aet6—
2 BR-1-01
GL-NEC-MAX NO EFFECT
20.2 1 IH-1-04
ERM-50% EFFECT
—aet3 —
GL-ERM-50% EFFECT
—aet4—
30.1 1 IH-1-03
—aet2—
—aetl—
8 CF-1-01
NEC-MAX NO EFFECT
—aet5—
44.8 1 IH-1-06
69.1 1 IH-1-07
69
lament. - tot
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=310 CHEM=Lead TEST=CR14 SAMPTYP=poirewater UNITS=ug/l
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
CF-1-05
CF-1-01
BR-l-CO
CF-1-03
CF-1-04
MR-1-25
MR-1-17
MR-1-02
CF-1-06
MR-l-CO
MR-1-07
MR-1-01
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
SR-1-03
BR-1-09
BR-1-08
BR-1-07
GL-NERM-50% NO EFFECT
SR-1-10
MR-1-19
MR-1-11
ERL-15% EFFECT
CF-1-02
BR-1-03
GL-TEL-SR (ERL*NERM)
SR-3-06
SR-3-02
SR-3-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-08
IH-1-06
GL-ERL-15% EFFECT
BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
SR-1-06
ERM-50% EFFECT
IH-1-04
GL-ERM-50% EFFECT
IH-1-03
IH-1-07
70
CONC
0.2
0.2
0.2
0.2
0.2
0.2
0.2
0.3
0.3
0.3
0.3
0.3
0.4
0.4
0.4
0.4
0.4
0.6
0.7
0.7
0.7
0.8
0.8
0.8
0.9
0.9
0.9
1.2
1.6
2.1
3.5
3.5
3.5
3.5
3.5
4.1
5.3
5.3
5.7
5.7
5.7
14.8
17.7
36.2
62.9
89.5
89.5
96.8
1284.0
J\UKlt_ULI.B-JJ
EFFECT RATIO £
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
.
NE
NE
NC 0.3
NC 0.4
t
NE
NE
* 2.1
NE
NC 0.7
NE
NE
NE
NE
** 25.2
NE
,
** 63.1
.
** 426.2
.
** 461.0
6114.3
-U I
5ITI
4
3
1
8
8
8
2
8
8
7
7
7
8
7
7
7
.
3
2
2
2
3
7
7
8
2
4
4
4
.
4
1
2
3
1
1
1
rewater UJNJ.MO
TOXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
100
100
100
100
96
95
100
84
109
138
122
113
107
100
116
117
104
105
38
47
90
111
70
79
62
103
100
96
95
0
.0
.0
.0
.0
.3
.1
.0
.0
.9
.8
.4
.4
.4
.0
.4
.9
.5
.0
.0
.9
.3
.9
.2
.0
.8
.3
.6
.7
.1
.0
=ug/ J
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
GROW
10
10
10
10
11
13
10
10
11
11
12
11
11
10
11
11
10
10
97
10
10
10
75
11
87
11
12
10
11
ND
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
ND
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
IT
K
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
67.8 NT
10
TOX 18.7 TX 52
TOX 2.0 TX ND
TOX 2.7 TX ND
TOX 0.0 TX ND
NT
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC 1
2279.0
2279.0
3937.0
4351.0
5387.0
7459.0
7459.0
7666.0
7666.0
8184.0
8702.0
8909.0
9116.0
10316.0
10360.0
10658.8
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
11700.0
13882.0
13882.0
13882.0
26468.3
26468.3
39159.0
59878.0
59878.0
59878.0
102352.0
106703.0
260023.0
JJ.UV.WJ
2FFEI
NE
NE
NE
NC
NC
NE
NC
NC
NE
NE
NE
SG
NE
NE
NE
NE
NE
SG
*
* *
**
* *
* *
APPENE. . 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=ng/g
4 SR-3-06
3 SR-1-10
4 SR-3-02
0.6 4 SR-3-05
0.5 2 BR-1-08
4 SR-3-16
0.6 2 BR-1-07
0.7 2 BR-1-09
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
4 SR-3-24
4 SR-3-08
3 SR-1-03
GL-TEL-SR(ERL*NERM)
1.3 3 SR-1-06
TEL-SR (ERL*NERM)
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
NEC-MAX NO EFFECT
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
1.2 2 BR-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
3.3 2 BR-1-01
5.1 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
8.7 1 IH-1-03
9.1 1 IH-1-06
22.2 1 IH-1-07
71
= U.-LlUCi
[•OXIC
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
1U —
su
111
101
105
104
113
111
86
83
113
110
115
12
100
100
100
100
100
OtSltl
RV
.8
.6
.9
.5
.7
.8
.4
.4
.3
.4
.6
.5
.0
.0
.0
.0
.0
1 UiN -L .
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
L o— iiy ,
GROW
94
10
10
94
85
10
85
90
10
10
95
87
ND
10
10
10
10
i y
TOXG
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
MATURE
74
33
51
22
22
16
0.
0.
14
61
23
0.
ND
10
10
10
10
TOXM
NT
NT
NT
TX
TX
NT
TX
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
TOX
77.3 TX
85
TX
68
NT
TOX
TOX
TOX
TOX
TOX
100
0
1
1
0
.0
.0
.4
.4
.0
NT
TX
TX
TX
TX
85
ND
96
68
ND
TX
ND
NT
NT
ND
0.
ND
0.
0.
ND
TX
ND
NT
NT
ND
-------
CONC I
11300.0
16600.0
16900.0
18700.0
19000.0
19600.0
19600.0
19600.0
19600.0
1960Q.O
22900.0
22900.0
25200.0
29800.0
30200.0
31000.0
31100.0
32400.0
32400.0
32400.0
34174.6
34200.0
35000.0
39825.9
46700.0
49000.0
51000.0
51000.0
51000.0
55000.0
55000.0
58000.0
58000.0
67700.0
68700.0
68700.0
68700.0
70000.0
86000.0
91300.0
107000.0
112000.0
117494.7
120656.5
218000.0
250000.0
251000.0
251000.0
251000.0
260000.0
286000.0
396000.0
450000.0
530000.0
589000.0
660000.0
660000.0
720000.0
878000.0
1354000.0
I"- \JLJl
5FFEI
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NG
NC
•it
it
NE
NE
NE
NE
*
*
* *
* *
**
**
**
* *
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=HA14 SAMPTYP=bottom sediment -
RATIO SITE SAMPLE C
9 TR-1-01
9 TR-1-03
4 SR-3-06
9 TR-1-02
3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
9 TR-1-04
NERM-50% NO EFFECT
4 SR-3-01
4 SR-3-02
—telm—
—slcl—
GL-NERM-50% NO EFFECT
5 WH-l-RE
5 WH-l-CO
1.0 5 WH-1-01
TEL-SR(ERL*NERM)
0.8 4 SR-3-05
— telf—
GL-TEL-SR(ERL*NERM)
—erl—
2.5 2 BR-1-09
2.6 2 BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
3 SR-1-03
NERH-85% NO EFFECT
4 SR-3-16
GL-NERH-85% NO EFFECT
4 SR-3-24
4 SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
3.6 2 BR-1-07
2.8 3 SR-1-06
—pelf~~
5.5 2 BR-1-03
—pelm—
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
—erm—
~-slc2 —
7.7 5 WH-1-02
GL-ERM-50% EFFECT
ERM-50% EFFECT
—aet6—
14.6 2 BR-1-01
20.2 1 IH-1-04
—aet3 —
—aet4—
30.1 1 IH-1-03
—aet2—
72
liiiwsiii, - uvua
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
100
87
111
100
101
100
100
100
100
100
93
116
105
100
100
35
104
83
113
115
111
113
110
86
12
.0
.5
.8
.0
.6
.0
.0
.0
.0
.0
.4
.2
.9
.0
.0
.0
.5
.4
.7
.6
.8
.3
.4
.4
.5
.j. UINJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
L1»=IN
GROW
ND
ND
94
ND
10
ND
10
10
10
10
ND
10
10
14
10
13
94
90
85
95
10
10
10
85
87
3/g —
TOXG
ND
ND
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
MATURE TOXM
ND
ND
74
ND
33
ND
10
10
10
10
ND
12
51
ND
ND
ND
22
0.
22
23
16
14
61
0.
0.
ND
ND
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
ND
ND
ND
TX
TX
TX
NT
NT
NT
NT
TX
NT
TOX
TOX
77.3 TX
85
TX
40.0 TX 11 NT
TOX 100.0 NT 85 TX
TOX 0.0 TX ND ND
TOX
1.4 TX 96 NT
44.8 1 IH-1-06
69.1 1 IH-1-07
TOX
TOX
1.4
0.0
TX
TX
68
ND
NT
ND
68
ND
0.
ND
0.
0.
ND
NT
ND
TX
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA)
INCLUDES NBS AND OTHER ( — )
NE no effect | NC<1 | NG=1 | SG 1-2
NORMALIZED TO DRY WEIGHT
SECs
| * 2-4 | **>4
73
JMUKU_UL>Ji=JJ.U 1
CONG EFFECT RATIO SIT:
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
3
3
3
3
3
4
4
4
4
4
5
5
5
5
36
89
96
1284
.2
.2
.2
.2
.2
.7
.7
.7
.7
.7
.7
.7
.7
.8
.8
.8
.6
.5
.5
.5
.5
.5
.1
.1
.1
.4
.4
.3
.5
.5
.7
.2
.5
.8
.0
NE
NE
NE
NE
NE
NE
* 3.3
* 3.3
.
.
* 3.8
NE
** 7.6
NE
NE
NE
.
.
NE
.
** 25.2
.
** 27.1
** 63.1
** 426.2
** 461.0
** 6114.3
9
4
3
1
2
3
2
2
.
.
.
.
.
.
2
3
2
4
4
4
.
4
1
2
3
1
1
1
CHEM=Lead TEST=HA14 SAMPTYP=porewater
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-03
BR-1-09
BR-1-08
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
GL-NERM-50% NO EFFECT
BR-1-07
SR-1-10
BR-1-03
SR-3-06
SR-3-02
SR-3-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
IH-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-01
SR-1-06
IH-1-04
IH-1-03
IH-1-07
:ewat«
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
2r UJNJ.T;
SURV
100.0
100.0
100.0
100.0
100.0
115.6
83.4
113.7
j-ug/.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
GROW
ND
10
10
10
10
95
90
85
TOXG
ND
NT
NT
NT
NT
NT
TX
TX
MATURE
ND
10
10
10
10
23
0.
22
TOXM
ND
NT
NT
NT
NT
NT
TX
TX
TOX
NOT
TOX
NOT
NOT
NOT
86
101
77
111
105
116
.4
.6
.3
.8
.9
.2
NT
NT
TX
NT
NT
NT
85
10
85
94
10
10
TX
NT
TX
NT
NT
NT
0.
33
68
74
51
12
TX
NT
NT
NT
NT
NT
NOT
TOX
110.4 NT 10 NT 61 NT
1.4 TX 68 NT 0. NT
TOX
TOX
TOX
TOX
TOX
100.
12,
0,
1.
0.
.0
.5
.0
.4
.0
NT
TX
TX
TX
TX
85
87
ND
96
ND
TX
NT
ND
NT
ND
0.
0.
ND
0.
ND
TX
NT
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (-—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=HA28 SAMPTYP=bottom sediment - sem UNITS=ng/g
74
2279
2279
3500
3937
4351
5387
6060
7459
7459
7666
8184
8702
8909
9116
9116
10360
10658
11700
11700
11700
11700
11700
11700
11700
11700
11900
13882
13882
17079
19400
19400
30806
32000
32000
32665
36700
39159
45700
46300
48600
50200
55000
55000
56300
59878
62400
62400
81115
102352
106703
260023
569000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NC
NE
NE
NE
NE
NC
NE
NC
NC
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
SG
NE
SG
NE
* *
SG
SG
*
NE
SG
*
* *
NE
* *
**
**
* *
0.2
0.2
0.9
0.9
,
.
0.8
.
0.9
.
.
.
1.6
1.3
4.6
1.9
1.9
2.0
1.9
2.3
5.1
.
.
8.7
9.1
22.2
19.3
4
3
8
4
4
2
7
4
2
2
.
4
4
3
3
9
4
3
1
8
2
7
2
8
7
7
2
7
7
7
8
8
.
7
1
8
1
1
1
8
SR-3-06
SR-1-10
CF-1-06
SR-3-02
SR-3-05
BR-1-08
MR-1-01
SR-3-16
BR-1-07
BR-1-09
GL-NERM-50% NO EFFECT
SR-3-24
SR-3-08
SR-1-03
NERM-50% NO EFFECT
SR-1-06
GL-TEL-SR (ERL*NERM)
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
GL-NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
MR-l-CO
BR-1-03
GL-ERL-15% EFFECT
TEL-SR(ERL*NERM)
CF-1-05
NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
MR-1-02
ERL-15% EFFECT
PEL-SR(ERM*NERH)
MR-1-25
BR-1-01
MR-1-07
MR-1-17
MR-1-19
CF-1-04
CF-1-03
ERM-50% EFFECT
MR-1-11
IH-1-04
CF-1-02
NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
IH-1-03
IH-1-06
IH-1-07
CF-1-01
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
100.0
100.0
120.3
103.8
96.1
97.4
108.1
96.1
80.3
88.2
102.6
88.3
96.2
10.3
100.0
100.0
100.0
100.0
100.0
100.0
100.0
79.0
.
114.9
.
109.3
.
109.3
89.5
91.9
115.1
114.0
128.4
123.0
90.7
0.0
102.7
.
1.4
1.4
0.0
64.9
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
92
97
10
10
94
10
79
10
85
92
10
92
91
60
ND
10
10
10
10
10
10
85
98
92
95
96
91
92
89
10
82
58
ND
94
96
68
ND
73
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
NT
TX
TX
ND
NT
NT
NT
ND
TX
96
10
90
10
11
10
68
95
10
10
10
95
10
37
ND
10
10
10
10
10
10
10
77
95
12
10
31
65
63
80
93
24
ND
48
0.
0.
ND
25
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
ND
NT
NT
NT
ND
TX
-------
APPENDIX 4a:
NE
ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
75
nurn_viJJ
CONC EFFEI
7000
10900
11300
14000
14700
14900
16600
16900
17000
18700
19000
19600
19600
19600
19600
19600
22000
22900
23200
24000
24100
25200
25200
26400
29800
30200
31000
31100
32000
32400
32400
32400
33700
34200
35000
37229
38500
39800
40500
41000
41358
46700
49000
51000
55000
55000
55000
57300
58000
58000
63200
67700
67700
68700
68700
70000
71100
81743
82600
85500
85600
86000
88600
91300
92900
98700
98700
99000
107000
112000
113000
120656
127000
127000
218000
250000
251000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.4
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.0
.0
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NG
NE
NE
NE
NE
NE
SG
SG
NE
*
NE
NE
SG
NE
NE
SG
NE
SG
NE
NE
»*
SG
SG
SG
SG
*
NE
NE
**
=310 CHEM=Lead TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
0.3 11 TB-1-01
6 UM-l-RE
9 TR-1-01
8 CF-1-06
6 UM-l-CO
0.3 7 MR-1-01
9 TR-1-03
4 SR-3-06
11 TB-l-RE
9 TR-1-02
1.0 3 SR-1-10
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
0.9 11 TB-1-02
9 TR-1-04
8 CF-l-CO
10 MB-1-02
6 UM-1-02
4 SR-3-01
NERM-50% NO EFFECT
7 MR-l-CO
4 SR-3-02
—telm—
—slcl—
GL-NERM-50% NO EFFECT
11 TB-1-04
5 WH-l-RE
5 WH-l-CO
1.0 5 WH-1-01
6 UM-1-03
4 SR-3-05
—telf—
TEL-SR(ERL*NERM)
8 CF-1-05
10 MB-1-04
10 MB-l-RE
1.7 11 TB-1-03
GL-TEL-SR(ERL*NERM)
—erl—
1.4 2 BR-1-09
2 BR-1-08
2.8 3 SR-1-03
GL-ERL-15% EFFECT
ERL-15% EFFECT
6 UM-1-01
4 SR-3-16
GL-NERH-85% NO EFFECT
1.1 7 MR-1-02
4 SR-3-24
NERH-85% NO EFFECT
4 SR-3-08
GL-NEC-MAX NO EFFECT
2.0 2 BR-1-07
10 MB-1-03
PEL-SR(ERM*NERH)
1.5 7 MR-1-07
8 CF-1-04
7 MR-1-25
4.4 3 SR-1-06
1.6 7 MR-1-17
—pelf—
1.7 7 MR-1-19
1.8 8 CF-1-03
ERM-50% EFFECT
1.8 7 MR-1-11
3.0 2 BR-1-03
—pelm—
8 CF-1-02
GL-PEL-SR(ERM*NERH)
10 MB-1-01
NEC-MAX NO EFFECT
—erm—
—slc2 —
7.7 5 WH-1-02
AAmCIl!
[-OXIC
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
. UVL'C
SURV
0.0
86.5
81.4
120.3
100.0
108.1
98.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
11.4
82.9
100.0
97.0
117.9
97.4
100.0
103.8
93.2
109.5
100.0
71.7
114.9
96.1
114.9
95.5
100.0
52.3
88.2
97.4
96.2
119.3
96.1
109.3
102.6
88.3
80.3
95.5
91.9
128.4
109.3
10.3
115.1
114.0
123.0
90.7
79.0
102.7
75.8
1J. VIM.
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
L4.£>— 11^
GROW
ND
ND
ND
10
ND
79
ND
92
10
ND
97
ND
10
10
10
10
72
ND
10
ND
ND
94
10
10
10
11
10
91
ND
94
98
ND
ND
97
92
10
91
ND
10
92
10
92
85
ND
91
10
95
60
92
89
82
58
85
94
ND
i I u
TOXG
ND
ND
ND
NT
ND
TX
ND
NT
NT
ND
TX
ND
NT
NT
NT
NT
TX
ND
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
ND
NT
NT
NT
TX
ND
NT
TX
NT
NT
TX
ND
TX
NT
NT
TX
TX
TX
TX
TX
TX
NT
ND
MATURE
ND
ND
ND
90
ND
68
ND
96
ND
ND
10
ND
10
10
10
10
ND
ND
10
ND
ND
11
10
10
ND
ND
ND
ND
ND
11
77
ND
'ND
ND
10
10
10
ND
95
95
10
95
10
ND
31
80
12
37
65
63
93
24
10
48
ND
TOXM
ND
ND
ND
NT
ND
NT
ND
NT
ND
ND
NT
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
NT
NT
NT
ND
ND
ND
ND
ND
NT
NT
ND
ND
ND
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
ND
TOX
36.5 TX
74
TX
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 76
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | *»>4
- NUMCODE=310 CHEM=Lead TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
251000
260000,
286000
396000
450000
530000.
589000.
660000
660000,
679000,
720000.
878000.
1354000.
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
GL-ERM-50% EFFECT
**
**
**
**
**
* *
8
20
30
12
44
69
.1
.2
.
.1
.4
.8
.1
2
1
1
.
8
.
1
1
— aet6 —
BR-1-01
IH-1-04
— aet3 —
— aet4 —
IH-1-03
— aet2 —
— aetl —
CF-1-01
— aet5 —
IH-1-06
IH-1-07
TOX
TOX
TOX
TOX
TOX
TOX
.
89.5
0.0
.
1.4
.
.
64.9
.
1.4
0.0
TX
TX
TX
TX
TX
TX
96
ND
96
73
68
ND
NT
ND
NT
TX
NT
ND
10
ND
0.
25
0.
ND
NT
ND
NT
TX
NT
ND
-------
CONC EFFEl
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
1
1
3
3
3
3
3
4
4
4
4
5
5
5
36
89
96
1284
.2
.2
.2
.2
.2
.2
.2
.2
.3
.3
.3
.3
.3
.3
.4
.4
.4
.4
.5
.7
.7
.7
.7
.7
.7
.7
.8
.8
.9
.9
.9
.2
.6
.8
.5
.5
.5
.5
.5
.1
.1
.1
.3
.3
.3
.7
.2
.5
.8
.0
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NC
NC
NE
NE
SG
SG
*
SG
NE
SG
*
*
*
NE
*
NE
NE
NE
NE
**
**
* *
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=310 CHEM=Lead TEST=HA28 SAMPTYP=porewater UNITS=ug/l
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-05
0.5 8 CF-1-01
2 BR-l-CO
0.5 8 CF-1-03
8 CF-1-04
7 MR-1-25
0.9 7 MR-1-17
0.9 7 MR-1-02
NERM-50% NO EFFECT
8 CF-1-06
7 MR-l-CO
1.1 7 MR-1-07
1.1 7 MR-1-01
TEL-SR(ERL*NERM)
3.3 3 SR-1-03
1.5 2 BR-1-09
2 BR-1-08
GL-TEL-SR (ERL*NERM)
GL-NERM-50% NO EFFECT
GL-ERL-15% EFFECT
ERL-15% EFFECT
1.8 2 BR-1-07
3.9 3 SR-1-10
2.6 7 MR-1-19
2.6 7 MR-1-11
ERM-50% EFFECT
8 CF-1-02
3.5 2 BR-1-03
PEL-SR(ERM*NERH)
4 SR-3-06
4 SR-3-02
4 SR-3-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
4 SR-3-08
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-PEL-SR(ERM*NERH)
25.2 1 IH-1-06
GL-ERM-50% EFFECT
12.5 2 BR-1-01
172.4 3 SR-1-06
426.2 1 IH-1-04
461.0 1 IH-1-03
6114.3 1 IH-1-07
77
rewat*
'OX 1C
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
££ U1NJ.1C
SURV
100.0
100.0
100.0
100.0
100.0
114.9
64.9
100.0
123.0
128.4
109.3
115.1
109.3
120.3
100.0
91.9
108.1
96.2
88.2
97.4
80.3
100.0
114.0
90.7
102.7
79.0
100.0
103.8
97.4
>=ug/ .
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
L
GROW
ND
10
10
10
10
98
73
10
82
10
95
92
92
10
10
91
79
91
92
10
85
97
89
58
94
85
92
10
94
TOXG
ND
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
NT
TX
TX
TX
NT
NT
TX
TX
TX
TX
NT
TX
NT
NT
NT
MATURE
ND
10
10
10
10
77
25
10
93
80
12
65
95
90
10
31
68
10
10
10
10
10
63
24
48
10
96
10
11
TOXM
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
88.3 NT 92 NT
1.4 TX
89.5
10.3
TX
TX
0.0 TX
1.4 TX
0.0 TX
68
96
60
ND
96
ND
NT
NT
TX
ND
NT
ND
95
0.
10
37
ND
0.
ND
NT
NT
NT
TX
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
78
iMurai-wi
CONC EFFE(
1830
2549
3465
3595
4707
5360
6668
7060
11113
11113
11767
11902
12093
12747
12747
12747
13358
14000
14000
14000
14000
14000
14000
14000
14000
17388
20000
20000
27390
27390
37833
65893
102239
102239
107991
113744
270987
294000
297564
408000
538000
562000
658000
680000
680000
700000
767000
1064000
3244000
8873000
8873000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.0
.0
.0
.5
.0
.5
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NC
NE
NC
NE
NC
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
* *
* *
NE
* *
NE
NE
NE
NE
NE
NE
NE
NE
* *
NE
NUMCODE=312 CHEM=
SAMPTYP=:
RATIO SITE SAMPLE
4 SR-3-06
2 BR-1-09
0.2 2 BR-1-07
3 SR-1-10
0.3 2 BR-1-08
4 SR-3-02
0.5 2 BR-1-03
4 SR-3-05
4 SR-3-08
GL-NERM-50% NO EFFECT
4 SR-3-16
GL-TEL-SR(ERL*NERM)
3 SR-1-03
1.3 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
TEL-SR(ERL*NERM)
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
4 SR-3-24
7 MR-l-CO
7 MR-1-01
2 BR-1-01
GL-NEC-MAX NO EFFECT
GL-PEL-SR(ERM*NERH)
4.7 1 IH-1-04
7.3 1 IH-1-06
GL-ERM-50% EFFECT
ERM-50% EFFECT
8.1 1 IH-1-03
PEL-SR(ERM*NERH)
8 CF-1-05
21.3 1 IH-1-07
8 CF-1-03
7 MR-1-02
8 CF-1-04
7 MR-1-17
7 MR-1-07
NERH-85% NO EFFECT
8 CF-1-02
7 MR-1-19
7 MR-1-25
6.1 7 MR-1-11
8 CF-1-01
NEC-MAX NO EFFECT
saiment - sen
TOXIC SURV
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
103.
105.
47.
90.
38.
100.
62.
104.
95.
102.
104.
18.
100.
100.
100.
100.
107.
100.
102.
100.
117.
67.
2.
0.
2.
96.
0.
84.
113.
109.
122.
116.
79.
111.
138.
70.
95.
3
0
9
3
0
6
8
9
1
7
5
7
0
0
0
0
4
0
2
0
9
8
0
0
7
3
0
0
4
9
4
4
0
9
8
2
1
1 UJNJ.1.
TOXS
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
is-ng,
GROW
11
10
10
10
97
12
87
11
11
12
10
52
10
10
10
10
11
10
11
10
11
10
ND
ND
ND
11
ND
10
11
11
12
11
11
10
11
75
13
ig
TOXG
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
79
CHEM=Zinc
28600
45000
51700
51800
52500
52500
52500
52500
55700
56300
69800
99000
120000
123000
124000
127000
143000
150000
159000
162500
166000
166300
195000
207000
219000
248822
271000
280832
286000
315000
347000
352000
359500
365000
367000
381000
381000
381000
410000
410000
463000
490000
541000
625000
631000
636000
734000
820000
854000
854000
899374
900000
900000
911000
942000
960000
1100000
1300000
1532481
1600000
1600000
2250000
2250000
2750000
3250000
4200000
4460000
7960000
10090000
10090000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NC
NE
NC
NE
NC
NE
NE
NE
NE
*
* *
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
* *
* *
**
* *
NE
8
5
7
7
4
3
1
2
8
4
4
3
1.4 5
5
2
0.4 2
4
0.5 2
.
4
0.8 2
4
3
8
4
2.3 3
4.9 5
4
7
8
7
8
.
7
2
.
8
7
.
7
42.9 1
,
.
61.9 1
6.6 7
85.0 1
151.6 1
8
CF-1-06
WH-l-CO
MR-1-01
MR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
CF-l-CO
SR-3-06
SR-3-01
SR-1-10
— slcl—
-~telf~-
— telm —
WH-1-01
WH-l-RE
— erl—
BR-1-09
GL-NERM-50% NO EFFECT
BR-1-08
SR-3-02
BR-1-07
NERM-50% NO EFFECT
SR-3-05
GL-TEL-SR (ERL*NERM)
— pelm —
TEL-SR(ERL*NERM)
BR-1-03
-—pelf—
SR-3-08
SR-1-03
GL-NERH-85% NO EFFECT
CF-1-05
SR-3-16
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
— erm —
— aet3 —
WH-1-02
— — clG U o~*~*
SR-3-24
MR-1-02
CF-1-03
MR-1-19
CF-1-04
— slc2~~
MR-1-07
NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
BR-1-01
GL-NEC-MAX NO EFFECT
CF-1-02
MR-1-17
— aetl —
— aet5 —
MR-1-25
PEL-SR(ERM*NERH)
— aet4 —
— aet2 —
IH-1-04
GL-ERM-50% EFFECT
ERM- 50% EFFECT
IH-1-03
MR-1-11
IH-1-06
IH-1-07
CF-1-01
NEC-MAX NO EFFECT @
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
107.4
100.0
117.9
100.0
100.0
100.0
100.0
100.0
100.0
103.3
96.7
90.3
8.6
85.7
105.0
.
38.0
100.6
47.9
.
104.9
62.8
95.1
104.5
96.3
102.7
18.7
.
.
.
51.4
.
102.2
113.4
84.0
111.9
109.9
116.4
67.8
79.0
122.4
138.8
.
2.0
.
.
2.7
70.2
0.0
0.0
95.1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
11
ND
11
10
10
10
10
10
10
11
10
10
ND
ND
10
97
12
10
11
87
11
10
11
12
52
ND
11
11
10
10
11
11
10
11
12
11
ND
ND
75
ND
ND
13
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
TX
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC EFFE<
0
0
0
0
0
0
0
1
1
2
2
2
2
3
3
3
3
3
3
3
5
6
6
6
9
9
10
10
10
13
19
19
28
29
40
49
49
50
50
52
55
60
135
166
183
187
1081
2630
2630
.9
.9
.9
.9
.9
.9
.9
.3
.3
.0
.3
.4
.9
.9
.9
.9
.9
.9
.9
.9
.0
.3
.3
.3
.8
.8
.6
.7
.7
.9
.0
.9
.0
.2
.4
.6
.6
.7
.7
.9
.2
.8
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
* *
NE
NE
NE
NE
**
NE
**
NE
NE
NE
*
**
NE
revsdtt
'OXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
»r unir:
SDRV
67.8
90.3
104.5
105.0
38.0
47.9
62.8
96.7
107.4
95.1
100.6
100.0
100.0
100.0
100.0
100.0
s-ug/ .
TOXS
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
L
GROW
10
10
10
10
97
10
87
10
11
11
12
10
10
10
10
10
TOXG
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
N0MCODE=312 CHEM=Zinc TEST=CR14 SAMPTYP=porewater
2 BR-1-01
3 SR-1-10
3 SR-1-03
2 BR-1-09
0.5 2 BR-1-08
0.5 2 BR-1-07
0.5 2 BR-1-03
4 SR-3-01
GL-NERM-50% NO EFFECT
8 CF-1-06
4 SR-3-08
4 SR-3-02
GL-TEL-SR(ERL*NERM)
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
TEL-SR(ERL*NERM)
1.6 1 IH-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
7 MR-l-CO
7 MR-1-01
7 MR-1-02
4 SR-3-06
GL-NEC-MAX NO EFFECT
GL-PEL-SR (ERM*NERH)
9.9 3 SR-1-06
8 CF-1-05
8 CF-1-04
7 MR-1-07
8 CF-1-03
12.7 1 IH-1-04
GL-ERM-50% EFFECT
7 MR-1-17
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
ERM-50% EFFECT
15.6 1 IH-1-03
7 MR-1-25
8 CF-1-02
7 MR-1-19
3.1 7 MR-1-11
277.2 1 IH-1-07
8 CF-1-01
NEC-MAX NO EFFECT
80
TOX
0.0 TX ND ND
ND
ND
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
100
117
113
103
18
96
109
116
84
2
122
2
138
79
111
70
0
95
.0
.9
.4
.3
.7
.3
.9
.4
.0
.0
.4
.7
.8
.0
.9
.2
.0
.1
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
10
11
11
11
52
11
11
11
10
ND
12
ND
11
11
10
75
ND
13
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
TX
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a:
NE
ASCENDING DATA TABLES (ALL DATA)
INCLUDES NBS AND OTHER (— 1
no effect I NC<1 I NG=1 I SG 1-2
NORMALIZED TO DRY WEIGHT
SECs
I * 2-4 I **>4
81
CONC I
1830.0
2549.0
3465.0
3595.0
4707.0
5360.0
6668.0
7060.0
9086.5
10762.2
11113.0
11113.0
11767.0
11902.0
12093.0
12747.0
12747.0
12747.0
14000.0
14000.0
14000.0
14000.0
14000.0
14000.0
14000.0
17388.0
17388.0
17388.0
27390.0
34306.3
34306.3
65893.0
84066.0
84066.0
102239.0
113744.0
JJJU-UJ
3FFEI
NE
NC
NC
NE
NC
NE
NC
NC
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
* *
* *
* *
297564.0
NUMCODE=312 CHEM=Zinc TEST=HA14 SAMPTYP=bottom sediment - sem UNITS=ng/g
4 SR-3-06
0.2 2 BR-1-09
0.2 2 BR-1-07
3 SR-1-10
0.3 2 BR-1-08
4 SR-3-02
0.5 2 BR-1-03
0.7 4 SR-3-05
GL-NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM) @
4 SR-3-08
NERM-50% NO EFFECT
4 SR-3-16
TEL-SR(ERL'NERM) @
3 SR-1-03
1.3 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
4 SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
2.0 2 BR-1-01
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
4.7 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
7.3 1 IH-1-06
8.1 1 IH-1-03
21.3 1 IH-1-07
saimeni. - sera
?OXIC SURV
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
111
83
86
101
113
105
77
104
110
111
115
12
100
100
100
100
100
.8
.4
.4
.6
.7
.9
.3
.5
.4
.8
.6
.5
.0
.0
.0
.0
.0
1 UJNJ..
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
is-ng/
GROW
94
90
85
10
85
10
85
94
10
10
95
87
ND
10
JLO
10
10
rg
TOXG
NT
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
MATURE TOXM
74
0.
0.
33
22
51
68
22
61
16
23
0.
ND
10
10
10
10
NT
TX
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
NOT
TOX
TOX
TOX
TOX
TOX
113.3 NT
10
100.0 NT 85
NT
TX
0.0 TX ND ND
1.4 TX
1.4 TX
0.0 TX
68
96
ND
NT
NT
ND
14
0.
ND
0.
0.
ND
NT
TX
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=312 CHEM=Zinc TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
82
40000.0
45000.0
45400.0
52500.0
52500.0
52500.0
52500.0
52500.0
52600.0
55200.0
55750.0
56300.0
69800.0
94150.1
99000.0
99000.0
120000.0
123000.0
124000.0
125463:1
127000.0
143000.0
150000.0
159000.0
159000.0
159000.0
166000.0
166300.0
195000.0
219000.0
271000.0
286000.0
315000.0
347000.0
349500.0
352000.0
352000.0
367000.0
381000.0
384043.0
385414.1
410000.0
410000.0
422000.0
422000.0
463000.0
490000.0
541000.0
541000.0
541000.0
820000.0
900000.0
960000.0
1100000.0
1600000.0
1600000.0
2250000.0
3250000.0
4460000.0
7960000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
it
NE
*
NC
if *
NE
NE
NE
*
**
NE
**
**
•*•*
**
**
.
.
.
1.4
.
3.0
.
3.2
3.7
1.0
.
5.4
.
.
.
.
.
2.3
.
.
4.9
.
,
.
.
17.1
.
.
.
42.9
61.9
85.0
151.6
9
5
9
9
4
3
1
2
9
9
.
4
4
3
5
5
2
2
4
2
4
2
4
3
4
3
5
.
4
.
2
.
1
1
1
1
TR-1-01
WH-l-CO
TR-1-03
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-04
TR-1-02
NERM-50% NO EFFECT
SR-3-06
SR-3-01
TEL-SR(ERL*NERM)
SR-1-10
GL-NERM-50% NO EFFECT
— slcl—
— telf—
— telm —
GL-TEL-SR (ERL*NERM)
WH-1-01
WH-l-RE
— erl—
BR-1-09
GL-ERL-15% EFFECT
ERL- 15% EFFECT
BR-1-08
SR-3-02
BR-1-07
SR-3-05
— pelm —
BR-1-03
—pelf—
SR-3-08
NERH-85% NO EFFECT
SR-1-03
GL-NERH-85% NO EFFECT
SR-3-16
SR-1-06
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— erm —
— aet3 —
GL-ERM-50% EFFECT
ERM-50% EFFECT
WH-1-02
— aet6 —
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— Slc2 —
BR-1-01
— aetl —
— aet5 —
— aet4 —
— aet2 —
IH-1-04
IH-1-03
IH-1-06
IH-1-07
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
100.0
100.0
87.5
100.0
100.0
100.0
100.0
100.0
93.4
100.0
.
111.8
116.2
101.6
35.0
100.0
83.4
.
113.7
105.9
86.4
104.5
.
77.3
110.4
115.6
111.8
12.5
40.0
113 l3
.
.
100.0
.
0.0
1.4
1.4
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
TX
TX
TX
TX
ND
10
ND
ND
10
10
10
10
ND
ND
94
10
10
13
14
90
85
10
85
94
85
10
95
10
87
11
10
85
ND
96
68
ND
ND
NT
ND
ND
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
ND
ND
ND
ND
ND
10
10
10
10
ND
ND
74
12
33
ND
ND
0.
22
51
0.
22
68
61
23
16
0.
ND
14
0.
ND
0.
0.
ND
ND
ND
ND
ND
NT
NT
NT
NT
ND
ND
NT
NT
NT
ND
ND
TX
TX
NT
TX
TX
NT
NT
NT
NT
NT
ND
NT
TX
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 83
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=312 CHEM=Zinc TEST=HA14 SAMPTYP=porewater UNITS=ug/l
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0.9 NC 0.2 2 BR-1-01 TOX 100.0 NT 85 TX 0. TX
0.9 NE . 3 SR-1-10 NOT 101.6 NT 10 NT 33 NT
0.9 NE . 3 SR-1-03 NOT 115.6 NT 95 NT 23 NT
0.9 NC 0.2 2 BR-1-09 TOX 83.4 NT 90 TX 0. TX
0.9 NC 0.2 2 BR-1-08 TOX 113.7 NT 85 TX 22 TX
0.9 NC 0.2 2 BR-1-07 TOX 86.4 NT 85 TX 0. TX
0.9 NC 0.2 2 BR-1-03 TOX 77.3 TX 85 TX 68 NT
1.3 NE . 4 SR-3-01 NOT 116.2 NT 10 NT 12 NT
1.3 . GL-NERM-50% NO EFFECT
1.8 . . NERM-50% NO EFFECT
2.3 NE . 4 SR-3-08 NOT 110.4 NT 10 NT 61 NT
2.4 NE . 4 SR-3-02 NOT 105.9 NT 10 NT 51 NT
2.9 . GL-TEL-SR(ERL*NERM)
3.4 . . TEL-SR(ERL*NERM) @
3.9 NE . 9 TR-l-CO NOT 100.0 NT ND ND ND ND
3.9 NE . 4 SR-3-CO NOT 100.0 NT 10 NT 10 NT
3.9 NE . 3 SR-l-CO NOT 100.0 NT 10 NT 10 NT
3.9 NE . 1 IH-l-CO NOT 100.0 NT 10 NT 10 NT
3.9 NE . 2 BR-l-CO NOT 100.0 NT 10 NT 10 NT
3.9 . . NERH-85% NO EFFECT
3.9 . GL-NERH-85% NO EFFECT
6.3 SG 1.6 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
6.3 . GL-ERL-15% EFFECT
6.3 . . ERL-15% EFFECT
10.7 NE . 4 SR-3-06 NOT 111.8 NT 94 NT 74 NT
10.7 . . NEC-MAX NO EFFECT
10.7 . . GL-NEC-MAX NO EFFECT
13.9 . PEL-SR(ERM*NERH)
13.9 . . GL-PEL-SR(ERM*NERH)
19.0 ** 9.9 3 SR-1-06 TOX 12.5 TX 87 NT 0. NT
49.6 ** 12.7 1 IH-1-04 TOX 0.0 TX ND ND ND ND
49.6 . . GL-ERM-50% EFFECT
49.6 . . ERM-50% EFFECT
60.8 ** 15.6 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
1081.0 ** 277.2 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
iNunuui
CONC EFFE<
1830
2549
3465
3595
4707
5360
6668
7060
11113
11113
11767
12093
12747
14000
14000
14000
14000
14000
14000
14000
14000
14000
17388
17388
17446
20000
20000
27390
27390
30372
37833
65893
65893
102239
102239
113744
294000
294000
297564
346340
408000
408000
538000
562000
658000
680000
700000
767000
1064000
1064000
3244000
8873000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.7
.1
.0
.0
.0
.0
.0
.0
.0
.0
.9
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NC
NC
NC
NE
NE
NC
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
*
**
**
**
NE
*•*
SG
NC
NE
SG
SG
NE
SG
NE
* *
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=312 CHEM=Zinc TEST=HA28 SAMPTYP=bottoro sediment - sem UNITS=
4 SR-3-06
0.3 2 BR-1-09
0.4 2 BR-1-07
0.3 3 SR-1-10
2 BR-1-08
4 SR-3-02
0.7 2 BR-1-03
4 SR-3-05
4 SR-3-08
GL-NERM-50% NO EFFECT
4 SR-3-16
0.9 3 SR-1-03
0.9 3 SR-1-06
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
4 SR-3-24
GL-NEC-MAX NO EFFECT
GL-TEL-SR (ERL*NERM)
7 MR-l-CO
0.0 7 MR-1-01
2.9 2 BR-1-01
GL-ERL-15% EFFECT
TEL-SR(ERL*NERM)
GL-PEL-SR(ERM*NERH)
4.7 1 IH-1-04
ERL-15% EFFECT
7.3 1 IH-1-06
GL-ERM-50% EFFECT
8.1 1 IH-1-03
8 CF-1-05
NERH-85% NO EFFECT
21.3 1 IH-1-07
PEL-SR(ERM*NERH)
1.3 8 CF-1-03
ERM-50% EFFECT
1.0 7 MR-1-02
8 CF-1-04
1.2 7 MR-1-17
1.3 7 MR-1-07
8 CF-1-02
1.4 7 MR-1-19
7 MR-1-25
NEC-MAX NO EFFECT
6.0 7 MR-1-11
28.0 8 CF-1-01
84
;uimei
'OXIC
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
it - sen
SURV
100.0
88.2
80.3
100.0
97.4
103.8
79.0
96.1
88.3
96.1
96.2
10.3
100.0
100.0
100.0
100.0
100.0
120.3
100.0
102.6
100.0
108.1
89.5
0.0
1.4
1.4
114.9
0.0
123.0
109.3
128.4
115.1
91.9
102.7
114.0
109.3
90.7
64.9
n UJMI.
TOXS
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
rs=ng/
GROW
92
92
85
97
10
10
85
94
92
10
91
60
ND
10
10
10
10
10
10
10
10
79
96
ND
68
96
98
ND
82
92
10
92
91
94
89
95
58
73
'g —
TOXG
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
ND
TX
TX
NT
TX
TX
NT
TX
NT
TX
TX
MATURE
96
10
10
10
10
10
10
11
95
95
10
37
ND
10
10
10
10
90
10
10
10
68
10
ND
0.
0.
77
ND
93
95
80
65
31
48
63
12
24
25
TOXM
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
ND
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=312 CHEM=Zinc TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
85
12000
28600
38000
40000
45000
45200
45400
46400
51700
51800
52500
52500
52500
52500
52500
52600
55200
55700
56300
57400
69800
70300
85150
97700
98091
99000
100000
106400
113000
116000
116244
117000
120000
123000
124000
127000
127000
134000
139000
143000
150000
159000
166000
166300
195000
201000
219000
260000
271000
286000
315000
347000
347000
352000
363602
365000
367000
381000
381000
410000
410000
463000
490000
541000
541000
541000
543991
547000
625000
631000
636000
694000
734000
820000
854000
900000
911000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
SG
NE
NE
NE
*
NE
**
NE
NE
**
**
NE
NC
SG
NC
NE
NE
SG
* *
NE
0.2 11
8
11
9
5
6
9
6
0.1 7
7
9
4
3
1
2
9
9
8
4
1.1 11
4
11
1.8 11
1.9 3
6
6
.
10
1.4 5
10
10
5
1.5 2
2
4
1.8 2
6
4
10
2.6 2
4
6.7 3
8
4
7.3 3
.
.
.
4.9 5
4
.
.
0.9 7
1.5 8
0.9 7
10
8
1.3 7
8.2 2
8
TB-1-01
CF-1-06
TB-l-RE
TR-1-01
WH-l-CO
UM-l-CO
TR-1-03
UM-l-RE
MR-1-01
MR-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-04
TR-1-02
CF-l-CO
SR-3-06
TB-1-02
SR-3-01
TB-1-04
NERM-50% NO EFFECT
TB-1-03
TEL-SR(ERL*NERM)
SR-1-10
UM-1-02
GL-NERM-50% NO EFFECT
ERL-15% EFFECT
UM-1-03
GL-TEL-SR (ERL*NERM)
MB-1-04
— slcl —
— telf—
— telm —
WH-1-01
GL-ERL-15% EFFECT
MB-l-RE
MB-1-02
WH-l-RE
— erl~
BR-1-09
BR-1-08
SR-3-02
BR-1-07
UM-1-01
SR-3-05
MB-1-03
— pelm —
BR-1-03
— pelf—
SR-3-08
GL-NERH-85% NO EFFECT
SR-1-03
GL-PEL-SR (ERM*NERH)
CF-1-05
SR-3-16
SR-1-06
GL-ERM-50% EFFECT
— erm —
— aet3 —
WH-1-02
— aet6 —
SR-3-24
NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
ERM- 50% EFFECT
MR-1-02
CF-1-03
MR-1-19
MB-1-01
CF-1-04
— slc2 —
MR-1-07
BR-1-01
CF-1-02
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
0
120
100
81
100
100
98
86
108
100
100
100
100
100
100
82
100
100
100
11
97
93
52
100
117
114
95
71
100
97
109
88
97
103
80
119
96
95
79
88
96
114
96
10
36
102
109
123
114
75
128
91
89
102
.0
.3
.0
.4
.0
.0
.6
.5
.1
.0
.0
.0
.0
.0
.0
.9
.0
.0
.0
.4
.4
.2
.3
.0
.9
.9
.5
.7
.0
.0
.5
.2
.4
.8
.3
.3
.1
.5
.0
.3
.2
.9
.1
.3
.
.5
.6
.3
.0
.0
.8
.4
.9
.5
.7
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
ND
10
10
ND
10
ND
ND
ND
79
10
ND
10
10
10
10
ND
ND
10
92
72
94
10
97
97
ND
ND
ND
91
ND
ND
11
92
10
10
85
ND
94
ND
85
92
91
98
10
60
74
10
92
82
89
ND
10
91
96
94
ND
NT
NT
ND
NT
ND
ND
ND
TX
NT
ND
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
NT
TX
ND
ND
ND
NT
ND
ND
NT
NT
NT
NT
TX
ND
NT
ND
TX
NT
TX
NT
NT
TX
TX
NT
TX
TX
TX
ND
NT
TX
NT
NT
ND
90
ND
ND
ND
ND
ND
ND
68
10
ND
10
10
10
10
ND
ND
10
96
ND
11
ND
ND
10
ND
ND
ND
ND
ND
ND
ND
10
10
10
10
ND
11
ND
10
95
10
77
95
37
ND
10
95
93
63
ND
80
31
10
48
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
ND
ND
NT
NT
ND
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
ND
NT
TX
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
^bottom sediment - total ONITS=ng/g
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
86
IMl
JMl,ULIC=JJ.
CONG EFFECT
942000,
960000.
1100000,
1300000,
1300000,
1600000,
1600000,
2250000,
3250000
4200000,
4460000
7960000
10090000
. 0 SG
.0
.0
.0 NE
.0
.0
.0
.0 **
.0 **
.0 **
.0 **
.0 **
.0 **
L (_nCJM
-^j
LHC
RATIO SITE
1.
.
.
42.
61.
6.
85.
151.
24.
4
9
9
2
0
6
1
7
.
7
1
1
7
1
1
8
TC.&i-nAio s«jnriir=ooi
(continued)
SAMPLE
MR-1-17
— aetl —
— aetS —
MR-1-25
NEC -MAX NO EFFECT
— aet4 —
— aet2 —
IH-1-04
IH-1-03
MR-1-11
IH-1-06
IH-1-07
CF-1-01
TOX 115.1 NT 92 TX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
109.3 NT 95
0.0 TX
1.4 TX
NT
TX
TX
90.7
1.4
0.0
64.9
TX
ND
96
58
68
ND
73
NT
ND
NT
TX
NT
ND
TX
65
12
ND
0.
24
0.
ND
25
NT
NT
ND
NT
TX
NT
ND
TX
-------
CONC 1
0.9
0.9
0.9
0.9
0.9
0.9
0.9
1.3
1.3
2.0
2.3
2.4
2.9
3.9
3.9
3.9
3.9
3.9
3.9
3.9
3.9
6.3
6.3
8C
. D
9.8
9.8
10.6
10.7
10.7
13.9
19.0
19.0
19.9
28.0
29.2
29.2
40.4
49.6
49.6
50.7
59.7
60.8
121.9
135.0
166.0
166.0
183.0
187.0
1081.0
2630.0
!FFE(
NC
NC
NC
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NC
NE
* *
NE
NE
NC
NC
* *
NC
**
NE
NE
*
*
**
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=312 CHEM=Zinc TEST=HA28 SAMPTYP=porewater
IT RATIO SITE SAMPLE CEK
0.4 2 BR-1-01
0.2 3 SR-1-10
0.2 3 SR-1-03
0.4 2 BR-1-09
2 BR-1-08
0.4 2 BR-1-07
0.4 2 BR-1-03
4 SR-3-01
GL-NERM-50% NO EFFECT
8 CF-1-06
4 SR-3-08
4 SR-3-02
GL-TEL-SR(ERL*NERM) @
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
GL-NERH-85% NO EFFECT
1.6 1 IH-1-06
GL-ERL-15% EFFECT
TEL-SR(ERL*NERM)
7 MR-l-CO
0.1 7 MR-1-01
0.1 7 MR-1-02
4 SR-3-06
GL-NEC-MAX NO EFFECT
GL-PEL-SR(ERM'NERH)
4.9 3 SR-1-06
ERL-15% EFFECT
8 CF-1-05
8 CF-1-04
0.4 7 MR-1-07
NERH-85% NO EFFECT
0.9 8 CF-1-03
12.7 1 IH-1-04
GL-ERM-50% EFFECT
0.7 7 MR-1-17
PEL-SR(ERM*NERH)
15.6 1 IH-1-03
ERM-50% EFFECT
7 MR-1-25
8 CF-1-02
NEC-MAX NO EFFECT
2.5 7 MR-1-19
2.6 7 MR-1-11
277.2 1 IH-1-07
59.8 8 CF-1-01
87
. e?waLt:.L UIMXJ.D
?OXIC StJRV
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
89.
100.
96.
88.
97.
80.
79.
97.
120.
88.
103.
100.
100.
100.
100.
100.
100.
1.
100.
108,
109,
100.
10,
114,
128,
91,
123,
0,
115.
1.
109,
102.
114.
90,
0,
64.
.5
,0
.2
.2
.4
.3
,0
.4
,3
,3
.8
,0
,0
,0
,0
,0
,0
,4
.0
.1
.3
.0
.3
.9
.4
.9
.0
.0
.1
.4
.3
.7
.0
.7
.0
.9
=ug/ j
TOXS
TX
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
TX
TX
L
GROW
96
97
91
92
10
85
85
94
10
92
10
ND
10
10
10
10
10
68
10
79
92
92
60
98
10
91
82
ND
92
96
95
94
89
58
ND
73
TOXG
NT
TX
TX
NT
NT
TX
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
TX
TX
ND
TX
NT
NT
NT
TX
TX
ND
TX
MATURE
10
10
10
10
10
10
10
11
90
95
10
ND
10
10
10
10
10
0.
10
68
95
96
37
77
80
31
93
ND
65
0.
12
48
63
24
ND
25
TOXM
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
TX
ND
TX
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I •«*>4
88
IN urauui
CONC
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
14.0
15.0
15.0
16.0
16.0
16.0
17.0
21.0
21.5
22.0
24.0
28.0
29.0
34.4
34.6
35.0
39.0
42.0
55.0
55.0
59.0
99.5
126.2
140.0
160.0
160.0
160.0
160.0
180.0
200.0
230.0
250.0
250.0
250.0
270.0
280.0
290.0
391.0
470.0
687.4
1004.0
1890.0
2100.0
2100.0
2100.0
2400.0
2700.0
3600.0
3600.0
5000.0
6600.0
7300.0
8500.0
20000.0
20000.0
20000.0
46000.0
jr*=^u<* »_
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
*
NC
NC
* *
NE
**
NE
NE
NE
NE
NE
NE
NC
**
**
**
* *
NE
nrjS^iNdl
RATIO
.
2.0
3.2
.
0.0
0.0
7.1
.
8.0
.
.
.
.
.
.
0.1
.
.
360.0
500.0
730.0
850.0
.
in urza..
SITE
3
4
3
1
8
8
8
2
8
8
7
8
5
7
7
7
7
7
8
7
5
.
3
7
2
3
2
2
5
4
5
4
4
4
4
4
4
2
.
.
1
1
1
1
2
Lene i jaiM — URJ. f* aAnrrir=jj<
SAMPLE
SR-1-10
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
CF-1-06
CF-1-04
BR-l-CO
CF-1-03
CF-1-05
MR-1-02
CF-1-02
WH-l-CO
MR-1-07
MR-1-01
MR-l-CO
MR-1-19
NERM-50% NO EFFECT
MR-1-17
CF-1-01
MR-1-25
WH-l-RE
TEL-SR (ERL*NERM)
— telm —
SR-1-03
MR-1-11
BR-1-09
SR-1-06
ERL-15% EFFECT
BR-1-08
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
BR-1-07
WH-1-01
SR-3-06
GL-ERL-15% EFFECT
— erl —
WH-1-02
SR-3-05
SR-3-16
SR-3-08
SR-3-02
NERH-85% NO EFFECT
SR-3-01
GL-NERH-85% NO EFFECT
SR-3-24
— pelm —
BR-1-03
PEL-SR(ERM'NERH)
GL-PEL-SR (ERM*NERH)
ERM-50% EFFECT
— erm —
— aet4 —
— aet2 —
— aetl —
— aet3 —
IH-1-04
GL-ERM-50% EFFECT
IH-1-07
— aet6 —
IH-1-03
IH-1-06
BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— aet5 —
o eia.Lu.Ksi t 1_ — i_
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
90
100
100
100
100
107
109
100
84
96
113
79
100
116
117
100
111
122
95
138
85
104
70
105
18
38
47
8
103
51
104
102
95
100
96
102
62
.3
.0
.0
.0
.0
.4
.9
.0
.0
.3
.4
.0
.0
.4
.9
.0
.9
.4
.1
.8
.7
.5
.2
.0
.7
.0
.9
.6
.3
.4
.9
.7
.1
.6
.7
.2
.8
UUO.A.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
uiN J. i ;
GROW
10
10
10
10
10
11
11
10
10
11
11
11
ND
11
11
10
10
12
13
11
ND
10
75
10
52
97
10
ND
11
ND
11
12
11
12
10
11
87
5=ny / g
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
TX
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
TX
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
TOX
TOX
TOX
NOT
2.0 TX ND
0.0 TX ND
ND
ND
2.7 TX ND ND
0.0 TX ND ND
67.8 NT 10 NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NDMCODE=404 CHEM=Naphthalene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
89
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
16.0
19.5
23.0
29.0
32.7
34.6
35.0
35.0
42.0
43.9
55.0
55.0
55.0
59.0
140.0
160.0
160.0
160.0
180.0
200.0
230.0
250.0
250.0
250.0
250.0
270.0
285.0
285.0
290.0
290.0
290.0
325.0
325.0
391.0
470.0
2100.0
2100.0
2100.0
2400.0
2700.0
3600.0
5000.0
6600.0
7300.0
8500.0
20000.0
46000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
*
* *
**
* *
NE
* *
NC
NE
NE
NE
NE
NE
* *
**
**
**
**
**
.
.
4.2
3.2
.
5.9
14.0
7.1
.
8.0
1.0
.
.
47.0
360.0
500.0
730.0
850.0
2000.0
.
3
9
9
9
9
4
3
1
2
5
9
5
3
2
.
3
2
2
5
4
5
4
4
4
4
4
4
.
2
.
.
.
.
.
1
1
.
1
1
2
.
SR-1-10
TR-l-CO
TR-1-03
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
WH-l-CO
NERM-50% NO EFFECT
TR-1-04
WH-l-RE
TEL-SR(ERL*NERM)
— telm —
SR-1-03
GL-NERM-50% NO EFFECT
BR-1-09
GL-TEL-SR (ERL*NERM)
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-08
BR-1-07
WH-1-01
SR-3-06
— erl —
WH-1-02
SR-3-05
SR-3-16
SR-3-08
SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-01
PEL-SR (ERM*NERH)
GL-PEL-SR (ERM*NERH)
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
— pelm —
BR-1-03
— erro —
— aet4 —
— aet2 —
— aetl —
— aet3— -
IH-1-04
IH-1-07
— aet6 —
IH-1-03
IH-1-06
BR-1-01
— aet5—
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
101.6
100.0
87.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
.
93.4
100.0
.
.
115.6
83.4
12.5
113.7
86.4
35.0
111.8
40.0
104.5
111.8
110.4
105.9
116.2
113.3
77.3
.
.
.
0.0
0.0
.
1.4
1.4
100.0
.
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
10
ND
ND
ND
ND
10
10
10
10
10
ND
14
95
90
87
85
85
13
94
11
94
10
10
10
10
10
85
ND
ND
96
68
85
NT
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
NT
TX
33
ND
ND
ND
ND
10
10
10
10
ND
ND
ND
23
0.
0.
22
0.
ND
74
ND
22
16
61
51
12
14
68
ND
ND
0.
0.
0.
NT
ND
ND
ND
ND
NT
NT
NT
NT
ND
ND
ND
NT
TX
NT
TX
TX
ND
NT
ND
TX
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
-------
in unuujj
CONC
0.0
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
13.0
13.0
14.0
14.6
15.0
15.0
16.0
16.0
16.0
16.0
16.5
17.0
20.0
21.0
22.0
23.0
24.0
24.0
28.0
29.0
30.0
34.0
34.6
35.0
39.0
39.0
40.0
42.0
42.0
49.8
55.0
59.0
59.0
60.0
97.5
110.0
139.6
140.0
160.0
160.0
160.0
180.0
200.0
200.0
230.0
250.0
250.0
250.0
270.0
285.0
290.0
290.0
325.0
391.0
470.0
1400.0
1400.0
2100.0
2100.0
2100.0
n=*iU'
EFFEI
NE
NC
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NE
NE
NE
NC
NC
NE
NE
NC
NC
NE
NE
*
NE
NE
NE
NE
*
SG
NE
* *
SG
* *
NE
NE
NE
**
* *
NE
**
NE
NE
NE
NE
NE
NE
* *
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=404 CHEM=Naphthalene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
90
11 TB-l-RE
0.6 3 SR-1-10
9 TR-l-CO
9 TR-1-03
9 TR-1-02
9 TR-1-01
11 TB-1-04
2.0 11 TB-1-03
2.0 11 TB-1-01
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-04
2 BR-l-CO
6 UM-l-RE
1.1 8 CF-1-03
ERL-15% EFFECT
8 CF-1-05
TEL-SR(ERL*NERM)
0.7 7 MR-1-02
8 CF-1-02
5 WH-l-CO
6 UM-l-CO
0.7 7 MR-1-07
0.7 7 MR-1-01
NERM-50% NO EFFECT
7 MR-l-CO
6 UM-1-02
0.9 7 MR-1-19
1.0 7 MR-1-17
9 TR-1-04
6 UM-1-03
2.0 8 CF-1-01
7 MR-1-25
5 WH-l-RE
6 UM-1-01
10 MB-1-03
—telm—
3.5 3 SR-1-03
1.7 7 MR-1-11
10 MB-1-04
8.0 11 TB-1-02
1.2 2 BR-1-09
GL-ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
5.5 3 SR-1-06
2 BR-1-08
GL-NERM-50% NO EFFECT
10 MB-l-RE
ERM-50% EFFECT
10 MB-1-02
PEL-SR(ERM'NERH)
4.1 2 BR-1-07
7,1 5 WH-1-01
4 SR-3-06
——er'l ——
8.0 5 WH-1-02
4 SR-3-05
NERH-85% NO EFFECT
4 SR-3-16
4 SR-3-08
4 SR-3-02
GL-NERH-85% NO EFFECT
4 SR-3-01
GL-PEL-SR (ERM*NERH)
4 SR-3-24
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
—pelm—
13.6 2 BR-1-03
10 MB-1-01
NEC-MAX NO EFFECT
—erm—
—aet4—
—aet2—
t <0^U..L.J
TOXIC
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
,IIC1*1-
SU1
100.
100.
100.
98.
100.
81.
93.
52.
0.
100.
100.
100.
100.
120.
128.
100.
86.
123.
114.
109.
102.
100.
100.
91.
108.
100.
117.
114.
115.
82.
114.
64.
109.
109.
119.
95.
96.
90.
95.
11.
88.
10.
97.
100.
97.
80.
71.
100.
36.
96.
96.
88.
103.
97.
102.
79.
75.
I
*V
.0
.0
,0
.6
,0
.4
2
3
.0
0
0
0
0
3
4
0
5
0
9
3
7
0
0
9
1
0
9
0
1
9
9
9
3
5
3
5
2
7
5
4
2
3
4
0
0
3
7
0
5
1
1
3
8
4
6
0
8
-vuaj.
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
U1NA 1
GROW
10
97
ND
ND
ND
ND
10
97
ND
10
10
10
10
10
10
10
ND
82
98
92
94
10
ND
91
79
10
ND
89
92
ND
ND
73
95
11
ND
ND
91
58
ND
72
92
60
10
ND
ND
85
91
92
74
94
10
92
10
94
10
85
ND
o-jig/ t
TOXG
NT
TX
ND
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
TX
NT
TX
NT
NT
ND
TX
TX
NT
ND
TX
TX
ND
ND
TX
NT
NT
ND
ND
TX
TX
ND
TX
NT
TX
NT
ND
ND
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
ND
1
MATURE
ND
10
ND
ND
ND
ND
ND
ND
ND
10
10
10
10
90
80
10
ND
93
77
95
48
ND
ND
31
68
10
ND
63
65
ND
ND
25
12
ND
ND
ND
10
24
ND
ND
10
37
10
ND
ND
10
ND
96
ND
11
95
95
10
11
10
10
ND
! TOXM
ND
NT
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
ND
TX
NT
NT
ND
NT
NT
ND
ND
TX
NT
ND
ND
ND
NT
TX
ND
ND
NT
TX
NT
ND
ND
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=404 CHEM=Naphthalene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
91
CONC EFFECT
2400.0
2700.0
3600.0
5000.0
6600.0
7300.0
8500.0
20000.0
46000.0
RATIO SITE SAMPLE
CEN TOXIC
SURV TOXS GROW TOXG MATURE TOXM
360,
500
730
850,
579,
.0
.0
.0
.0
.7
1
1
1
1
2
— aet3 —
IH-1-04
IH-1-07
— aet6 —
IH-1-03
IH-1-06
BR-1-01
— aet5 —
TOX
TOX
TOX
TOX
TOX
0.
0.
1.
1.
89.
,0
.0
.4
.4
,5
TX
TX
TX
TX
TX
ND
ND
96
68
96
ND
ND
NT
NT
NT
ND
ND
0.
0.
10
ND
ND
NT
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=408 CHEM=Fluorene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
92
7.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
19.0
19.0
21.2
29.7
38.0
46.0
50.0
69.0
88.0
88.0
88.0
91.4
95.0
140.0
144.0
160.0
200.0
230.0
250.0
250.0
250.0
270.0
280.0
290.0
400.0
540.0
540.0
540.0
600.0
651.9
689.9
790.0
1000.0
1700.0
1700.0
1700.0
1800.0
1800.0
1800.0
2400.0
3200.0
3600.0
61000.0
84000.0
NE
NE
NE
NE
NE
NE
NE
NE
NG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
*
* *
NC
NE
NE
NE
NE
NE
NE
NE
NC
**
* *
NE
* *
**
* *
1.0
.
.
.
,
.
0.1
3.8
6.1
.
0.2
0.6
79.0
.
117.2
.
.
240.0
320.0
6100.0
3
5
4
3
7
7
7
7
7
7
7
7
1
8
8
8
8
8
8
8
2
5
3
2
2
3
5
2
4
4
4
4
4
4
4
2
1
5
.
2
.
1
1
1
SR-1-10
WH-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-25
MR-1-19
MR-1-17
MR-1-11
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
CF-1-01
BR-l-CO
NERM-50% NO EFFECT
WH-l-RE
— erl~
— telm—
TEL-SR(ERL*NERM)
SR-1-03
BR-1-09
BR-1-08
SR-1-06
WH-1-02
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR (ERL'NERM)
GL-NERM-50% NO EFFECT
BR-1-07
— pelm —
SR-3-06
SR-3-05
SR-3-16
SR-3-08
SR-3-02
NERH-85% NO EFFECT
SR-3-01
GL-NERH-85% NO EFFECT
SR-3-24
BR-1-03
— erm —
— aet4 —
— aet2 —
— aet6 —
PEL-SR (ERM*NERH)
GL-PEL-SR (ERM*NERH)
IH-1-04
— aet3 —
WH-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-01
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-03
IH-1-06
— aetl—
IH-1-07
— aet5 —
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
90
100
100
100
100
138
111
122
70
116
113
117
100
100
107
96
109
84
79
95
100
85
104
105
38
18
51
47
103
104
102
95
100
96
102
62
2
8
67
2
0
0
.3
.0
.0
.0
.0
.8
.9
.4
.2
.4
.4
.9
.0
.0
.4
.3
.9
.0
.0
.1
.0
.7
.5
.0
.0
.7
.4
.9
.3
.9
.7
.1
.6
.7
.2
.8
.0
.6
.8
.7
.0
.0
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
10
ND
10
10
10
11
10
12
75
11
11
11
10
10
11
11
11
10
11
13
10
ND
10
10
97
52
ND
10
11
11
12
11
12
10
11
87
ND
ND
10
ND
ND
ND
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (--) SECs
NE no f .ect [ NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=408 CHEM=Fluorene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
93
7.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
19.0
19.0
21.2
24.0
29.0
34.6
38.0
38.0
43.6
46.0
50.0
50.0
50.0
51.0
69.0
88.0
140.0
144.0
160.0
200.0
230.0
250.0
250.0
250.0
250.0
270.0
290.0
290.0
290.0
385.7
385.7
400.0
540.0
540.0
540.0
595.0
595.0
600.0
790.0
1000.0
1700.0
1800.0
2400.0
3200.0
3600.0
61000.0
84000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
* *
NE
*
* *
* *
NE
NC
NE
NE
NE
NE
NE
**
* *
* *
* *
**
**
* *
,
4.6
5.0
3.8
6.1
14.0
1.0
.
.
.
.
.
40.0
.
.
.
.
79.0
.
117.2
180.0
240.0
320.0
6100.0
3
5
9
9
9
4
3
1
2
5
9
.
3
2
2
9
3
5
2
4
4
4
4
4
4
4
.
.
2
1
5
2
1
1
1
.
SR-1-10
WH-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
WH-l-RE
— erl—
— telm —
NERM-50% NO EFFECT
TR-1-03
TEL-SR(ERL*NERM)
SR-1-03
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
BR-1-09
BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
TR-1-04
SR-1-06
WH-1-02
BR-1-07
— pelm —
SR-3-06
SR-3-05
SR-3-16
SR-3-08
SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-01
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
BR-1-03
— erm —
— aet4 —
— aet2 —
GL-ERM-50% EFFECT
ERM- 50% EFFECT
— aet6 —
IH-1-04
— aet3 —
WH-1-01
BR-1-01
IH-1-03
IH-1-06
— aetl —
IH-1-07
~aet5~
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
101.
100.
100.
100.
100.
100.
100.
100.
100.
100.
87.
115.
83.
113.
93.
12.
40.
86.
.
111.
104.
111.
110.
105.
.
116.
113.
77.
.
0.
35.
100.
1.
1.
0.
.
6
0
0
0
0
0
0
0
0
0
5
6
4
7
4
5
0
4
8
5
8
4
9
2
3
3
0
0
0
4
4
0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
TX
TX
10
10
ND
ND
ND
10
10
10
10
14
ND
95
90
85
ND
87
11
85
94
94
10
10
10
10
10
85
ND
13
85
96
68
ND
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
TX
TX
ND
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
TX
NT
NT
ND
33
ND
ND
ND
ND
10
10
10
10
ND
ND
23
0.
22
ND
0.
ND
0.
74
22
16
61
51
12
14
68
ND
ND
0.
0.
0.
ND
NT
ND
ND
ND
ND
NT
NT
NT
NT
ND
ND
NT
TX
TX
ND
NT
ND
TX
NT
TX
NT
NT
NT
NT
NT
NT
ND
ND
TX
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=408 CHEM=Fluorene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
94
0.0
7.0
7.0
9.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
16.0
18.0
19.0
19.0
21.2
29.0
31.0
38.0
46.0
46.0
48.0
50.0
50.0
51.0
69.0
88.0
100.0
100.0
130.0
140.0
140.0
144.0
149.7
160.0
160.0
200.0
230.0
250.0
250.0
250.0
270.0
290.0
290.0
385.7
400.0
540.0
540.0
540.0
595.0
600.0
790.0
1000.0
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
NE
NE
NE
NE
NG
NG
NG
NG
NG
NG
NE
NE
NE
NE
NE
NG
NE
NG
NE
NE
NE
NE
NE
NE
*
SG
NE
NE
* *
**
NE
NE
NE
**
NE
NE
NE
NE
NE
NE
NE
* *
* *
0
2
2
2
1
1
1
1
1
1
1
1
3
1
6
6
4
13
79
.7
.
.
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.
.8
.5
.9
.1
,
.7
.
.
.
.
.3
.
.
.0
11
6
3
6
5
6
9
9
9
11
11
11
11
4
3
7
7
7
7
7
7
7
7
1
8
8
8
8
8
8
8
2
6
6
5
.
9
10
3
2
2
9
3
5
10
10
10
2
.
4
4
4
4
4
4
4
2
.
1
TB-l-RE
UM-l-RE
SR-1-10
UM-1-01
WH-l-CO
UM-l-CO
TR-l-CO
TR-1-02
TR-1-01
TB-1-04
TB-1-03
TB-1-02
TB-1-01
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-25
MR-1-19
MR-1-17
MR-1-11
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
CF-1-01
BR-l-CO
TEL-SR (ERL*NERM)
NERM-50% NO EFFECT
ERL-15% EFFECT
UM-1-02
UM-1-03
WH-l-RE
— erl—
— telm —
TR-1-03
MB-1-03
SR-1-03
BR-1-09
GL-ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
BR-1-08
GL-NERM-50% NO EFFECT
TR-1-04
SR-1-06
WH-1-02
MB-1-04
MB-1-02
MB-l-RE
BR-1-07
ERM-50% EFFECT
— pelm —
PEL-SR(ERM*NERH)
SR-3-06
NERH-85% NO EFFECT
SR-3-05
SR-3-16
SR-3-08
SR-3-02
GL-NERH-85% NO EFFECT
SR-3-01
SR-3-24
GL-NEC-MAX NO EFFECT
GL-PEL-SR (ERM*NERH)
BR-1-03
— erm —
— aet4 —
— aet2 —
GL-ERM-50% EFFECT
--aet6 —
IH-1-04
— aet3 —
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
100.0
86.5
100.0
119.3
100.0
100.0
100.0
100.0
81.4
93.2
52.3
11.4
0.0
100.0
100.0
100.0
109.3
114.0
115.1
90.7
91.9
109.3
108.1
100.0
100.0
120.3
114.9
128.4
123.0
102.7
64.9
100.0
117.9
114.9
109.5
98.6
95.5
96.2
88.2
97.4
82.9
10.3
36.5
95.5
97.0
100.0
80.3
g
100.0
9e!i
96.1
88.3
103.8
97.4
102.6
.
79.0
.
.
,
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
10
ND
97
ND
10
ND
ND
ND
ND
10
97
72
ND
10
10
10
95
89
92
58
91
92
79
10
10
10
98
10
82
94
73
10
ND
ND
11
ND
ND
91
92
10
ND
60
74
ND
ND
ND
85
92
94
10
92
10
94
10
85
ND
NT
ND
TX
ND
NT
ND
ND
ND
ND
NT
NT
TX
ND
NT
NT
NT
NT
TX
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
ND
ND
NT
ND
ND
TX
NT
NT
ND
TX
TX
ND
ND
ND
TX
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
ND
10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
12
63
65
24
31
95
68
10
10
90
77
80
93
48
25
10
ND
ND
ND
ND
ND
10
10
10
ND
37
ND
ND
ND
ND
10
96
11
95
95
10
11
10
10
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
ND
ND
ND
NT
NT
NT
ND
TX
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
95
j\jurn.uijr;=^uo i_naJXL=r xuorene rnai— nA^o ;sAn.ri ir=uuucum seuiiueiiu - UUQCIJ. ui^-no^ny/ y
(continued)
CONC EFFECT
1700
1800
2400
3000
3000
3200
3600
61000
84000
.0 **
.0 **
.0 **
.0 NE
.0
.0 **
.0
.0 **
.0
RATIO
117.2
60.0
240.0
.
320.0
,
6100.0
SITE
5
2
1
10
1
1
SAMPLE
WH-1-01
BR-1-01
IH-1-03
MB-1-01
NEC -MAX NO
IH-1-06
— aetl —
IH-1-07
— aet5 —
CEN TOXIC
TOX
TOX
TOX
NOT
EFFECT
TOX
TOX
SURV
71.7
89.5
1.4
75.8
1.4
0.0
TOXS
TX
TX
TX
NT
TX
TX
GROW
91
96
96
ND
68
ND
TOXG
NT
NT
NT
ND
NT
ND
MATURE
ND
10
0.
ND
0.
ND
TOXM
ND
NT
NT
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=409 CHEM=Phenanthrene TEST=CR14 SAMPTYP=bottom sediment - total
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CP-1-05
8 CF-1-03
2 BR-l-CO
7 MR-1-25
8 CF-1-04
7 MR-1-17
8 CF-1-02
7 MR-1-07
7 MR-1-02
NERM-50% NO EFFECT
3 SR-1-10
—telf—
2.5 7 MR-1-11
7 MR-1-19
8 CF-1-01
—telm—
TEL-SR(ERL*NERM)
5 WH-l-RE
4 SR-3-06
-~erl-~
4 SR-3-01
3 SR-1-03
6.4 5 WH-1-02
ERL-15% EFFECT
3.1 3 SR-1-06
GL-ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
GL-NERM-50% NO EFFECT
4 SR-3-16
0.2 2 BR-1-08
4 SR-3-02
—pelf—
2 BR-1-09
—pelm—
4 SR-3-08
NERH-85% NO EFFECT
0.3 2 BR-1-07
4 SR-3-05
GL-NERH-85% NO EFFECT
4 SR-3-24
20.0 5 WH-1-01
PEL-SR(ERM*NERH)
0.6 2 BR-1-03
—erm—
—aet4—
—aet2—
GL-PEL-SR
-------
JMUJMI_UUB-«U:
CONC EFFEI
10
10
10
10
10
10
10
10
27
41
86
100
100
130
160
197
220
225
240
270
340
350
390
390
390
460
460
510
510
515
540
544
550
550
580
680
720
749
111
1000
1000
1000
1100
1100
1100
1400
1500
1500
1500
2200
2400
3400
5400
6100
6900
7000
9900
33000
182000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.9
.7
.0
.0
.0
.0
.5
.0
.2
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.8
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
*
NE
* *
NE
* *
NE
NE
* *
SG
NE
* *
* *
* *
* *
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—} SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEM=Phenanthrene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
97
6.4
3.1
46.0
54.0
68.0
1.7
20.0
140.0
340.0
610.0
700.0
990.0
3300.0
WH-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-10
— telf—
— telm—
WH-l-RE
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
SR-3-06
TEL-SR(ERL*NERM)
TR-1-03
GL-TEL-SR (ERL*NERM)
— erl—
SR-3-01
SR-1-03
WH-1-02
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-16
BR-1-08
SR-3-02
GL-NERH-85% NO EFFECT
— pelf—
BR-1-09
— pelm —
TR-1-04
NERH-85% NO EFFECT
SR-3-08
BR-1-07
SR-3-05
GL-PEL-SR (ERM*NERH)
PEL-SR(ERM*NERH)
SR-3-24
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
WH-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-03
— erm —
— aet4— •
i a tJU.-Liue.ii u ~
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
100
100
100
100
100
100
100
100
101
100
111
87
116
115
40
12
111
113
105
83
93
110
86
104
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.8
.5
.2
.6
.0
.5
.8
.7
.9
.4
.4
.4
.4
.5
UUUd.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
L Ul^-L .
GROW
10
ND
ND
ND
10
10
10
10
10
14
94
ND
10
95
11
87
10
85
10
90
ND
10
85
94
Lo-iiy/
TOXG
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
TX
NT
TX
ND
NT
TX
NT
y
MATURE
ND
ND
ND
ND
10
10
10
10
33
ND
74
ND
12
23
ND
0.
16
22
51
0.
ND
61
0.
22
TOXM
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
ND
NT
NT
TX
NT
TX
ND
NT
TX
TX
NOT
TOX
TOX
— aet6 —
— eqp —
IH-1-04
— aet3 —
BR-1-01
— aetl —
IH-1-03
IH-1-06
IH-1-07
— aet5 —
113.3 NT
10
35.0 TX 13
77.3 TX
85
TOX 0.0 TX ND
TOX 100.0 NT 85
TOX 1.4 TX 96
TOX 1.4 TX 68
TOX 0.0 TX ND
NT
NT
TX
ND
TX
NT
NT
ND
14
ND
68
ND
0.
0.
0.
ND
NT
ND
NT
ND
TX
NT
NT
ND
-------
iNurav.uuj
CONC ]
0.0
2.0
6.0
7.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
16.0
16.0
18.0
18.0
18.7
19.0
25.0
27.0
27.0
30.0
30.0
40.0
41.9
58.0
59.0
63.0
82.0
86.7
100.0
100.0
160.0
180.0
200.0
215.0
220.0
240.0
270.0
270.4
300.0
340.0
340.0
345.0
350.0
390.0
409.1
460.0
460.0
485.0
510.0
515.0
540.0
544.0
550.0
580.0
580.0
680.0
720.0
798.7
1000.0
1000.0
1100.0
1100.0
1400.0
1500.0
1500.0
1500.0
i=y u:
3FFEI
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
SG
NE
SG
SG
*
SG
NE
NE
**
NE
* *
**
NE
NE
NE
* *
* *
NE
NE
NE
**
* *
**
NE
NE
NE
*
NE
NE
*
NE
NE
**
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 j SG 1-2 | * 2-4 | **>4
409 CHEM=Phenanthrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
11 TB-l-RE
6 OM-1-01
6 UM-1-02
6 UM-l-RE
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
9 TR-1-02
9 TR-1-01
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
0.8 7 MR-1-01
10 MB-1-03
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-05
0.8 8 CF-1-03
2 BR-l-CO
NERM-50% NO EFFECT
7 MR-1-25
8 CF-1-04
1.4 7 MR-1-17
8 CF-1-02
TEL-SR(ERL*NERM)
1.5 7 MR-1-07
1.9 7 MR-1-02
2.7 3 SR-1-10
ERL-15% EFFECT
1.5 11 TB-1-03
10 MB-l-RE
11 TB-1-04
—telf—
4.5 7 MR-1-11
6 UM-1-03
4.8 7 MR-1-19
6.4 8 CF-1-01
—telm—
5 WH-l-RE
10 MB-1-02
4 SR-3-06
9.0 11 TB-1-02
10.0 11 TB-1-01
GL-NERM-50% NO EFFECT
9 TR-1-03
—erl—
4 SR-3-01
GL-TEL-SR(ERL*NERM)
10 MB-1-04
34.0 3 SR-1-03
GL-ERL-15% EFFECT
ERM-50% EFFECT
6.4 5 WH-1-02
39.0 3 SR-1-06
PEL-SR(ERM*NERH)
4 SR-3-16
2 BR-1-08
NERH-85% NO EFFECT
4 SR-3-02
—pelf—
2.3 2 BR-1-09
—pelm—
9 TR-1-04
4 SR-3-08
GL-NERH-85% NO EFFECT
2.9 2 BR-1-07
4 SR-3-05
GL-PEL-SR (ERM*NERH)
4 SR-3-24
GL-NEC-MAX NO EFFECT
20.0 5 WH-1-01
GL-ERM-50% EFFECT
6.0 2 BR-1-03
—erm—
—aet4—
~aet2—
98
11 &e>u.-
roxic
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
Luieii "-
su
100
119
117
86
100
100
100
100
81
100
100
100
108
95
100
100
120
114
123
100
109
128
115
102
91
109
100
52
100
93
90
114
114
64
109
97
100
11
0
98
97
95
96
36
10
96
97
103
88
82
88
80
96
102
71
79
RV
.0
.3
.9
.5
.0
.0
.0
.0
.4
.0
.0
.0
.1
.5
.0
.0
.3
.9
.0
.0
.3
.4
.1
.7
.9
.3
.0
.3
.0
.2
.7
.9
.0
.9
.5
.0
.0
.4
.0
.6
.4
.5
.2
.5
.3
.1
.4
.8
.2
.9
.3
.3
.1
.6
.7
.0
LUUd.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
L UXNX.
GROW
10
ND
ND
ND
10
ND
ND
ND
ND
10
10
10
79
ND
10
10
10
98
82
10
95
10
92
94
91
92
97
97
ND
10
58
ND
89
73
11
ND
92
72
ND
ND
94
ND
91
74
60
10
10
10
92
ND
92
85
94
10
91
85
ia-ng/
TOXG
NT
ND
ND
ND
NT
ND
ND
ND
ND
NT
NT
NT
TX
ND
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
TX
NT
ND
NT
TX
ND
TX
TX
NT
ND
NT
TX
ND
ND
NT
ND
TX
TX
TX
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
TX
g
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
68
ND
10
10
90
77
93
10
12
80
65
48
31
95
10
ND
ND
ND
24
ND
63
25
ND
ND
96
ND
ND
ND
11
ND
10
ND
37
95
10
10
10
ND
95
10
11
10
ND
10
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
ND
ND
ND
TX
ND
NT
TX
ND
ND
NT
ND
ND
ND
NT
ND
NT
ND
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 99
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=409 CHEM=Phenanthrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
2200.
2400.
3400,
5400,
6100,
6900,
7000.
9900,
20000.
20000.
33000.
182000
.0
.0
.0 **
.0
.0 **
.0
.0 **
.0 **
.0 NE
.0
.0 **
.0
340.
26.
700.
990.
3300.
,0
.0
.0
.0
.0
1
2
.
1
1
10
1
— -aet6 —
— eqp —
IH-1-04
— aet3 —
BR-1-01
— aetl —
IH-1-03
IH-1-06
MB-1-01
NEC-MAX NO EFFECT
IH-1-07
— aet5 —
TOX
TOX
TOX
TOX
NOT
TOX
0
89
1
1
75
0
.
.0
.
.5
.4
.4
.8
.0
TX
TX
TX
TX
NT
TX
ND
96
96
68
ND
ND
ND
NT
NT
NT
ND
ND
ND
10
0.
0.
ND
ND
ND
NT
NT
NT
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
100
IMUEH-k
CONC
8.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
16.0
18.0
37.4
38.0
46.9
66.0
85.3
100.0
120.0
120.0
129.6
140.0
140.0
140.0
160.0
200.0
220.0
230.0
240.0
240.0
245.0
250.0
250.0
270.0
270.0
290.0
520.0
547.7
580.9
960.0
960.0
1100.0
1100.0
1250.0
1250.0
1400.0
1700.0
1700.0
1700.0
2400.0
3400.0
4400.0
13000.0
34000.0
130000.0
JUCt=<±±V
EFFECT
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NC
* *
NE
NE
**
NE
NC
NE
NE
NE
NE
SG
**
NE
* *
* *
* *
i,n£i.ci=Ai
RATIO
1.0
.
.
,
.
.
.
1.4
„
0.2
10.0
15.7
0.4
.
.
1.8
140.0
240.0
340.0
13000
icnrai
SITE
3
5
4
3
7
7
7
7
7
7
7
1
8
8
8
8
8
8
2
7
8
5
3
3
2
2
5
4
4
5
4
2
.
4
4
4
4
.
.
.
2
.
,
1
2
1
1
1
=ene TjS5T=i.K±4 SAMfTir=D
SAMPLE
SR-1-10
WH-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-25
MR-1-17
MR-1-11
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
BR-l-CO
NERM-50% NO EFFECT
MR-1-19
CF-1-01
WH-l-RE
TEL-SR(ERL*NERM)
SR-1-06
— telm—
SR-1-03
— erl —
BR-1-09
BR-1-08
GL-NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM)
WH-1-02
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-06
SR-3-05
WH-1-01
SR-3-16
BR-1-07
NERH-85% NO EFFECT
— pelm —
SR-3-08
SR-3-02
SR-3-01
GL-NERH-85% NO EFFECT
SR-3-24
— aet6 —
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— aet4 —
— aet2 —
BR-1-03
— erm —
GL-ERM-50% EFFECT
ERM-50% EFFECT
IK-1-04
BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-03
IH-1-06
— aet3 —
— aetl —
— aetS—
IH-1-07
o^vj.J-ui^ii k. v.
roxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
90
100
100
100
100
138
122
70
116
113
117
100
100
107
96
109
84
79
100
111
95
85
18
104
105
38
51
103
104
8
102
47
95
100
96
.3
.0
.0
.0
.0
.8
.4
.2
.4
.4
.9
.0
.0
.4
.3
.9
.0
.0
.0
.9
.1
.7
.7
.5
.0
.0
.4
.3
.9
.6
.7
.9
.1
.6
.7
rVv-a.L
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
NT
NT
u« J. i ;
GROW
10
ND
10
10
10
11
12
75
11
11
11
10
10
11
11
11
10
11
10
10
13
ND
52
10
10
97
ND
11
11
ND
12
10
11
12
10
3=ny / g
TOXG
NT
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
NT
NT
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT 102.2 NT
11
NT
TOX 62.8 NT 87 TX
TOX 2.0 TX ND ND
NOT 67.8 NT 10 NT
TOX 2.7 TX ND ND
TOX 0.0 TX ND ND
TOX 0.0 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=410 CHEM=Anthracene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
101
8.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
18.0
31.6
38.0
46.9
66.0
66.0
81.2
85.3
100.0
100.0
100.0
120.0
140.0
160.0
200.0
220.0
230.0
240.0
245.0
250.0
250.0
250.0
250.0
270.0
290.0
290.0
290.0
409.3
409.3
520.0
670.0
670.0
960.0
960.0
1100.0
1100.0
1400.0
1700.0
2400.0
3400.0
4400.0
13000.0
34000.0
130000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
* *
* *
**
NE
NC
* *
NE
* *
NE
NE
NE
NE
* *
**
* *
* *
* *
**
1.4
10.0
12.0
10.0
1.0
15.7
24.0
.
110.0
140.0
170.0
240.0
340.0
13000
3
5
9
9
9
9
9
4
3
1
2
5
.
3
.
3
2
2
5
4
4
5
4
2
.
4
4
.
4
4
.
.
.
,
2
1
2
1
1
1
SR-1-10
WH-l-CO
TR-l-CO
TR-1-04
TR-1-03
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
WH-l-RE
TEL-SR(ERL*NERM)
SR-1-06
— telm —
SR-1-03
GL-NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM)
— erl—
BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-08
WH-1-02
SR-3-06
SR-3-05
WH-1-01
SR-3-16
BR-1-07
— pelm —
SR-3-08
SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-01
SR-3-24
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM'NERH)
— aet6 —
GL-ERM-50% EFFECT
ERM-50% EFFECT
— aet4 —
— aet2 —
BR-1-03
— erm —
IH-1-04
BR-1-01
IH-1-03
IH-1-06
— aet3 —
— aetl —
— aet5 —
IH-1-07
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
101.6
100.0
100.0
93.4
87.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
12.5
115.6
83.4
113.7
40.0
111.8
104.5
35.0
111.8
86.4
110.4
105.9
116.2
113.3
.
77.3
.
0.0
100.0
1.4
1.4
.
.
.
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
10
10
ND
ND
ND
ND
ND
10
10
10
10
14
87
95
90
85
11
94
94
13
10
85
10
10
10
10
85
ND
85
96
68
ND
NT
NT
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
ND
TX
NT
NT
ND
33
ND
ND
ND
ND
ND
ND
10
10
10
10
ND
0.
23
0.
22
ND
74
22
ND
16
0.
61
51
12
14
68
ND
0.
0.
0.
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
ND
NT
NT
TX
TX
ND
NT
TX
ND
NT
TX
NT
NT
NT
NT
NT
ND
TX
NT
NT
ND
-------
ttJU£!l-UUr.=4J
CONC EFFEC
0
2
6
7
8
9
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
13
16
18
30
38
46
50
66
66
85
89
100
120
120
140
140
140
160
167
200
200
220
230
240
245
250
250
250
270
290
290
409
520
670
960
960
1100
1100
1400
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.9
.0
.0
.0
.3
.0
.0
.0
.0
.0
.0
.0
.0
.3
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.3
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
SG
NE
NE
NE
NE
NG
NG
NG
NG
NG
NE
NE
NE
NE
NE
NE
NG
NE
NE
SG
SG
NE
NE
*
NE
**
SG
NE
**
NE
NE
NE
**
NE
*
NE
NE
NE
NE
* *
* It
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
410 CHEM=Anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
102
11 TB-l-RE
6 UM-1-01
6 UM-1-02
6 UM-l-RE
0.8 3 SR-1-10
6 UM-1-03
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
9 TR-1-04
9 TR-1-03
9 TR-1-02
9 TR-1-01
11 TB-1-04
2.0 11 TB-1-03
2.0 11 TB-1-02
2.0 11 TB-1-01
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
7 MR-1-25
1.0 7 MR-1-17
1.0 7 MR-1-11
1.0 7 MR-1-07
1.0 7 MR-1-02
1.0 7 MR-1-01
10 MB-1-03
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-05
8 CF-1-04
1.0 8 CF-1-03
8 CF-1-02
2 BR-l-CO
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
ERL-15% EFFECT
1.3 7 MR-1-19
1.6 8 CF-1-01
5 WH-l-RE
10 MB-l-RE
3.8 3 SR-1-06
—telm—
10 MB-1-02
6.6 3 SR-1-03
GL-ERL-15% EFFECT
~erl—
GL-TEL-SR (ERL*NERM)
1.5 2 BR-1-09
2 BR-1-08
GL-NERM-50% NO EFFECT
10.0 5 WH-1-02
10 MB-1-04
ERM-50% EFFECT
4 SR-3-06
PEL-SR(ERM*NERH)
4 SR-3-05
NERH-85% NO EFFECT
15.7 5 WH-1-01
4 SR-3-16
3.7 2 BR-1-07
—pelm—
4 SR-3-08
4 SR-3-02
GL-NERH-85% NO EFFECT
4 SR-3-01
4 SR-3-24
GL-NEC-MAX NO EFFECT
GL-PEL-SR(ERM*NERH)
—aet6—
GL-ERM-50% EFFECT
—aet4—
—aet2—
16.9 2 BR-1-03
—erm—
140.0 1 IH-1-04
b^UJ.1]
?OXIC
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
.ieni_ - t.
SURV
100.0
119.3
117.9
86.5
100.0
114.9
100.0
100.0
100.0
82.9
98.6
100.0
81.4
93.2
52.3
11.4
0.0
100.0
100.0
100.0
109.3
115.1
90.7
91.9
109.3
108.1
95.5
100.0
100.0
120.3
114.9
128.4
123.0
102.7
100.0
114.0
64.9
109.5
100.0
10.3
97.0
96.2
88.2
97.4
36.5
95.5
100.0
96.1
71.7
96.1
80.3
88.3
103.8
97.4
102.6
ocdx
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
UJN.LT;
GROW
10
ND
ND
ND
97
ND
10
ND
ND
ND
ND
ND
ND
10
97
72
ND
10
10
10
95
92
58
91
92
79
ND
10
10
10
98
10
82
94
10
89
73
11
ND
60
ND
91
92
10
74
ND
92
94
91
10
85
92
10
94
10
s-ng/g
TOXG
NT
ND
ND
ND
TX
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
TX
ND
NT
NT
NT
NT
TX
TX
TX
TX
TX
ND
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
ND
TX
ND
TX
NT
NT
TX
ND
NT
NT
NT
NT
TX
NT
NT
NT
NT
MATURE
ND
ND
ND
ND
10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
12
65
24
31
95
68
ND
10
10
90
77
80
93
48
10
63
25
ND
ND
47
I D
10
10
10
ND
ND
96
11
ND
95
10
95
10
11
10
TOXM
ND
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
TX
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
TX
ND
NT
NT
NT
ND
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
TOX 79.0 TX 85 TX 10 NT
TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 103
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
-- NUMCODE=410 CHEM=Anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
1700.0 ** 26.2 2 BR-1-01 TOX 89.5 TX 96 NT 10 NT
2000.0 NE . 10 MB-1-01 NOT 75.8 NT ND ND ND ND
2000.0 . . NEC-MAX NO EFFECT
2400.0 ** 240.0 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
3400.0 ** 340.0 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
4400.0 . . ~aet3—
13000.0 . . —aetl—
34000.0 . . ~~aet5—
130000.0 ** 13000 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
iNU£ai_ULm=^ j..
CONC EFFEI
10.
10.
10.
10.
10.
10.
10.
10.
10.
10.
12.
13.
21.
22.
24.
26.
36.
37.
39.
64.
68.
110.
110.
111.
113.
130.
133.
144.
160.
160.
160.
190.
234.
270.
345.
420.
500.
580.
600.
630.
760.
760.
990.
1000.
1200.
1200.
1200.
1484.
1494.
1700.
1900.
2355.
2400.
2500.
2900.
3000.
4800.
4800.
5100.
7500.
7500.
7500.
8600.
14000.
20400.
24000.
30000.
40000.
96000.
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
5
0
2
0
0
0
0
0
0
0
0
0
0
0
0
9
0
0
0
0
0
0
0
0
0
0
0
0
0
0
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
*
NE
NE
NE
NE
NE
NE
NC
NC
* *
NE
NE
NC
**
NE
* *
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER ( —) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=4ll CHEM=Fluoranthene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-05
8 CF-1-03
2 BR-l-CO
7 MR-1-25
8 CF-1-06
1 MR-1-17
8 CF-1-02
7 MR-1-07
8 CF-1-04
3 SR-1-10
NERM-50% NO EFFECT
7 MR-1-02
TEL-SR(ERL*NERM)
1.9 7 MR-1-11
1.6 5 WH-1-02
ERL-15% EFFECT
—telf—
—telm—
5 WH-l-RE
7 MR-1-19
8 CF-1-01
4 SR-3-06
2.0 3 SR-1-06
GL-ERL-15% EFFECT
3 SR-1-03
GL-TEL-SR(ERL*NERM)
4 SR-3-01
GL-NERM-50% NO EFFECT
4 SR-3-16
4 SR-3-02
4 SR-3-08
~erl—
4 SR-3-05
0.3 2 BR-1-08
NERH-85% NO EFFECT
0.3 2 BR-1-07
14.3 5 WH-1-01
4 SR-3-24
2 BR-1-09
GL-NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
—pelm—
—aet4—
0.7 2 BR-1-03
—pelf—
GL-PEL-SR(ERM*NERH)
—aet2 —
ERM-50% EFFECT
—aet6—
480.0 1 IH-1-04
GL-ERM-50% EFFECT
—erm—
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
860.0 1 IH-1-03
1400.0 1 IH-1-06
—eqp—
—aet3—
—aetl—
4000.0 1 IH-1-07
—aet5—
104
1 »CUJ.JUCAI L. —
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
100
100
100
100
117
100
100
96
84
100
138
107
122
79
116
109
90
113
70
51
85
111
95
103
18
104
96
102
100
95
104
38
47
8
102
105
.0
.0
.0
.0
.9
.0
.0
.3
.0
.0
.8
.4
.4
.0
.4
.9
.3
.4
.2
.4
.7
.9
.1
.3
.7
.5
.7
.7
.6
.1
.9
.0
.9
.6
.2
.0
UVJUCL.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
L. WIN -L .
GROW
ND
10
10
10
11
10
10
11
10
10
11
11
12
11
11
11
10
11
75
ND
ND
10
13
11
52
10
10
12
12
11
11
97
10
ND
11
10
La=uy /
TOXG
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
y
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
TOX
62.8 NT
87
TX
2.0 TX ND ND
NOT 67.8 NT 10 NT
TOX 2.7 TX ND ND
TOX 0.0 TX ND ND
TOX 0.0 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=411 CHEM=Fluoranthene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
105
10.0
10.0
10.0
10.0
10.0
10.0
29.0
31.0
36.0
110.0
111.0
113.0
130.0
130.0
144.2
145.0
152.3
160.0
160.0
160.0
160.0
190.0
270.0
390.0
420.0
500.0
500.0
580.0
580.0
600.0
630.0
710.0
760.0
774.6
834.3
990.0
1000.0
1200.0
1200.0
1200.0
1200.0
1200.0
1200.0
1494.0
1700.0
1900.0
2355.0
2500.0
3000.0
4800.0
5100.0
7500.0
8600.0
14000.0
20400.0
24000.0
30000.0
40000.0
96000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
*
NE
NE
NE
NE
NE
NE
SG
NE
* *
**
**
NE
**
* *
**
* *
**
* *
* *
.
.
.
.
1.6
.
.
.
2.0
t
1.4
76.0
99.0
14.3
120.0
190.0
480.0
.
750.0
860.0
1400.0
4000.0
5
9
4
3
1
2
9
9
3
5
5
4
3
3
4
9
4
4
4
4
9
2
2
5
4
2
2
1
2
1
1
1
WH-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-02
TR-1-01
SR-1-10
WH-1-02
— telf—
— telm —
WH-l-RE
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
SR-3-06
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-1-03
SR-3-01
TR-1-03
SR-3-16
SR-3-02
GL-NERH-85% NO EFFECT
SR-3-08
NERH-85% NO EFFECT
— erl —
SR-3-05
TR-1-04
BR-1-08
GL-PEL-SR (ERM*NERH)
PEL-SR(ERM*NERH)
BR-1-07
WH-1-01
SR-3-24
BR-1-09
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
— pelm —
— aet4 —
BR-1-03
—pelf—
— aet2 —
— aet6 —
IH-1-04
— erm —
BR-1-01
IH-1-03
IH-1-06
— eqp —
— aet3 —
— aetl —
IH-1-07
— aetS—
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
100
100
100
100
100
100
100
100
101
40
100
111
12
115
116
87
111
105
110
104
93
113
86
35
113
83
77
0
100
1
1
0
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.8
.5
.6
.2
.5
.8
.9
.4
.5
.4
.7
.4
.0
.3
.4
.
.
.
.
.
.3
.
.0
.0
.4
.4
.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
TX
TX
10
ND
10
10
10
10
ND
ND
10
11
14
94
87
.
95
10
ND
10
10
10
94
ND
85
85
13
10
90
85
ND
85
96
68
ND
NT
ND
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
TX
TX
NT
NT
TX
TX
ND
TX
NT
NT
ND
ND
ND
10
10
10
10
ND
ND
33
ND
ND
74
0.
23
12
ND
16
51
61
22
ND
22
0.
ND
14
0.
68
ND
0.
0.
0.
ND
ND
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
NT
NT
NT
NT
ND
NT
NT
NT
TX
ND
TX
TX
ND
NT
TX
NT
ND
TX
NT
NT
ND
-------
iMurauuijj
CONC ]
0.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
12.0
13.0
20.0
21.0
22.0
24.0
26.0
27.0
29.0
30.0
30.0
31.0
31.5
33.0
36.0
39.0
50.0
51.0
68.0
89.0
110.0
110.0
111.0
113.0
130.0
132.0
133.0
144.0
153.8
160.0
160.0
175.0
190.0
210.0
215.0
270.0
318.6
390.0
400.0
420.0
500.0
500.0
580.0
580.0
600.0
630.0
630.0
710.0
720.0
760.0
869.5
990.0
1000.0
1200.0
1200.0
1200.0
1200.0
1494.0
1700.0
1900.0
2355.0
2500.0
3000.0
i=^tj..
EFFEl
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NC
SG
NE
*
NE
NE
NE
SG
NE
*
it
NE
NE
**
NE
SG
NE
NE
**
**
NE
* *
* *
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
* *
NE
*
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
411 CHEM=Fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
106
11 TB-l-RE
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
0.4 11 TB-1-01
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
0.9 7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-05
0.6 8 CF-1-03
2 BR-l-CO
7 MR-1-25
8 CF-1-06
0.8 11 TB-1-03
1.9 7 MR-1-17
8 CF-1-02
2.2 7 MR-1-07
8 CF-1-04
6 UM-l-RE
9 TR-1-02
1.2 11 TB-1-02
NERM-50% NO EFFECT
9 TR-1-01
TEL-SR (ERL*NERM)
ERL-15% EFFECT
3.6 3 SR-1-10
3.5 7 MR-1-02
11 TB-1--04
6 UM-1-01
6.2 7 MR-1-11
6 UM-1-02
1.6 5 WH-1-02
GL-ERL-15% EFFECT
—telf—
— telm—
5 WH-l-RE
6 UM-1-03
12.1 7 MR-1-19
8.9 8 CF-1-01
GL-TEL-SR (ERL*NERM)
4 SR-3-06
16.0 3 SR-1-06
ERM-50% EFFECT
19.0 3 SR-1-03
10 MB-1-03
GL-NERM-50% NO EFFECT
4 SR-3-01
PEL-SR(ERM*NERH)
9 TR-1-03
10 MB-l-RE
4 SR-3-16
4 SR-3-02
10 MB-1-02
4 SR-3-08
NERH-85% NO EFFECT
—erl—
4 SR-3-05
GL-NERH-85% NO EFFECT
9 TR-1-04
10 MB-1-04
2 BR-1-08
GL-PEL-SR (ERM*NERH)
2.6 2 BR-1-07
14.3 5 WH-1-01
4 SR-3-24
3.1 2 BR-1-09
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
—pelm—
—aet4—
4.9 2 BR-1-03
—pelf—
—aet2—
—aet6—
ki K>eLu.iueuu -
POXIC SURV
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
100
100
100
100
0
100
100
100
108
100
100
114
123
100
109
120
52
115
102
91
128
86
100
11
81
100
109
93
119
90
117
36
109
114
114
64
100
10
96
95
97
98
100
96
103
97
88
96
82
95
97
80
71
102
88
.0
.0
.0
.0
.0
.0
.0
.0
.1
.0
.0
.9
.0
.0
.3
.3
.3
.1
.7
.9
.4
.5
.0
.4
.4
.0
.3
.2
.3
.7
.9
.5
.5
.9
.0
.9
.0
.3
.2
.5
.4
.6
.0
.1
.8
.0
.3
.1
.9
.5
.4
.3
.7
.6
.2
i-uta.
TOXS
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
L UWJ.
GROW
10
10
ND
ND
ND
10
10
10
79
10
10
98
82
10
95
10
97
92
94
91
10
ND
ND
72
ND
97
92
10
ND
58
ND
74
11
ND
89
73
92
60
91
ND
94
ND
ND
10
10
ND
92
94
ND
ND
10
85
91
10
92
is-ng/
TOXG
NT
NT
ND
ND
ND
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
ND
ND
TX
ND
TX
TX
NT
ND
TX
ND
TX
NT
ND
TX
TX
NT
TX
TX
ND
NT
ND
ND
NT
NT
ND
NT
NT
ND
ND
NT
TX
NT
NT
NT
g
MATURE TOXM
ND
ND
ND
ND
ND
10
10
10
68
10
10
77
93
10
12
90
ND
65
48
31
80
ND
ND
ND
ND
10
95
ND
ND
24
ND
ND
ND
ND
63
25
96
37
10
ND
11
ND
ND
95
10
ND
95
11
ND
ND
10
10
ND
10
10
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
NT
ND
ND
ND
ND
NT
NT
ND
ND
TX
ND
ND
ND
ND
NT
TX
NT
TX
NT
ND
NT
ND
ND
NT
NT
ND
NT
NT
ND
ND
NT
NT
ND
NT
NT
TOX
79.0 TX
85
TX
10
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 107
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=411 CHEM=Fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO
4800.
5100,
7500,
8600.
10000.
10000,
14000,
20400,
24000.
30000.
40000.
96000,
.0 **
.0
.0 **
.0 **
.0 NE
.0
.0 **
.0
.0
.0
.0 **
.0
480
19
860
1400.
4000,
.0
.5
.0
.0
.0
SITE SAMPLE CEN TOXIC
1
2
1
10
1
1
IH-1-04
— erm —
BR-1-01
IH-1-03
MB-1-01
NEC -MAX NO EFFECT
IH-1-06
— eqp —
— aet3 —
— aetl —
IH-1-07
— aetS—
TOX
TOX
TOX
NOT
TOX
TOX
SURV
0.
89.
1.
75.
1.
0.
0
5
4
8
4
0
TOXS
TX
TX
TX
NT
TX
TX
GROW
ND
96
96
ND
68
ND
TOXG
ND
NT
NT
ND
NT
ND
MATURE TOM
ND
10
0.
ND
0.
ND
ND
NT
NT
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
108
J^UJ^!
CONC :
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
14.0
18.0
21.0
26.0
29.0
32.0
38.0
44.0
53.0
61.0
67.5
94.0
120.0
120.0
144.0
145.0
153.0
160.0
270.0
550.0
570.0
570.0
594.5
620.0
665.0
690.0
710.0
750.0
750.0
875.0
880.0
880.0
950.0
1000.0
1100 .0
1398.0
1450.0
1684.6
1800.0
2100.0
2600.0
2600.0
2824.0
3200.0
3225.0
3300.0
5500.0
5500.0
6100.0
6100.0
6100.0
16000.0
16000.0
16000.0
26000.0
40000.0
55000.0
62000.0
l_UU£j='
EFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
NE
NE
NE
NE
NE
*
NC
NE
NE
NE
NE
**
NE
NC
NE
NC
**
NE
**
**
**
•± x z \-n£,n=
r RATIO
.
.
.
1.6
2.3
.
2.8
0.3
18.3
0.5
.
0.9
.
.
550.0
1600.0
4000.0
5500.0
ryxe
SITE
5
4
3
7
7
1
8
8
8
8
2
7
8
8
7
7
7
3
7
5
5
7
8
.
4
4
3
3
.
2
4
4
2
.
4
5
4
2
4
2
.
.
.
.
1
.
2
.
1
.
1
1
.
ine TJS5T=(,KJ.4 SAMPTYF=DOt
! SAMPLE
WH-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-03
BR-l-CO
MR-1-25
CF-1-04
CF-1-02
MR-1-07
MR-1-02
MR-1-17
NERM-50% NO EFFECT
SR-1-10
— telf—
MR-1-11
TEL-SR(ERL*NERM)
WH-l-RE
WH-1-02
ERL-15% EFFECT
MR-1-19
CF-1-01
—telm—
SR-3-06
SR-3-01
SR-1-03
SR-1-06
GL-ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
GL-NERM-50% NO EFFECT
— erl—
BR-1-08
SR-3-02
SR-3-16
BR-1-09
— pelf—
SR-3-05
NERH-85% NO EFFECT
WH-1-01
SR-3-08
BR-1-07
— pelm —
GL-NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
SR-3-24
BR-1-03
— erm —
— aet4 —
GL-PEL-SR (ERM*NERH)
— aet6 —
ERM- 50% EFFECT
— aet2 —
IH-1-04
GL-ERM-50% EFFECT
BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-03
._ -s^l-T^ —
etc t. J
~""*3Gtl™~"
— eqp —
IH-1-06
IH-1-07
— aetS —
"=i_tJ-AUCJ
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
,1U UWL
SURV
100
100
100
100
117
100
100
107
96
84
100
138
109
79
116
113
122
90
70
85
51
111
95
103
96
104
18
38
100
102
105
104
8
95
47
102
62
.0
.0
.0
.0
.9
.0
.0
.4
.3
.0
.0
.8
.9
.0
.4
.4
.4
.3
.2
.7
.4
.9
.1
.3
.7
.5
.7
.0
.6
.7
.0
.9
.6
.1
.9
.2
.8
.aj. UJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
HJ.O. D— J
GROW
ND
10
10
10
11
10
10
11
11
10
10
11
11
11
11
11
12
10
_75
ND
ND
10
13
11
10
10
52
97
12
12
10
11
ND
11
10
11
87
uy/9 -
TOXG
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
TX
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX 2.0 TX ND ND ND ND
NOT 67.8 NT 10 NT ND ND
TOX
2.7 TX ND ND ND ND
TOX 0.0 TX ND ND ND ND
TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
109
CONC EFFECT RATIO SITE SAMPLE
10
10
10
10
10
10
10
28
44
53
94
94
120
127
153
160
231
269
270
270
550
570
570
570
590
665
690
710
750
750
750
750
875
880
908
908
950
1000
1100
1100
1100
1398
1800
1800
1800
2100
2600
2600
3200
3300
5500
6100
16000
16000
16000
26000
40000
55000
62000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.1
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.3
.3
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
NE
*
NE
* *
NE
NE
* *
SG
**
NE
**
NE
**
**
* *
* *
* *
**
2.3
.
2.8
.
69.0
75.0
1.3
.
.
18.3
110.0
.
.
.
.
210.0
550.0
610.0
1600.0
4000.0
5500.0
5
9
9
4
3
1
2
9
3
5
5
4
9
4
3
3
9
2
4
4
2
4
5
4
2
.
4
.
.
2
.
.
.
1
2
1
.
1
1
WH-l-CO
TR-l-CO
TR-1-02
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-01
SR-1-10
— telf—
WH-l-RE
NERM-50% NO EFFECT
WH-1-02
GL-NERM-50% NO EFFECT
—telrn —
SR-3-06
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
TR-1-03
SR-3-01
SR-1-03
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
TR-1-04
— erl —
BR-1-08
SR-3-02
SR-3-16
BR-1-09
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
— pelf—
SR-3-05
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
WH-1-01
SR-3-08
BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
— pelm —
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
BR-1-03
— erm —
— aet4 —
— aet6 —
— aet2 —
IH-1-04
BR-1-01
IH-1-03
— aet3 —
— aetl —
*~ —• SCpD-- •—
IH-l-06
IH-1-07
— aet5 —
jaiment. - tou
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
100
100
100
100
100
100
100
100
101
100
40
111
87
116
115
12
93
113
105
111
83
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.8
.5
.2
.6
.5
.4
.7
.9
.8
.4
aj. ui
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
MJLTO-I
GROW
10
ND
ND
10
10
10
10
ND
10
14
11
94
ND
10
95
87
ND
85
10
10
90
ig/g -
TOXG
NT
ND
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
ND
TX
NT
NT
TX
MATURE TOXM
ND
ND
ND
10
10
10
10
ND
33
ND
ND
74
ND
12
23
0.
ND
22
51
16
0.
ND
ND
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
ND
NT
NT
NT
ND
TX
NT
NT
TX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
104.5 NT 94 NT
35.0 TX
110.4 NT
86.4 NT
13 NT
10 NT
85 TX
113.3 NT 10 NT
77.3 TX 85 TX
0.0 TX
100.0 NT
1.4 TX
1.4
0.0
TX
TX
ND
85
96
68
ND
ND
TX
NT
NT
ND
22
ND
61
0.
14
68
ND
0.
0.
0.
ND
TX
ND
NT
TX
NT
NT
ND
TX
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGH1
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=412 CHEM=Pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
110
0.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
14.0
18.0
21.0
26.0
26.0
28.0
29.0
32.0
40.0
40.0
40.0
44.0
44.3
49.0
50.0
53.0
61.0
70.0
76.0
94.0
94.0
120.0
120.0
136.0
144.0
145.0
153.0
160.0
160.6
210.0
215.0
270.0
270.0
347.5
440.0
493.2
550.0
570.0
590.0
600.0
600.0
665.0
690.0
700.0
710.0
750.0
750.0
875.0
880.0
880.0
950.0
983.9
1000.0
1100.0
1100.0
1398.0
1800.0
1800.0
2100.0
2600.0
2600.0
3200.0
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
*
NE
*
*
SG
SG
**
SG
**
NE
NE
NE
NE
*
NE
**
* *
NE
NE
NE
NE
NE
* *
**
NE
NE
NE
NE
NE
NE
*
NE
* *
NE
*
NE
* *
.
0.8
0.7
.
.
2.2
.
2.4
2.7
1.1
1.1
.
4.4
1.4
5.1
2.3
12.0
10.5
.
.
.
.
55.0
57.0
,
2.1
18.3
3.1
.
,
6.0
.
11
5
6
9
9
4
3
7
7
1
8
8
8
8
2
7
8
8
6
7
9
7
7
11
11
3
11
7
11
6
5
6
5
6
7
8
4
.
10
9
4
.
10
3
3
9
10
10
.
2
4
4
2
4
5
4
2
4
.
2
.
.
TB-l-RE
WH-l-CO
UM-l-CO
TR-l-CO
TR-1-02
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-03
BR-l-CO
MR-1-25
CF-1-04
CF-1-02
UM-l-RE
MR-1-07
TR-1-01
MR-1-02
MR-1-17
TB-1-03
TB-1-02
ERL-15% EFFECT
SR-1-10
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
TB-1-01
— telf—
MR-1-11
TB-1-04
UM-1-01
WH-l-RE
UM-1-02
WH-1-02
GL-ERL-15% EFFECT
UM-1-03
MR-1-19
CF-1-01
— telm —
SR-3-06
GL-TEL-SR ( ERL*NERM )
MB-1-03
GL-NERM-50% NO EFFECT
TR-1-03
SR-3-01
ERM- 50% EFFECT
MB-1-04
PEL-SR(ERM*NERH)
SR-1-03
SR-1-06
TR-1-04
MB-l-RE
MB-1-02
— erl—
BR-1-08
NERH-85% NO EFFECT
SR-3-02
SR-3-16
BR-1-09
— pelf--
SR-3-05
GL-NERH-85% NO EFFECT
WH-1-01
GL-PEL-SR (ERM*NERH)
SR-3-08
BR-1-07
GL-ERM-50% EFFECT
— pelm —
SR-3-24
GL-NEC-MAX NO EFFECT
BR-1-03
— erm —
— aet4 —
— aet6 —
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
108.1
100.0
100.0
120.3
114.9
123.0
100.0
109.3
128.4
102.7
86.5
91.9
81.4
109.3
115.1
52.3
11.4
100.0
0.0
90.7
93.2
119.3
109.5
117.9
36.5
114.9
114.0
64.9
100.0
95.5
98.6
97.4
95.5
96.2
10.3
82.9
100.0
97.0
97.4
103.8
96.1
88.2
96.1
71.7
88.3
80.3
102.6
79.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
TX
10
10
ND
ND
ND
10
10
10
79
10
10
10
98
82
10
95
10
94
ND
91
ND
92
92
97
72
97
ND
58
10
ND
11
ND
74
ND
89
73
92
ND
ND
94
ND
91
60
ND
ND
ND
10
10
10
92
94
91
92
85
10
85
NT
NT
ND
ND
ND
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
TX
ND
TX
TX
NT
TX
TX
ND
TX
NT
ND
NT
ND
TX
ND
TX
TX
NT
ND
ND
NT
ND
TX
TX
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
ND
ND
ND
ND
ND
10
10
10
68
10
10
90
77
93
10
12
80
48
ND
31
ND
95
65
ND
ND
10
ND
24
ND
ND
ND
ND
ND
ND
63
25
96
ND
ND
11
ND
10
37
ND
ND
ND
10
10
95
10
11
ND
95
10
10
10
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
ND
NT
NT
ND
ND
NT
ND
TX
ND
ND
ND
ND
ND
ND
NT
TX
NT
ND
ND
NT
ND
NT
TX
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
111
CONC EFFECT RATIO SITE SAMPLE
=bottom sediment - total UNITS=ng/g
(continued)
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
3300
5500
6100
9000
9000
16000
16000
16000
26000
40000
55000
62000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
**
* *
NE
**
**
**
550
17
1600
4000
5500
.
.0
.4
.0
.
.0
.0
.
1
2
10
1
1
1
— aet2 —
IH-1-04
BR-1-01
MB-1-01
NEC -MAX NO EFFECT
IH-1-03
— aet3 —
— aetl —
— eqp —
IH-1-06
IH-1-07
— aetS —
TOX
TOX
NOT
TOX
TOX
TOX
0.0
89.5
75.8
TX
TX
NT
1.4 TX
ND
96
ND
96
1.4 TX 68
0.0 TX ND
ND
NT
ND
NT
NT
ND
ND
10
ND
0.
0.
ND
ND
NT
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
112
JMUMUUlJiS='
CONC
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
13.0
15.0
16.0
19.0
19.0
21.0
31.7
35.0
41.0
74.8
75.5
81.0
89.0
160.0
170.0
250.0
250.0
250.0
260.0
261.0
270.0
273.9
300.0
300.0
300.0
310.0
340.0
340.0
385.0
440.0
470.0
490.0
575.0
680.0
690.0
693.0
1100.0
1195.0
1300.0
1554.0
1600.0
1600.0
3500.0
3500.0
3500.0
4200.0
4200.0
4200.0
5100.0
5100.0
7300.0
13000.0
16000.0
25000.0
26000.0
i-LJ l_HJM
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NC
NE
**
NE
NE
NE
NC
* *
NC
NE
NE
**
* *
* *
* *
i-eenz tc
RATIO
.
.
.
.
0.5
1.4
.
.
.
.
0.2
.
4.6
.
,
0.4
19.2
.
0.5
.
420.0
.
.
730.0
1600.0
2500.0
ajantj
SITE
5
4
3
7
7
7
1
8
8
8
8
8
2
7
8
3
7
7
7
5
5
.
7
8
4
3
4
4
.
2
.
4
3
.
.
2
4
.
4
2
5
.
2
4
.
.
.
.
2
.
.
1
.
.
.
1
1
1
aracene TBST=CRJ.« SAMPTY
SAMPLE
WH-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-17
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-03
CF-1-02
BR-l-CO
MR-1-11
CF-1-04
SR-1-10
MR-1-07
MR-1-02
NERM-50% NO EFFECT
MR-1-25
— telf—
WH-1-02
WH-l-RE
— telm—
TEL-SR(ERL*NERM)
MR-1-19
CF-1-01
SR-3-06
SR-1-03
SR-3-16
SR-3-02
GL-NERM-50% NO EFFECT
BR-1-08
— erl —
SR-3-01
GL-TEL-SR (ERL'NERM)
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-09
SR-3-05
NERH-85% NO EFFECT
— pelf —
SR-3-08
BR-1-07
WH-1-01
GL-NERH-85% NO EFFECT
BR-1-03
SR-3-24
— pelm —
— aet6 —
PEL- SR ( ERM*NERH )
— aet4 —
GL-PEL-SR (ERM'NERH)
— erm —
— aet2 —
BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-04
GL-ERM-50% EFFECT
ERM- 50% EFFECT
~""ciet j "*"•
— aetl —
IH-1-03
— aet5 —
IH-1-06
IH-1-07
— eqp —
, uiu s> cu, J.iueii u
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
100.
100.
100.
100.
122.
117.
100.
100.
107.
96.
84.
79.
100.
70.
109.
90.
116.
113.
138.
51.
85.
111.
95.
103.
104.
102.
100.
38.
96.
18.
105.
104.
95.
47.
8.
62.
102.
0
0
0
0
4
9
0
0
4
3
0
0
0
2
9
3
4
4
8
4
7
9
1
3
5
7
6
0
7
7
0
9
1
9
6
8
2
- U»JI
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
NT
L.CIA ui
GROW
ND
10
10
10
12
11
10
10
11
11
10
11
10
75
11
10
11
11
11
ND
ND
10
13
11
10
12
12
97
10
52
10
11
11
10
ND
87
11
>H.iO=IJ
TOXG
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
TX
NT
ig/g
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
TOX
TOX
67.8 NT 10 NT ND ND
2.0 TX ND ND ND ND
2.7 TX ND
ND ND
TOX 0.0 TX ND NID ND ND
TOX 0.0 TX ND SD ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect j NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
113
CEN TOXIC
SURV TOXS GROW TOXG MATURE TOXM
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
15.0
31.7
35.0
41.0
41.0
74.8
100.0
100.5
103.2
130.0
160.0
161.6
170.0
250.0
250.0
260.0
260.0
260.0
261.0
270.0
270.0
270.0
300.0
310.0
340.0
363.7
363.7
385.0
440.0
470.0
490.0
490.0
490.0
680.0
690.0
690.0
690.0
693.0
1100.0
1300.0
1600.0
1600.0
3500.0
4200.0
5100.0
5100.0
7300.0
13000.0
16000.0
25000.0
26000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
**
NE
* *
**
SG
NE
**
**
* *
NE
**
* *
* *
* *
**
.
1.4
.
.
26.0
.
.
.
4.6
31.0
1.1
47.0
19.2
68.0
.
.
350.0
420.0
730.0
f
1600.0
2500.0
5
9
9
9
4
3
1
2
3
5
5
.
9
.
9
4
3
4
4
2
4
3
2
4
4
2
5
2
4
2
1
1
t
1
1
WH-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-10
— telf—
WH-1-02
WH-l-RE
NERM-50% NO EFFECT
— telm —
TR-1-03
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
TR-1-04
SR-3-06
GL-TEL-SR (ERL*NERM)
SR-1-03
SR-3-16
SR-3-02
BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
— erl~
SR-3-01
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-1-06
BR-1-09
SR-3-05
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— pelf—
SR-3-08
BR-1-07
WH-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-03
SR-3-24
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— pelm —
— aet6 —
— aet4 —
— erm —
— aet2~
BR-1-01
IH-1-04
— aet3 —
— aetl —
IH-1-03
— aet5 —
IH-1-06
IH-1-07
— eqp —
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
101.6
40.0
100.0
.
.
87.5
.
.
93.4
111.8
115.6
111.8
105.9
113.7
116.2
12.5
83.4
104.5
110.4
86.4
35.0
.
.
77.3
113.3
100.0
0.0
.
1.4
.
1.4
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
TX
TX
TX
10
ND
ND
ND
10
10
10
10
10
11
14
ND
ND
94
95
10
10
85
10
87
90
94
10
85
13
85
10
85
ND
96
68
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
TX
NT
TX
ND
NT
NT
ND
ND
ND
ND
ND
10
10
10
10
33
ND
ND
ND
ND
74
23
16
51
22
12
0.
0.
22
61
0.
ND
68
14
0.
ND
0.
0.
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
ND
ND
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
ND
NT
NT
TX
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHS
INCLUDES NBS AND OTHER (--) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA28 SAMPTYP=bottom sediment - total 0NITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
0.0 NE . 11 TB-l-RE
7.0 NE . 6 UM-l-RE
10.0 NE . 5 WH-l-CO
10.0 NE . 6 UM-l-CO
10.0 NE . 9 TR-l-CO
10.0 NE . 9 TR-1-02
10.0 NE . 9 TR-1-01
10.0 NC 1.0 11 TB-1-02
10.0 NE . 4 SR-3-CO
10.0 NE . 3 SR-l-CO
10.0 NE . 7 MR-l-CO
10.0 NC 0.6 7 MR-1-17
10.0 NC 0.6 7 MR-1-01
10.0 NE . 1 IH-l-CO
10.0 NE . 8 CF-l-CO
10.0 NE . 8 CF-1-06
10.0 NE . 8 CF-1-05
10.0 NC 0.9 8 CF-1-03
10.0 NE . 8 CF-1-02
10.0 NE . 2 BR-l-CO
13.0 NC 0.8 7 MR-1-11
13.0 NE . 8 CF-1-04
13.0 . NERM-50% NO EFFECT
15.0 SG 1.5 3 SR-1-10
15.7 . TEL-SR(ERL*NERM)
16.0 SG 1.0 7 MR-1-07
19.0 SG 1.2 7 MR-1-02
19.0 . . ERL-15% EFFECT
20.0 NE . 11 TB-1-04
20.0 SG 2.0 11 TB-1-03
21.0 NE . 7 MR-1-25
27.0 NE . 6 UM-1-01
31.7 . . —telf—
35.0 SG 1.4 5 WH-1-02
35.0 . . GL-ERL-15% EFFECT
41.0 NE . 5 WH-l-RE
44.0 NE . 6 UM-1-02
68.0 NE . 6 UM-1-03
74.8 . . —telm—
81.0 ** 5.2 7 MR-1-19
84.7 . GL-TEL-SR(ERL*NERM)
89.0 ** 8.4 8 CF-1-01
90.0 ** 9.0 11 TB-1-01
99.0 NE . 10 MB-1-03
100.0 NE . 9 TR-1-03
130.0 NE . 9 TR-1-04
160.0 NE . 4 SR-3-06
170.0 ** 17.0 3 SR-1-03
200.0 NE . 10 MB-1-02
205.0 . . GL-NERM-50% NO EFFECT
250.0 NE . 4 SR-3-16
250.0 NE . 4 SR-3-02
260.0 NE . 2 BR-1-08
261.0 . . — erl—
270.0 NE . 4 SR-3-01
270.0 . . NERH-85% NO EFFECT
284.6 . PEL-SR(ERM*NERH)
300.0 ** 30.0 3 SR-1-06
300.0 NE . 10 MB-l-RE
300.0 . . ERM-50% EFFECT
310.0 * 2.3 2 BR-1-09
340.0 NE . 4 SR-3-05
340.0 . . GL-NERH-85% NO EFFECT
360.0 NE . 10 MB-1-04
385.0 . . —pelf—
408.2 . . GL-PEL-SR (ERM*NERH)
440.0 NE . 4 SR-3-08
470.0 * 3.5 2 BR-1-07
490.0 ** 19.2 5 WH-1-01
490.0 . . GL-ERM-50% EFFECT
680.0 ** 5.0 2 BR-1-03
690.0 NE . 4 SR-3-24
690.0 . . GL-NEC-MAX NO EFFECT
693.0 . . —pelm—
1100.0 . . —aet6~
1300.0 . . —aet4—
1600.0 . . —erm—
114
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
IU^*l|i_il I,
SURV
100.0
86.5
100.0
100.0
100.0
100.0
81.4
11.4
100.0
100.0
100.0
115.1
108.1
100.0
100.0
120.3
114.9
123.0
102.7
100.0
90.7
128.4
100.0
91.9
109.3
93.2
52.3
109.3
119.3
36.5
109.5
117.9
114.9
114.0
64.9
0.0
95.5
98.6
82.9
100.0
96.2
97.0
9e!i
103.8
97.4
97.4
10.3
100.0
88.2
96.1
9s! 5
88.3
80.3
71.7
79.0
102.6
L.VJI
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
TX
NT
-CLJ. UX
GROW
10
ND
10
ND
ND
ND
ND
72
10
10
10
92
79
10
10
10
98
82
94
10
58
10
97
91
92
10
97
95
ND
74
11
ND
ND
89
73
ND
ND
ND
ND
92
91
ND
10
10
10
94
60
ND
92
94
ND
92
85
91
85
10
1J. 1 3 — 1
TOXG
NT
ND
NT
ND
ND
ND
ND
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
ND
TX
NT
ND
ND
TX
TX
ND
ND
ND
ND
NT
TX
ND
NT
NT
NT
NT
TX
ND
NT
NT
ND
NT
TX
NT
TX
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
65
68
10
10
90
77
93
48
10
24
80
10
31
95
ND
ND
12
ND
ND
ND
ND
ND
63
25
ND
ND
ND
ND
96
10
ND
95
10
10
11
37
ND
10
11
ND
95
10
ND
10
10
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
ND
ND
NT
ND
ND
ND
ND
ND
NT
TX
ND
ND
ND
ND
NT
NT
ND
NT
NT
NT
NT
TX
ND
NT
NT
ND
NT
NT
ND
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 115
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
1600.0
3000.0 NE
3000.0
3500.0 **
4200.0 **
5100.0
5100.0
7300.0 **
13000.0
16000.0 **
25000.0 **
26000.0
10
— aet2 —
MB-1-01
NOT
75
.8
NT
ND
ND
ND
ND
NEC -MAX NO EFFECT
25.
420.
730.
.
1600.
2500.
9
0
0
0
0
2
1
1
1
1
BR-1-01
IH-1-04
— aet3 —
— aetl —
IH-1-03
~aet5—
IH-1-06
IH-1-07
— eqp —
TOX
TOX
TOX
TOX
TOX
89
0
1
1
0
.5
.0
.4
.4
.0
TX
TX
TX
TX
TX
96
ND
96
68
ND
NT
ND
NT
NT
ND
10
ND
0.
0.
ND
NT
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGH:'
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
116
iN UtfH
CONC
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
17.0
20.0
24.0
24.0
27.0
28.0
30.0
30.0
40.0
56.0
57.1
108.0
110.0
113.0
114.0
122.5
160.0
250.0
270.0
270.0
270.0
330.0
367.4
384.0
400.0
440.0
440.0
440.0
470.0
500.0
500.0
500.0
600.0
620.0
645.0
690.0
846.0
862.0
1100.0
1400.0
1512.6
1580.0
1831.4
2800.0
2800.0
4000.0
4000.0
4000.0
5200.0
5200.0
5200.0
8600.0
9200.0
9200.0
26000.0
34000.0
39000.0
-UU£i=*iX<
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
*
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
*
NE
* *
NC
NC
NE
**
it *
* *
* *
a i_ncn=<.
RATIO
.
0.9
3.3
.
.
0.3
3.5
.
18.8
0.5
0.7
,
.
520.0
860.0
2600.0
3900.0
;nrysi
SITE
5
4
3
7
7
1
8
8
8
8
2
7
8
3
7
7
8
7
7
5
5
8
7
4
4
4
4
.
4
3
4
2
2
3
4
5
.
2
.
2
.
2
1
1
1
1
ene TEST=l;K±4 SAMPTYP=DO
SAMPLE
WH-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-03
BR-l-CO
MR-1-17
CF-1-04
SR-1-10
MR-1-02
MR-1-07
CF-1-02
MR-1-11
NERM-50% NO EFFECT
MR-1-25
WH-l-RE
— telf—
— telm —
WH-1-02
CF-1-01
MR-1-19
TEL-SR(ERL*NERM)
SR-3-06
SR-3-02
SR-3-16
SR-3-01
GL-NERM-50% NO EFFECT
SR-3-05
GL-TEL-SR (ERL'NERM)
— erl—
SR-1-03
SR-3-08
BR-1-08
NERH-85% NO EFFECT
BR-1-09
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
SR-3-24
WH-1-01
GL-NERH-85% NO EFFECT
BR-1-07
— pelm —
— pelf—
BR-1-03
— aet4 —
PEL-SR(ERM*NERH)
— aet6 —
GL-PEL-SR (ERM*NERH)
— erm —
— aet2 —
BR-1-01
NEC-MAX NO EFFECT
GL -NEC-MAX NO EFFECT
IH-1-04
GL-ERM-50% EFFECT
ERM- 50% EFFECT
IH-1-03
— aet3 —
— aetl —
IH-1-06
— aet5—
IH-1-07
•acuxiut
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
SURV
100
100
100
100
117
100
100
107
96
84
100
122
109
90
113
116
79
70
138
85
51
95
111
103
100
102
96
104
104
95
38
105
18
102
8
.0
.0
.0
.0
.9
.0
.0
.4
.3
.0
.0
.4
.9
.3
.4
.4
.0
.2
.8
.7
.4
.1
.9
.3
.6
.7
.7
.9
.5
.1
.0
.0
.7
.2
.6
'lax
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
U1NJ.J.S-
GROW
ND
10
10
10
11
10
10
11
11
10
10
12
11
10
11
11
11
75
11
ND
ND
13
10
11
12
12
10
11
10
11
97
10
52
11
ND
= ng/g
TOXG
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
MATURE TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
TOX
47.9 TX
10
62.8 NT 87
NT
TX
NOT 67.8 NT 10 NT
TOX 2.0 TX ND ND
TOX 2.7 TX ND ND
TOX 0.0 TX ND ND
TOX 0.0 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
CONC I
10.0
10.0
10.0
10.0
10.0
10.0
10.0
24.0
34.0
56.0
56.0
57.1
108.0
108.0
110.0
135.9
160.0
188.8
210.0
250.0
270.0
270.0
330.0
330.0
330.0
384.0
400.0
400.0
440.0
440.0
440.0
450.0
470.0
500.0
525.4
551.0
600.0
600.0
600.0
620.0
690.0
690.0
690.0
846.0
862.0
1100.0
1400.0
1580.0
2800.0
2800.0
4000.0
5200.0
8600.0
9200.0
9200.0
26000.0
34000.0
39000.0
JUCt—,
2FFE(
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
NE
NE
SG
NE
NE
* *
NE
* *
*
NE
* *
* *
* it
**
* *
* *
* *
**
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=414 CHEM=Chrysene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=
5 WH-l-CO
9 TR-l-CO
9 TR-1-02
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
3 SR-1-10
9 TR-1-01
5 WH-l-RE
NERM-50% NO EFFECT
— telf—
GL-NERM-50% NO EFFECT
— telm—
3.3 5 WH-1-02
TEL-SR(ERL*NERM)
4 SR-3-06
GL-TEL-SR(ERL*NERM)
9 TR-1-03
4 SR-3-02
4 SR-3-16
4 SR-3-01
1.2 4 SR-3-05
GL-ERL-15% EFFECT
ERL-15% EFFECT
—erl—
3 SR-1-03
GL-NERH-85% NO EFFECT
4 SR-3-08
44.0 2 BR-1-08
NERH-85% NO EFFECT
9 TR-1-04
47.0 2 BR-1-09
3.5 3 SR-1-06
GL-PEL-SR(ERM*NERH)
PEL-SR(ERM*NERH)
4 SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
18.8 5 WH-1-01
69.0 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
—pelm—
-~pelf~~
110.0 2 BR-1-03
—aet4—
—aet6—
—erm—
—aet2—
400.0 2 BR-1-01
520.0 1 IH-1-04
860.0 1 IH-1-03
—aet3—
—aetl—
2600.0 1 IH-1-06
—aet5—
3900.0 1 IH-1-07
117
ieuimeiiL. - uu
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
100.
100.
100.
100.
100.
100.
100.
101.
100.
100.
40.
111.
87.
105.
111.
116.
104.
115.
110.
113.
93.
83.
12.
113.
35.
86.
0
0
0
0
0
0
0
6
0
0
0
8
5
9
8
2
5
6
4
7
4
4
5
3
0
4
UdA I
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
;i\xi o=
GROW
10
ND
ND
10
10
10
10
10
ND
14
11
94
ND
10
10
10
94
95
10
85
ND
90
87
10
13
85
=iiy/y
TOXG MATURE
NT
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
ND
TX
NT
NT
NT
TX
ND
ND
ND
10
10
10
10
33
ND
ND
ND
74
ND
51
16
12
22
23
61
22
ND
0.
0.
14
ND
0.
TOXM
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
NT
NT
TX
NT
NT
TX
ND
TX
NT
NT
ND
TX
TOX
TOX
TOX
TOX
TOX
TOX
77.3 TX
100.0 NT
0.0 TX
1.4 TX
1.4 TX
0.0 TX
85
85
ND
96
68
TX
TX
ND
NT
NT
ND ND
68
0.
ND
0.
0.
ND
NT
TX
ND
NT
NT
ND
-------
rjum^jv
CONC ]
0.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
17.0
20.0
20.0
24.0
24.0
24.0
24.0
26.8
27.0
28.0
30.0
30.0
34.0
40.0
53.0
56.0
57.1
78.0
90.0
100.0
108.0
110.0
110.0
113.0
114.0
150.2
160.0
170.0
205.0
210.0
250.0
270.0
270.0
300.0
330.0
330.0
384.0
400.0
406.2
440.0
440.0
440.0
450.0
470.0
490.0
500.0
500.0
551.0
600.0
600.0
620.0
690.0
690.0
846.0
862.0
1100.0
1400.0
1580.0
2800.0
jur.-'
SFFEt
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
*
NC
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
*
* *
* *
NE
NE
NE
NE
NE
NE
NE
NE
**
NE
NE
NE
*
NE
**
NE
**
*
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=414 CHEM=Chrysene TEST=HA28 SAMPTYP=bottom sediment - total UNITS-
11 TB-l-RE
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
9 TR-1-02
1.0 11 TB-1-03
1.0 11 TB-1-02
1.0 11 TB-1-01
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
0.4 7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-05
0.6 8 CF-1-03
2 BR-l-CO
0.7 7 MR-1-17
11 TB-1-04
8 CF-1-04
6 UM-l-RE
2.4 3 SR-1-10
1.0 7 MR-1-02
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
1.1 7 MR-1-07
8 CF-1-02
1.2 7 MR-1-11
ERL-15% EFFECT
9 TR-1-01
7 MR-1-25
6 UM-1-01
5 WH-l-RE
—telf—
6 UM-1-02
10 MB-l-RE
6 UM-1-03
—telm—
3.3 5 WH-1-02
GL-ERL-15% EFFECT
7.2 8 CF-1-01
4.6 7 MR-1-19
GL-TEL-SR (ERL*NERM)
4 SR-3-06
10 MB-1-03
GL-NERM-50% NO EFFECT
9 TR-1-03
4 SR-3-02
4 SR-3-16
4 SR-3-01
10 MB-1-02
4 SR-3-05
NERH-85% NO EFFECT
~erl—
40.0 3 SR-1-03
PEL-SR(ERM*NERH)
4 SR-3-08
2 BR-1-08
GL-NERH-85% NO EFFECT
9 TR-1-04
2.1 2 BR-1-09
10 MB-1-04
50.0 3 SR-1-06
ERM-50% EFFECT
GL-PEL-SR(ERM'NERH)
4 SR-3-24
GL-NEC-MAX NO EFFECT
18.8 5 WH-1-01
3.1 2 BR-1-07
GL-ERM-50% EFFECT
—pelm—
—pelf—
4.9 2 BR-1-03
—aet4—
—aetS—
—erm—
118
>CU.XUI*
?OXIC
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
=lil. U*.
SURV
100.0
100.0
100.0
100.0
100.0
52.3
11.4
0.0
100.0
100.0
100.0
108.1
100.0
100.0
120.3
114.9
123.0
100.0
115.1
93.2
128.4
86.5
100.0
109.3
91.9
102.7
90.7
81.4
109.3
119.3
109.5
117.9
100.0
114.9
36.5
64.9
114.0
100.0
95.5
98.6
103.8
96.1
97.4
97.0
96.1
96.2
88.3
97.4
82.9
88.2
95.5
10.3
102.6
71.7
80.3
juax i
TOXS
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
JJ.NAJ.O-
GROW
10
10
ND
ND
ND
97
72
ND
10
10
10
79
10
10
10
98
82
10
92
10
10
ND
97
92
91
94
58
ND
95
ND
11
ND
ND
ND
74
73
89
92
ND
ND
10
10
94
ND
94
91
92
10
ND
92
ND
60
10
91
85
•iiu/y
TOXG
NT
NT
ND
ND
ND
NT
TX
ND
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
ND
TX
TX
TX
NT
TX
ND
NT
ND
NT
ND
ND
ND
TX
TX
TX
NT
ND
ND
NT
NT
NT
ND
NT
TX
NT
NT
ND
NT
ND
rx
NT
NT
rx
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
68
10
10
90
77
93
10
65
ND
80
ND
10
95
31
48
24
ND
12
ND
ND
ND
ND
ND
ND
25
63
96
ND
ND
10
95
11
ND
11
10
95
10
ND
10
ND
37
10
ND
10
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
TX
NT
TX
ND
NT
ND
ND
ND
ND
ND
ND
TX
NT
NT
ND
ND
NT
NT
NT
ND
NT
NT
NT
NT
ND
NT
ND
TX
NT
ND
NT
TOX
79.0 TX
85
TX
10
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 119
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=414 CHEM=Chrysene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
2800.
3000,
3000,
4000,
5200,
8600,
9200.
9200.
26000,
34000,
39000,
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
* *
* *
* *
**
**
17.8
520.0
860.0
.
.
2600.0
.
3900.0
10
2
1
1
1
1
— aet2 —
MB-1-01
NEC-MAX NO EFFECT
BR-1-01
IH-1-04
IH-1-03
— aet3 —
— aetl— -
IH-1-06
— aet5—
IH-1-07
NOT
TOX
TOX
TOX
TOX
TOX
75,
89,
0
1,
1,
0,
.8
.5
.0
.4
.4
.0
NT
TX
TX
TX
TX
TX
ND
96
ND
96
68
ND
ND
NT
ND
NT
NT
ND
ND
10
ND
0.
0.
ND
ND
NT
ND
NT
NT
ND
-------
w urauuLU
CONC
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
12.5
15.0
25.0
31.9
41.0
48.0
51.2
84.0
88.8
160.0
210.0
210.0
210.0
219.8
220.0
230.0
230.0
250.0
250.0
270.0
280.0
350.0
350.0
430.0
440.0
440.0
440.0
460.0
470.0
620.0
763.0
782.0
1580.0
1600.0
1600.0
1600.0
1724.8
1933.9
3000.0
3600.0
5800.0
5800.0
5800.0
7000.0
8500.0
8500.0
10000.0
18200.0
21000.0
22000.0
1=«JL /
EFFE(
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
*
NE
NE
NE
NE
NE
NE
NC
NE
NE
**
NC
NC
NE
* *
**
* *
25000.0
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=417 CHEM=Benzo(a)pyrene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
3 SR-1-10
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
7 MR-1-25
7 MR-1-17
0.6 7 MR-1-11
7 MR-1-07
7 MR-1-02
7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
8 CF-1-05
8 CF-1-04
8 CF-1-03
2 BR-l-CO
NERM-50% NO EFFECT
8 CF-1-02
1.0 5 WH-1-02
—telf—
5 WH-l-RE
7 MR-1-19
TEL-SR(ERL*NERM)
8 CF-1-01
—telm—
4 SR-3-06
2.1 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
4 SR-3-05
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
4 SR-3-02
4 SR-3-01
3 SR-1-03
0.2 2 BR-1-08
NERH-85% NO EFFECT
——er\*-—
4 SR-3-24
2 BR-1-09
GL-NERH-85% NO EFFECT
18.0 5 WH-1-01
0.2 2 BR-1-03
0.3 2 BR-1-07
—pelm—
—pelf—
—aet6—
—erm—
—aet4—
—aet2—
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
—aetl—
—aet3—
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
700.0 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
1000.0 1 IH-1-03
—aet5—
2100.0 1 IH-1-07
—eqp—
2500.0 1 IH-1-06
120
,1111 O^V
roxic
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
.A .1.1111^1 IV
SURV
90.3
100.0
100.0
100.0
100.0
138.8
122.4
70.2
116.4
113.4
117.9
100.0
100.0
107.4
96.3
109.9
84.0
100.0
79.0
51.4
85.7
111.9
95.1
103.3
18.7
104.9
102.7
95.1
100.6
96.7
104.5
38.0
102.2
105.0
8.6
62.8
47.9
UWU(
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
3.± Vi^J
GROW
10
ND
10
10
10
11
12
75
11
11
11
10
10
11
11
11
10
10
11
_ND
ND
10
13
11
52
11
12
11
12
10
10
97
11
10
ND
87
10
. ID— IU
TOXG
NT
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
NT
j/y
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT 67.8 NT 10 NT ND ND
TOX
TOX
TOX
TOX
2.0 TX ND
(TO
ND
2.7 TX ND !JD ND
0.0 TX ND MD ND
0.0 TX ND .SD ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=HA14 SAMPTYP=bottom sediment -
CONC EFFECT RATIO SITE SAMPLE C
121
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
24.0
25.0
31.9
41.0
41.0
62.0
80.0
88.8
100.5
119.8
160.0
187.5
210.0
220.0
230.0
250.0
250.0
250.0
270.0
270.0
280.0
350.0
350.
350.
393.
409.
430.
440.
440.
440.0
440.0
460.0
470.0
620.0
620.0
620.0
763.0
782.0
1580.0
1600.0
1600.0
1600.0
3000.0
3600.0
5800.0
7000.0
10000.0
18200.0
21000.0
22000.0
25000.0
NE . 3 SR-1-10
NE . 5 WH-l-CO
NE . 9 TR-l-CO
NE . 9 TR-1-02
NE . 4 SR-3-CO
NE . 3 SR-l-CO
NE . 1 IH-l-CO
NE . 2 BR-l-CO
NE . 9 TR-1-01
NC 1.0 5 WH-1-02
—telf—
NE . 5 WH-l-RE
NERM-50% NO EFFECT
NE . 9 TR-1-04
NE . 9 TR-1-03
—telm—
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
NE . 4 SR-3-06
GL-TEL-SR(ERL*NERM)
* 2.1 3 SR-1-06
NC 1.0 4 SR-3-05
NE . 4 SR-3-16
NE . 4 SR-3-08
NE . 4 SR-3-02
NERH-85% NO EFFECT
NE . 4 SR-3-01
GL-NERH-85% NO EFFECT
NE . 3 SR-1-03
** 35.0 2 BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
—erl—
NE . 4 SR-3-24
** 44.0 2 BR-1-09
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
** 18.0 5 WH-1-01
** 47.0 2 BR-1-03
** 62.0 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
—pelm—
~-pelf~~
—aet6—
—erm—
—aet4—
—aet2—
—aetl—
—aet3—
** 580.0 2 BR-1-01
** 700.0 1 IH-1-04
** 1000.0 1 IH-1-03
—aet5—
** 2100.0 1 IH-1-07
—eqp—
** 2500.0 1 IH-1-06
>m sec
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
nment -
SURV
101.6
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
40.0
100.0
93.4
87.5
111.8
12.5
104.5
111.8
110.4
105.9
116.2
115.6
113.7
113.3
83.4
35.0
77.3
86.4
COte
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
iX U1MJ
GROW
10
10
ND
ND
10
10
10
10
ND
11
14
ND
ND
94
87
94
10
10
10
10
95
85
10
90
13
85
85
Lii3=ng
TOXG
NT
NT
ND
ND
NT
NT
NT
NT
ND
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
/g
MATURE
33
ND
ND
ND
10
10
10
10
ND
ND
ND
ND
ND
74
0.
22
16
61
51
12
23
22
14
0.
ND
68
0.
TOXM
NT
ND
ND
ND
NT
NT
NT
NT
ND
ND
ND
ND
ND
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
ND
NT
TX
TOX 100.0 NT 85 TX 0. TX
TOX 0.0 TX ND ND ND ND
TOX 1.4 TX 96 NT 0. NT
TOX 0.0 TX ND ND ND ND
TOX 1.4 TX 68 NT 0. NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 [ * 2-4 | **>4
NDMCODE=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
122
0.0
6.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
12.5
15.0
20.0
20.0
20.0
24.0
25.0
30.0
31.9
32.
41.
48.
.4
.0
.0
56.0
62.0
80.0
82.0
84.0
84.0
87.0
88.8
100.0
100.0
100.5
160.0
167.7
180.0
210.0
220.0
220.0
230.0
250.0
250.0
270.0
270.0
280.0
280.0
319.8
350.0
409.1
430.0
440.0
440.0
440.0
460.0
465.0
470.0
620.0
620.0
763.0
782.0
1000.0
1000.0
1580.0
NE . 11 TB-l-RE
NC 0.6 3 SR-1-10
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 9 TR-l-CO
NE . 9 TR-1-02
NC 1.0 11 TB-1-03
NC 1.0 11 TB-1-01
NE . 4 SR-3-CO
NE . 3 SR-l-CO
NE . 7 MR-l-CO
NE . 7 MR-1-25
NG 1.0 7 MR-1-17
NG 1.0 7 MR-1-11
NG 1.0 7 MR-1-07
NG 1.0 7 MR-1-02
NG 1.0 7 MR-1-01
NE . 1 IH-l-CO
NE . 8 CF-l-CO
NE . 8 CF-1-06
NE . 8 CF-1-05
NE . 8 CF-1-04
NC 0.9 8 CF-1-03
NE . 2 BR-l-CO
NERM-50% NO EFFECT
NE . 8 CF-1-02
NE . 6 UM-l-RE
NE . 11 TB-1-04
SG 2.0 11 TB-1-02
NE . 9 TR-1-01
NC 1.0 5 WH-1-02
NE . 6 UM-1-01
—telf—
TEL-SR(ERL*NERM)
NE . 5 WH-l-RE
** 4.8 7 MR-1-19
NE . 6 UM-1-02
NE . 9 TR-1-04
NE . 9 TR-1-03
NE . 6 UM-1-03
** 7.6 8 CF-1-01
ERL-15% EFFECT
NE . 10 MB-1-03
—telm—
NE . 10 MB-l-RE
NE . 10 MB-1-02
GL-NERM-50% NO EFFECT
NE . 4 SR-3-06
GL-TEL-SR(ERL*NERM)
NE . 10 MB-1-04
** 21.0 3 SR-1-06
NE . 4 SR-3-05
NERH-85% NO EFFECT
NE . 4 SR-3-16
NE . 4 SR-3-08
NE . 4 SR-3-02
NE . 4 SR-3-01
GL-NERH-85% NO EFFECT
** 28.0 3 SR-1-03
GL-ERL-15% EFFECT
PEL-SR(ERM*NERH)
NE . 2 BR-1-08
GL-PEL-SR(ERM*NERH)
—erl—
NE . 4 SR-3-24
* 2.4 2 BR-1-09
GL-NEC-MAX NO EFFECT
** 18.0 5 WH-1-01
ERM-50% EFFECT
* 2.6 2 BR-1-03
* 3.4 2 BR-1-07
GL-ERM-50% EFFECT
—pelm—
—pelf—
NE . 10 MB-1-01
NEC-MAX NO EFFECT
—aet6—
raxic
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
SURV
100.0
100.0
100.0
100.0
100.0
100.0
52.3
0.0
100.0
100.0
100.0
109.3
115.1
90.7
91.9
109.3
108.1
100.0
100.0
120.3
114.9
128.4
123.0
100.0
102.7
86.5
93.2
11.4
81.4
36.5
119.3
109.5
114.0
117.9
82.9
98.6
114.9
64.9
95.5
100.0
97.0
100.0
95.5
10.3
96.1
96.1
88.3
103.8
97.4
Wl-t
TOXS
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
AX Wntj
GROW
10
97
10
ND
ND
ND
97
ND
10
10
10
95
92
58
91
92
79
10
10
10
98
10
82
10
94
ND
10
72
ND
74
ND
11
89
ND
ND
ND
ND
73
ND
ND
ND
92
ND
60
94
10
92
10
94
L L S — 11V
TOXG
NT
TX
NT
ND
ND
ND
NT
ND
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
ND
NT
TX
ND
TX
ND
NT
TX
ND
ND
ND
ND
rx
MD
TO
.ttD
:\FT
ND
TX
NT
NT
NT
]
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
123
CONG EFFECT RATIO SITE SAMPLE
CEN TOXIC
SURV TOXS GROW TOXG MATURE TOXM
1600.0
1600.0
1600.0
3000.0
3600.0
5800.0
7000.0
10000.0
18200.0
21000.0
22000.0
25000.0
32,
700,
1000,
2100,
2500,
.2
.0
.0
.0
.0
2
1
1
1
.
1
— erm —
— aet4 —
— aet2 —
~~aetl~~
— aet3 —
BR-1-01
IH-1-04
IH-1-03
— aet5 —
IH-1-07
— eqp —
IH-1-06
TOX
TOX
TOX
TOX
TOX
89
0
1
0
1
•
.
.5
.0
.4
.
.0
.
.4
TX
TX
TX
TX
TX
96
ND
96
ND
68
NT
ND
NT
ND
NT
10
ND
0.
ND
0.
NT
ND
NT
ND
NT
-------
PENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGH"
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
124
NUMCODE=418 CHEM=Indeno (1,2,3-c,d)pyrene TEST=CR14 SAMPTYP=bottom sediment - totctl UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
17.3
30.0
30.0
30.0
32.0
61.0
78.0
160.0
160.0
160.0
183.3
200.0
210.0
220.0
220.0
230.0
250.0
250.0
250.0
250.0
270.0
280.0
290.0
300.0
520.0
600.0
660.0
690.0
836.7
1218.2
1800.0
2600.0
2800.0
3800.0
3800.0
3800.0
5300.0
5300.0
7300.0
7600.0
11000.0
22000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NC
NE
*
NE
NE
NE
NE
NE
NE
NC
NE
NE
* *
NC
NE
* *
* *
* *
* *
.
.
.
.
.
1.0
1.4
.
0.1
2.0
.
0.2
.
14.3
0.4
.
,
530.0
.
730.0
1100.0
2200.0
5
4
3
3
7
7
7
7
7
7
1
8
8
8
8
8
8
2
7
5
7
5
8
2
4
3
.
4
3
2
4
4
4
2
4
.
4
5
2
.
.
2
1
.
1
1
1
WH-l-CO
SR-3-CO
SR-l-CO
SR-1-10
MR-l-CO
MR-1-25
MR-1-17
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
BR-l-CO
NERM-50% NO EFFECT
MR-1-11
TEL-SR(ERL*NERM)
WH-1-02
MR-1-19
ERL-15% EFFECT
WH-l-RE
CF-1-01
BR-1-08
SR-3-06
SR-1-06
GL-ERL-15% EFFECT
GL-TEL-SR (ERL'NERM)
SR-3-05
GL-NERM-50% NO EFFECT
SR-1-03
BR-1-09
SR-3-16
SR-3-08
SR-3-02
BR-1-07
NERH-85% NO EFFECT
SR-3-01
GL-NERH-85% NO EFFECT
SR-3-24
WH-1-01
BR-1-03
— aet4 —
— aet6 —
— aet2 —
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
— aetl —
— aet3 —
ERM-50% EFFECT
BR-1-01
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-04
GL-ERM-50% EFFECT
IH-1-03
~aet5 —
IH-1-07
IH-1-06
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
100.0
100.0
100.0
90.3
100.0
138.8
122.4
116.4
113.4
117.9
100.0
100.0
107.4
96.3
109.9
84.0
79.0
100.0
70.2
51.4
111.9
85.7
95.1
38.0
103.3
18.7
104.9
104.5
105.0
102.7
95.1
100.6
47.9
96.7
102.2
8.6
62.8
67.8
2.0
2.7
0.0
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
TX
TX
ND
10
10
10
10
11
12
11
11
11
10
10
11
11
11
10
11
10
75
ND
10
ND
13
97
11
52
11
10
10
12
11
12
10
10
11
ND
87
10
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 | **>4
125
NUMCODE=418 CHEM=Indeno (1,2,3-c,d)pyrene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC S0RV TOXS GROW TOXG MATURE TOXM
10
10
10
10
10
10
10
10
10
30
32
78
78
78
86
96
111
160
160
160
160
200
220
220
230
250
250
250
250
260
270
290
290
290
290
300
320
326
410
410
520
600
660
690
1800
2600
3800
5300
7300
7600
11000
22000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.5
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
* *
NE
NE
*
NC
NE
* *
NE
NE
NE
* *
NE
NE
NE
* *
* *
**
**
* *
* *
* *
.
.
1.4
7.8
2.0
1.0
22.0
25.0
14.3
.
.
.
.
52.0
380.0
530.0
730.0
1100.0
2200.0
5
9
9
9
4
3
3
1
2
5
5
2
9
4
3
4
3
2
4
4
4
2
4
9
4
5
2
2
1
1
1
1
WH-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
SR-1-10
IH-l-CO
BR-l-CO
WH-1-02
WH-l-RE
BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
TR-1-03
SR-3-06
SR-1-06
GL-NERM-50% NO EFFECT
SR-3-05
SR-1-03
BR-1-09
SR-3-16
SR-3-08
SR-3-02
BR-1-07
GL-NERH-85% NO EFFECT
NERH-85% NO EFFECT
SR-3-01
TR-1-04
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
WH-1-01
GL-PEL-SR (ERM*NERH)
PEL-SR (ERM*NERH)
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-03
— aet4 —
— aet6 —
— aet2—
— aetl —
— aet3 —
BR-1-01
IH-1-04
IH-1-03
— aet5 —
IH-1-07
IH-1-06
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
100.0
100.0
100.0
100.0
100.0
100.0
101.6
100.0
100.0
40.0
100.0
113.7
87.5
111.8
12.5
104.5
115.6
83.4
111.8
110.4
105.9
86.4
116.2
93.4
113.3
.
.
35.0
.
.
.
77.3
.
.
.
.
100.0
0.0
1.4
.
0.0
1.4
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
10
ND
ND
ND
10
10
10
10
10
11
14
85
ND
94
87
94
95
90
10
10
10
85
10
ND
10
13
85
85
ND
96
ND
68
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
ND
NT
NT
TX
TX
ND
NT
ND
NT
ND
ND
ND
ND
10
10
33
10
10
ND
ND
22
ND
74
0.
22
23
0.
16
61
51
0.
12
ND
14
ND
68
0.
ND
0.
ND
0.
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
ND
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
ND
NT
ND
NT
TX
ND
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 I **>4
126
NUMCODE=418 CHEM=Indeno (1,2,3-c,djpyrene TEST=HA28 SAMPTYP=bottom sediment - totcl UNITS=ng/g
CONG EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
7.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
17.3
28.0
30.0
30.0
30.0
32.0
50.0
59.0
61.0
78.0
78.0
85.0
96.0
100.0
111.7
120.0
160.0
160.0
160.0
160.0
200.0
220.0
220.0
230.0
230.0
239.8
250.0
250.0
250.0
250.0
250.0
270.0
290.0
290.0
290.0
300.0
320.2
410.0
520.0
600.0
660.0
690.0
770.0
770.0
1800.0
2600.0
3800.0
5300.0
7300.0
7600.0
11000.0
22000.0
NE
NE
NE
NE
NE
NE
NE
NE
NG
NE
NE
NG
NG
NG
NG
NE
NE
NE
NE
NE
NG
NE
NE
SG
NE
SG
*
NE
NE
NE
* *
NE
NE
NE
NE
NE
NE
NE
* *
NE
* *
it *
NE
NE
NE
* *
NE
NE
NE
* *
* *
NE
* *
* *
* *
* *
* *
.
.
1.0
1.0
1.0
1.0
1.0
1.0
1.3
1.4
3.0
6.1
.
.
.
16.0
22.0
5.0
.
.
5.7
.
.
14.3
.
11.8
86.4
530.0
730.0
1100.0
2200.0
6
5
6
9
9
9
4
3
3
7
7
7
7
7
7
1
8
8
8
8
8
8
2
7
6
5
7
5
6
6
8
2
.
10
10
10
10
9
4
3
.
4
3
2
4
.
4
4
2
.
4
9
4
5
,
2
.
10
.
2
1
1
1
1
UM-l-RE
WH-l-CO
UM-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
SR-1-10
MR-l-CO
MR-1-25
MR-1-17
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
BR-l-CO
NERM-50% NO EFFECT
MR-1-11
TEL-SR(ERL*NERM)
UM-1-01
WH-1-02
MR-1-19
ERL-15% EFFECT
WH-l-RE
UM-1-02
UM-1-03
CF-1-01
BR-1-08
GL-NERM-50% NO EFFECT
MB-l-RE
MB-1-04
MB-1-02
GL-TEL-SR (ERL*NERM)
MB-1-03
TR-1-03
SR-3-06
SR-1-06
GL-ERL-15% EFFECT
SR-3-05
SR-1-03
BR-1-09
SR-3-16
NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
SR-3-08
SR-3-02
BR-1-07
GL-NERH-85% NO EFFECT
ERM-50% EFFECT
SR-3-01
TR-1-04
SR-3-24
GL-NEC-MAX NO EFFECT
WH-1-01
GL- PEL- SR ( ERM*NERH )
GL-ERM-50% EFFECT
BR-1-03
— aet4 —
— aet6 —
— aet2 —
MB-1-01
NEC-MAX NO EFFECT
— aetl—
— aet3 —
BR-1-01
IH-1-04
IH-1-03
— aetS —
IH-1-07
IH-1-06
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
86.5
100.0
100.0
100.0
100.0
81.4
100.0
100.0
100.0
100.0
109.3
115.1
91.9
109.3
108.1
100.0
100.0
120.3
114.9
128.4
123.0
102.7
100.0
90.7
119.3
36.5
114.0
109.5
117.9
114.9
64.9
97.4
100.0
95.5
97.0
95.5
98.6
100.0
10.3
96.1
96.2
88.2
96.1
88.3
103.8
80.3
97.4
82.9
102.6
71.7
t
79.0
75.8
89.5
0.0
1.4
0.0
1.4
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
TX
ND
10
ND
ND
ND
ND
10
10
97
10
95
92
91
92
79
10
10
10
98
10
82
94
10
58
ND
74
89
11
ND
ND
73
10
ND
ND
ND
ND
ND
92
60
94
91
92
10
92
10
85
94
ND
10
91
85
ND
96
ND
96
ND
68
ND
NT
ND
ND
ND
ND
NT
NT
TX
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
ND
TX
TX
NT
ND
ND
TX
NT
ND
ND
ND
ND
ND
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
ND
NT
NT
TX
ND
NT
ND
NT
ND
NT
ND
ND
ND
ND
ND
ND
10
10
10
10
12
65
31
95
68
10
10
90
77
80
93
48
10
24
ND
ND
63
ND
ND
ND
25
10
ND
ND
ND
ND
ND
96
37
11
10
10
95
95
10
10
11
ND
10
ND
10
ND
10
ND
0.
ND
0.
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
ND
ND
ND
TX
NT
ND
ND
ND
ND
ND
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
ND
NT
ND
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo (g,h, Dperylene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
127
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
14.0
18.0
18.0
19.0
19.0
26.0
30.0
42.0
62.0
64.0
74.2
91.0
160.0
200.0
215.0
230.0
240.0
249.7
250.0
250.0
260.0
260.0
270.0
290.0
290.0
290.0
290.0
300.0
300.0
310.0
600.0
620.0
670.0
720.0
1279.8
1374.8
1400.0
2600.0
3800.0
3800.0
3800.0
6300.0
6300.0
6300.0
9600.0
18200.0
21000.0
28000.0
NE . 5 WH-l-CO
NE . 4 SR-3-CO
NE . 3 SR-l-CO
NE . 7 MR-l-CO
NE . 7 MR-1-17
NC 0.9 7 MR-1-11
NE . 7 MR-1-07
NE . 7 MR-1-02
NE . 7 MR-1-01
NE . 1 IH-l-CO
NE . 8 CF-l-CO
NE . 8 CF-1-05
NE . 2 BR-l-CO
NE . 3 SR-1-10
NE . 7 MR-1-25
NE . 7 MR-1-19
NE . 8 CF-1-03
NE . 8 CF-1-06
NERM-50% NO EFFECT
NE . 5 WH-l-RE
SG 1.7 5 WH-1-02
NE . 8 CF-1-02
NE . 8 CF-1-01
NE . 8 CF-1-04
TEL-SR(ERL*NERM)
NC 0.1 2 BR-1-08
NE . 4 SR-3-06
NE . 4 SR-3-05
GL-NERM-50% NO EFFECT
NE . 4 SR-3-16
NE . 2 BR-1-09
GL-TEL-SR(ERL*NERM)
NE . 4 SR-3-08
NE . 4 SR-3-02
NC 0.2 2 BR-1-07
NERH-85% NO EFFECT
NE . 4 SR-3-01
NE . 4 SR-3-24
* 2.6 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
** 16.7 5 WH-1-01
GL-NERH-85% NO EFFECT
NE . 3 SR-1-03
—aet6—
NC 0.5 2 BR-1-03
—aet4—
—aet2—
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
—aetl—
—aet3—
NE . 2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
** 630.0 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
** 960.0 1 IH-1-03
—aet5—
** 2100.0 1 IH-1-07
** 2800.0 1 IH-1-06
Jttum seu.uiieii
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
100.
100.
100.
100.
122.
70.
116.
113.
117.
100.
100.
96.
100.
90.
138.
111.
84.
107.
85.
51.
79.
95.
109.
38.
103.
104.
102.
105.
95.
100.
47.
96.
102.
18.
8.
104.
62.
0
0
0
0
4
2
4
4
9
0
0
3
0
3
8
9
0
4
7
4
0
1
9
0
3
9
7
0
1
6
9
7
2
7
6
5
8
c. - i
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
-UL.CU.
GROW
ND
10
10
10
12
75
11
11
11
10
10
11
10
10
11
10
10
11
ND
ND
11
13
11
97
11
11
12
10
11
12
10
10
11
52
ND
10
87
U1N X J. i>
TOXG
ND
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
TX
=iiU/ U
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT 67.8 NT 10 NT ND ND
TOX 2.0 TX ND ND ND ND
TOX 2.7 TX ND ND ND ND
TOX 0.0 TX ND ND ND ND
TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h,i)perylene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE
128
10
10
10
10
10
10
10
10
13
26
30
88
89
91
91
91
120
150
160
160
200
230
240
250
250
260
260
265
270
270
290
290
300
310
310
310
349
352
460
460
600
620
670
720
1400
2600
3800
6300
9600
18200
21000
28000
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.0
.0
.7
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.1
.4
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
**
NE
NE
NC
NE
* *
NE
NE
NE
* *
NE
NE
*
* *
NE
* *
* *
* *
* *
* *
* *
.
.
.
.
1.7
9.1
.
1.0
24.0
26.0
.
.
2.6
16.7
.
.
62.0
.
380.0
630.0
960.0
2100.0
2800.0
5
9
9
9
4
3
1
2
3
5
5
2
,
9
4
4
4
2
4
4
9
2
4
4
3
5
3
2
.
2
1
1
1
1
WH-l-CO
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-10
WH-l-RE
WH-1-02
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
BR-1-08
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
TR-1-03
SR-3-06
GL-NERM-50% NO EFFECT
SR-3-05
SR-3-16
BR-1-09
SR-3-08
SR-3-02
TR-1-04
BR-1-07
NERH-85% NO EFFECT
SR-3-01
GL-NERH-85% NO EFFECT
SR-3-24
SR-1-06
WH-1-01
SR-1-03
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM'NERH)
GL-ERM-50% EFFECT
ERM-50% EFFECT
— aet6—
BR-1-03
— aet4 —
— aet2 —
— aetl —
— aet3 —
BR-1-01
IH-1-04
IH-1-03
— aet5 —
IH-1-07
IH-1-06
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
100
100
100
100
100
100
100
100
101
100
40
113
87
111
104
111
83
110
105
93
86
116
113
12
35
115
77
100
0
1
0
1
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.
.7
.5
.8
.5
.8
.4
.4
.9
.4
.4
.
.2
.3
.5
.0
.6
.3
t
.0
.0
.4
.
.0
.4
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
TX
TX
TX
TX
10
ND
ND
ND
10
10
10
10
10
14
11
85
ND
94
94
10
90
10
10
ND
85
10
10
87
13
95
85
85
ND
96
ND
68
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
TX
NT
NT
ND
TX
NT
NT
NT
NT
NT
TX
TX
ND
NT
ND
NT
ND
ND
ND
ND
10
10
10
10
33
ND
ND
22
ND
74
22
16
0.
61
51
ND
0.
12
14
0.
ND
23
68
0.
ND
0.
ND
0.
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
ND
NT
TX
NT
TX
NT
NT
ND
TX
NT
NT
NT
ND
NT
NT
TX
ND
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h,i)perylene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
129
0.0
7.0
10.0
10.0
10.0
10.0
10.0
10.
10.
10.
10.
10.
10.
10.
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
13.0
13.0
14.0
15.5
18.0
18.0
18.5
19.0
20.0
26.0
30.0
30.0
33.0
42.0
50.0
61.4
62.0
64.0
64.0
91.0
94.0
100.0
100.0
120.0
125.5
150.0
160.0
200.0
230.0
230.0
240.0
250.0
250.0
250.0
251.5
260.0
260.0
270.0
275.0
278.4
290.0
290.0
290.0
300.0
310.0
310.0
600.0
620.0
670.0
720.0
1200.0
1200.0
1400.0
2600.0
3800.0
NE . 11 TB-l-RE
NE . 6 UM-l-RE
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 9 TR-l-CO
NE . 9 TR-1-02
NE . 9 TR-1-01
NE . 11 TB-1-04
SG 2.0 11 TB-1-02
SG 2.0 11 TB-1-01
NE . 4 SR-3-CO
NE . 3 SR-l-CO
NE . 7 MR-l-CO
NC 0.8 7 MR-1-17
NC 0.8 7 MR-1-11
NC 0.8 7 MR-1-07
NC 0.8 7 MR-1-02
NC 0.8 7 MR-1-01
NE . 1 IH-l-CO
NE . 8 CF-l-CO
NE . 8 CF-1-05
NE . 2 BR-l-CO
SG 1.3 3 SR-1-10
ERL-15% EFFECT
NE . 7 MR-1-25
TEL-SR(ERL*NERM)
SG 1.5 7 MR-1-19
NC 0.6 8 CF-1-03
NERM-50% NO EFFECT
NE . 8 CF-1-06
4.0 11 TB-1-03
NE . 5 WH-l-RE
SG 1.7 5 WH-1-02
GL-ERL-15% EFFECT
NE . 6 UM-1-01
NE . 8 CF-1-02
NE . 6 UM-1-02
GL-TEL-SR (ERL*NERM)
* 2.1 8 CF-1-01
NE . 6 UM-1-03
NE . 8 CF-1-04
NE . 2 BR-1-08
NE . 10 MB-l-RE
NE . 10 MB-1-03
NE . 10 MB-1-02
NE . 10 MB-1-04
GL-NERM-50% NO EFFECT
NE . 9 TR-1-03
NE . 4 SR-3-06
NE . 4 SR-3-05
NE . 4 SR-3-16
NERH-85% NO EFFECT
** 4.8 2 BR-1-09
NE . 4 SR-3-08
NE . 4 SR-3-02
GL-NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
NE . 9 TR-1-04
** 5.1 2 BR-1-07
NE . 4 SR-3-01
ERM-50% EFFECT
GL-PEL-SR(ERM'NERH)
NE . 4 SR-3-24
** 29.0 3 SR-1-06
GL-NEC-MAX NO EFFECT
** 16.7 5 WH-1-01
** 31.0 3 SR-1-03
GL-ERM-50% EFFECT
—aet6—
** 12.3 2 BR-1-03
—aet4—
—aet2—
NE . 10 MB-1-01
NEC-MAX NO EFFECT
—aetl—
—aet3—
** 75.2 2 BR-1-01
it. torn
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
seuiiuexi
SURV
100.0
86.5
100.0
100.0
100.0
100.0
81.4
93.2
11.4
0.0
100.0
100.0
100.0
115.1
90.7
91.9
109.3
108.1
100.0
100.0
114.9
100.0
100.0
109.3
114.0
123.0
120.3
52.3
109.5
36.5
119.3
102.7
117.9
64.9
114.9
128.4
97.4
100.0
95.5
97.0
95.5
98.6
100.0
96.1
96.1
88.2
88.3
103.8
82.9
80.3
97.4
102.6
10.3
71.7
96.2
u - i
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
TX
NT
,UUCii
GROW
10
ND
10
ND
ND
ND
ND
10
72
ND
10
10
10
92
58
91
92
79
10
10
98
10
97
95
89
82
10
97
11
74
ND
94
ND
73
ND
10
10
ND
ND
ND
ND
ND
92
94
10
92
92
10
ND
85
94
10
60
91
91
UiM J. 1 O
TOXG
NT
ND
NT
ND
ND
ND
ND
NT
TX
ND
NT
NT
NT
TX
TX
TX
TX
TX
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
TX
ND
NT
ND
TX
ND
NT
NT
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
ND
TX
NT
NT
TX
NT
TX
=ny / y
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
65
24
31
95
68
10
10
77
10
10
12
63
93
90
ND
ND
ND
ND
48
ND
25
ND
80
10
ND
ND
ND
ND
ND
96
11
95
10
95
10
ND
10
11
10
37
ND
10
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
ND
NT
ND
TX
ND
NT
NT
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
TX
ND
NT
TOX
NOT
TOX
79.0 TX
85
TX
75.8 NT ND ND
89.5 TX
96
NT
10
ND
10
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 130
INCLUDES NBS AND OTHER (—) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h,i)perylene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
6300.0
9600.0
18200.0
21000.0
28000.0
* *
* *
* *
* *
630.0
960.0
2100.0
2800.0
J.
1
.
1
1
IH-1-04
IH-1-03
— aet5 —
IH-1-07
IH-1-06
TOX
TOX
TOX
TOX
0.0
1.4
0.0
1.4
TX
TX
TX
TX
ND
96
ND
68
1JD
NT
1ID
1JT
ND
0.
ND
0.
ND
NT
ND
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=420 CHEM=Benzo(b,k)fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
131
10.0
14.0
14.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
21.0
25.0
25.0
26.0
27.2
37.0
37.0
40.0
40.0
40.0
40.0
71.0
88.0
98.0
102.0
133.0
157.6
158.0
159.0
300.0
350.0
350.0
390.0
400.0
500.0
770.0
920.0
4000.0
4000.0
GL-SECs NOT REPORTED
NE . 9 TR-1-02
NC 0.2 5 WH-1-02
NE . 6 UM-l-RE
NE . 9 TR-l-CO
NE . 11 TB-l-RE
NC 0.7 11 TB-1-01
NE . 4 SR-3-CO
NE . 3 SR-l-CO
NE . 7 MR-l-CO
NE . 7 MR-1-25
NG 1.0 7 MR-1-17
NG 1.0 7 MR-1-07
NG 1.0 7 MR-1-02
NG 1.0 7 MR-1-01
NE . 1 IH-l-CO
NE . 8 CF-l-CO
NE . 8 CF-1-06
NE . 8 CF-1-05
NC 0.8 8 CF-1-03
NE . 2 BR-l-CO
NERM-50% NO EFFECT
NE . 9 TR-1-01
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 8 CF-1-04
TEL-SR(ERL*NERM)
SG 1.9 7 MR-1-11
ERL-15% EFFECT
NE . 11 TB-1-04
SG 1.3 11 TB-1-03
SG 1.3 11 TB-1-02
NE . 8 CF-1-02
ERM-50% EFFECT
NE . 5 WH-l-RE
NE . 6 UM-1-01
** 5.1 7 MR-1-19
NE . 6 UM-1-02
PEL-SR(ERM*NERH)
** 6.3 8 CF-1-01
NE . 6 UM-1-03
NE . 10 MB-1-02
NE . 10 MB-1-03
NERH-85% NO EFFECT
NE . 9 TR-1-03
NE . 10 MB-l-RE
NE . 10 MB-1-04
NE . 9 TR-1-04
** 16.3 5 WH-1-01
NE . 10 MB-1-01
NEC-MAX NO EFFECT
>ottom seaime
'OXIC SURV
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
100.
36.
86.
100.
100.
0.
100.
100.
100.
109.
115.
91.
109.
108.
100.
100.
120.
114.
123.
100.
81.
100.
100.
128.
90.
93.
52.
11.
102.
109.
119.
114.
117.
64.
114.
97.
95.
98.
100.
95.
82.
71.
75.
0
5
5
0
0
0
0
0
0
3
1
9
3
1
0
0
3
9
0
0
4
0
0
4
7
2
3
4
7
5
3
0
9
9
9
0
5
6
0
5
9
7
8
nc -
TOXS
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
cocaj
GROW
ND
74
ND
ND
10
ND
10
10
10
95
92
91
92
79
10
10
10
98
82
_10
ND
10
ND
10
58
10
97
72
94
11
ND
89
ND
73
ND
ND
ND
ND
ND
ND
ND
91
ND
L UKiiTS-ng/g
TOXG MATURE
ND
TX
ND
ND
NT
ND
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
NT
ND
NT
ND
NT
TX
NT
NT
TX
NT
NT
ND
TX
ND
TX
ND
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
10
10
10
12
65
31
95
68
10
10
90
77
93
10
ND
ND
ND
80
24
ND
ND
ND
48
ND
ND
63
ND
25
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
TX
ND
ND
ND
NT
ND
ND
NT
ND
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 132
INCLUDES NBS AND OTHER (—-) SECS
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=422 CHEM=Dibenz(a,h)anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
GL-SECs NOT REPORTED
0.0
2.0
6.2
7.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
10.0
12.0
12.0
15.0
18.0
20.0
22.0
23.0
28.2
50.0
53.0
53.0
62.0
63.4
89.0
93.0
135.0
200.0
200.0
230.0
230.0
260.0
430.0
540.0
870.0
870.0
970.0
3200.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NG
NG
NG
NG
NG
NG
NE
NE
NE
NE
NE
NG
NE
NE
NE
SG
SG
*
NE
NE
NE
NE
NE
**
NE
NE
NE
NE
11
6
6
5
6
9
9
9
11
2.0 11
2.0 11
4
3
7
7
1.0 7
1.0 7
1.0 7
1.0 7
1.0 7
1.0 7
1
8
8
8
8
1.0 8
8
2
5
1.1 5
1.8 8
4.0 11
6
6
.
10
9
10
.
8.1 5
9
10
.
10
10
.
.
TB-l-RE
UM-1-01
— telm —
UM-l-RE
WH-l-CO
UM-l-CO
TR-l-CO
TR-1-02
TR-1-01
TB-1-04
TB-1-02
TB-1-01
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-25
MR-1-19
MR-1-17
MR-1-11
MR-1-07
MR-1-02
MR-1-01
IH-l-CO
CF-l-CO
CF-1-06
CF-l-OS
CF-1-04
CF-1-03
CF-1-02
BR-l-CO
TEL-SR{ERL*NERM)
NERM-50% NO EFFECT
ERL-15% EFFECT
WH-l-RE
WH-1-02
ERM-50% EFFECT
CF-1-01
TB-1-03
UM-1-02
UM-1-03
PEL-SR(ERM*NERH)
MB-1-04
TR-1-03
NERH-85% NO EFFECT
MB-1-03
— erl—
WH-1-01
TR-1-04
— pelm —
MB-1-02
— aet6 —
— aet4 —
— aet2 —
— erm —
MB-l-RE
—aetl —
MB-1-01
NEC-MAX NO EFFECT
— aet3 —
— aetS—
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
@
TOX
TOX
NOT
NOT
@
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
@
100
119
86
100
100
100
100
81
93
11
0
100
100
100
109
114
115
90
91
109
108
100
100
120
114
128
123
102
100
109
36
64
52
117
114
95
98
95
71
82
97
100
75
.0
.3
.5
.0
.0
.0
.0
.4
.2
.4
.0
.0
.0
.0
.3
.0
.1
.7
.9
.3
.1
.0
.0
.3
.9
.4
.0
.7
.0
.5
.5
.9
.3
.9
.9
.
.5
.6
.5
.7
.9
.0
.
.
.0
.
.8
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
10
ND
ND
10
ND
ND
ND
ND
10
72
ND
10
10
10
95
89
92
58
91
92
79
10
10
10
98
10
82
94
10
11
74
73
97
ND
ND
ND
ND
ND
91
ND
ND
ND
ND
NT
ND
ND
NT
ND
ND
ND
ND
NT
TX
ND
NT
NT
NT
NT
TX
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
10
10
10
12
63
65
24
31
95
68
10
10
90
77
80
93
48
10
ND
ND
25
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
l^UKt.
CONC I
34.1
160.0
160.0
160.0
160.0
160.0
164.0
166.0
167.0
171.0
171.0
172.0
220.0
225.0
228.0
235.0
251.0
263.0
267.0
271.0
277.0
389.0
588.5
711.0
807.0
1066.0
1297.0
1297.0
1684.0
2000.0
2720.0
3156.0
3553.0
3553.0
4022.0
4081.0
4375.0
4687.5
5000.0
5190.0
5340.0
5420.0
5518.0
5518.0
6380.0
6996.0
8118.0
8498.0
9240.0
13020.0
13660.6
16770.0
21911.2
24000.0
33819.0
44792.0
59140.0
59140.0
84600.0
84600.0
84600.0
108600.0
220000.0
254100.0
528031.0
640000.0
-UlJd-
2FFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
NE
NE
*
NC
NE
NE
NE
NE
NE
NE
NC
* *
NE
NC
* *
NE
**
* *
* *
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=450 CHEM=PAH-T TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
—telf—
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
2 BR-l-CO
8 CF-1-05
7 MR-1-01
7 MR-l-CO
5 WH-l-CO
8 CF-1-03
8 CF-1-06
7 MR-1-17
3 SR-1-10
7 MR-1-07
7 MR-1-25
7 MR-1-02
8 CF-1-04
NERM-50% NO EFFECT
8 CF-1-02
—pelf—
1.3 7 MR-1-11
TEL-SR(ERL*NERM)
5 WH-l-RE
7 MR-1-19
8 CF-1-01
2.9 5 WH-1-02
ERL-15% EFFECT
— telm—
—slcl—
4 SR-3-06
3 SR-1-03
3.0 3 SR-1-06
GL-ERL-15% EFFECT
ov.i
. ~~*5£.L
GL-TEL-SR(ERL*NERM)
0.1 2 BR-1-08
GL-NERM-50% NO EFFECT
4 SR-3-16
4 SR-3-01
4 SR-3-02
4 SR-3-05
2 BR-1-09
NERH-85% NO EFFECT
4 SR-3-08
0.2 2 BR-1-07
GL-NERH-85% NO EFFECT
19.3 5 WH-1-01
4 SR-3-24
0.4 2 BR-1-03
PEL-SR(ERM'NERH)
—pelm—
GL-PEL-SR(ERM*NERH)
—aet6—
ERM-50% EFFECT
—erm—
369.6 1 IH-1-04
GL-ERM-50% EFFECT
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
678.8 1 IH-1-03
—Slc2 —
1588.1 1 IH-1-06
3300.2 -1 IH-1-07
—aet5—
133
iiment - coca
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
100
100
100
100
100
96
117
100
100
84
107
122
90
116
138
113
109
79
70
85
111
95
51
103
104
18
38
102
96
100
104
105
95
47
8
102
62
.0
.0
.0
.0
.0
.3
.9
.0
.0
.0
.4
.4
.3
.4
.8
.4
.9
.0
.2
.7
.9
.1
.4
.3
.5
.7
.0
.7
.7
.6
.9
.0
.1
.9
.6
.2
.8
J. LUMJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
.is=nc
GROW
10
10
10
10
10
11
11
10
ND
10
11
12
10
11
11
11
11
11
75
ND
10
13
ND
11
10
52
97
12
10
12
11
10
11
10
ND
11
87
f/g
TOXG MATURE
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
ND
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
NOT
TOX
TOX
TOX
2.0 TX ND ND
67.8 NT 10 NT
2.7 TX
ND
0.0 TX ND
0.0 TX ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=450 CHEM=PAH-T TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
134
34.1
160.0
160.0
160.0
160.0
160.0
169.0
171.0
225.0
238.0
277.0
711.0
711.0
1297.0
1589.4
1684.0
1715.5
2000.0
2092.0
2468.8
2720.0
3156.0
3553.0
3553.0
3553.0
4022.0
4051.0
4375.0
5000.0
5190.0
5340.0
5340.0
5340.0
5420.0
5518.0
6380.0
6736.4
6736.4
6996.0
8498.0
8498.0
8498.0
9240.0
9240.0
9240.0
13020.0
16770.0
24000.0
44792.0
59140.0
84600.0
108600.0
220000.0
254100.0
528031.0
640000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
*
NE
* *
NE
NE
NE
SG
* *
NE
* *
* *
NE
* *
* *
* *
* *
* *
* *
2.9
.
3.0
.
.
27.3
1.1
34.5
.
.
43.7
19.3
81.4
369.6
528.8
678.8
1588.1
3300.2
9
4
3
1
2
9
5
3
9
5
5
.
.
.
9
4
3
3
9
2
4
4
4
4
2
4
2
5
.
4
.
2
.
.
.
1
2
1
1
1
.
— telf—
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-02
WH-l-CO
SR-1-10
TR-1-01
— pelf—
WH-l-RE
NERM-50% NO EFFECT
WH-1-02
TEL-SR(ERL*NERM)
— telm—
GL-NERM-50% NO EFFECT
— slcl—
TR-1-03
GL-TEL-SR (ERL*NERM)
SR-3-06
SR-1-03
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
__erl—
TR-1-04
BR-1-08
SR-3-16
SR-3-01
SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-05
BR-1-09
SR-3-08
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
BR-1-07
WH-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
SR-3-24
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
BR-1-03
— pelm —
— aet6 —
— erm —
IH-1-04
BR-1-01
IH-1-03
— slc2—
IH-1-06
IH-1-07
— aet5~
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
.
100.0
100.0
100.0
100.0
100.0
100.0
100.0
101.6
100.0
100.0
40.0
.
87.5
111.8
115.6
12.5
93.4
113.7
111.8
116.2
105.9
104.5
83.4
110.4
.
86.4
35.0
113.3
77.3
.
0.0
100.0
1.4
1.4
0.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
TX
TX
TX
ND
10
10
10
10
ND
10
10
ND
14
11
ND
94
"95
87
ND
85
10
10
10
94
90
10
85
13
10
85
ND
85
96
68
ND
ND
NT
NT
NT
NT
ND
NT
NT
ND
NT
NT
ND
NT
NT
NT
ND
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
ND
TX
NT
NT
ND
ND
10
10
10
10
ND
ND
33
ND
ND
ND
ND
74
23
0.
ND
22
16
12
51
22
0.
61
0.
ND
14
68
ND
0.
0.
0.
ND
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
ND
NT
NT
NT
ND
TX
NT
NT
NT
TX
TX
NT
TX
ND
NT
NT
ND
TX
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
135
iNUEU.
CONC E
20.1
34.1
160.0
160.0
160.0
160.0
160.0
160.0
164.0
166.0
167.0
169.0
171.0
171.0
171.0
172.0
187.0
220.0
225.0
228.0
235.0
238.0
240.0
240.0
251.0
263.0
264.0
271.0
277.0
290.5
310.0
389.0
410.0
440.0
450.0
689.0
711.0
807.0
958.0
1066.0
1297.0
1297.0
1535.0
1684.0
2000.0
2092.0
2145.0
2226.5
2720.0
2879.0
2880.0
3156.0
3368.1
3547.5
3553.0
3599.0
4022.0
4051.0
4375.0
5000.0
5095.0
5190.0
5340.0
5420.0
5420.0
5518.0
6380.0
6786.7
6996.0
8498.0
8498.0
9240.0
9240.0
13020.0
16770.0
24000.0
44792.0
.uurj-
IFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
SG
SG
SG
NE
NE
SG
SG
NE
NE
NE
SG
*
*
NE
NE
NE
**
NE
**
*
NE
NE
NE
NE
NE
**
**
NE
NE
NE
NE
NE
NE
NE
*
NE
*
**
NE
**
NDMCODE=450 CHEM=PAH-T TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
IATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
0
0
1
1
1
1
1
1
2
2
4
5
2
19
22
2
3
19
5
.8
.8
.
.1
.4
.1
.5
.2
.9
.5
.7
.0
.2
.9
.
.
.
.
.7
.2
.
.4
.1
.3
.7
11
9
4
3
1
8
2
8
7
7
9
5
6
8
8
6
7
3
7
7
9
11
7
8
8
11
7
11
11
6
6
5
7
6
8
5
10
9
4
10
10
3
3
10
9
2
4
4
4
4
2
4
2
5
4
2
TB-l-RE
— telf—
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
CF-l-CO
BR-l-CO
CF-1-05
MR-1-01
MR-l-CO
TR-1-02
WH-l-CO
UM-l-CO
CF-1-03
CF-1-06
UM-l-RE
MR-1-17
SR-1-10
MR-1-07
MR-1-25
TR-1-01
TB-1-03
ERL-15% EFFECT
MR-1-02
CF-1-04
TEL-SR(ERL*NERM)
CF-1-02
—pelf—
NERM-50% NO EFFECT
TB-1-04
MR-1-11
TB-1-02
TB-1-01
UM-1-01
UM-1-02
WH-l-RE
MR-1-19
UM-1-03
CF-1-01
WH-1-02
GL-ERL-15% EFFECT
MB-1-03
— telm —
— slcl-r-
TR-1-03
GL-TEL-SR (ERL'NERM)
ERM-50% EFFECT
SR-3-06
MB-l-RE
MB-1-02
SR-1-03
PEL-SR (ERM*NERH)
GL-NERM-50% NO EFFECT
SR-1-06
MB-1-04
~erl~
TR-1-04
BR-1-08
SR-3-16
NERH-85% NO EFFECT
SR-3-01
SR-3-02
SR-3-05
GL -NERH-85% NO EFFECT
BR-1-09
SR-3-08
GL-PEL-SR (ERM*NERH)
BR-1-07
WH-1-01
GL-ERM-50% EFFECT
SR-3-24
GL-NEC-MAX NO EFFECT
BR-1-03
— pelm —
— aet6 —
— erm —
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
100.
.
100.
100.
100.
100.
100.
100.
114.
108.
100.
100.
100.
100.
123.
120.
86.
115.
100.
91.
109.
81.
52.
109.
128.
102.
93.
90.
11.
0.
119.
117.
109.
114.
114.
64.
36.
95.
98.
.
100.
100.
97.
96.
.
10.
95.
82.
97.
96.
97.
103.
96.
88.
88.
80.
71.
102.
79.
0
0
0
0
0
0
0
9
1
0
0
0
0
0
3
5
1
0
9
3
4
3
3
4
7
2
7
4
0
3
9
5
0
9
9
5
5
6
0
0
0
2
3
5
9
4
1
4
8
1
2
3
3
7
6
0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
TX
10
ND
10
10
10
10
10
98
79
10
ND
10
ND
82
10
ND
92
97
91
95
ND
97
92
10
94
10
58
72
ND
ND
ND
11
89
ND
73
74
ND
ND
92
ND
ND
91
60
ND
ND
10
10
94
10
94
92
92
85
91
10
85
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
ND
TX
NT
ND
TX
TX
TX
NT
ND
NT
TX
NT
NT
NT
TX
TX
ND
ND
ND
NT
TX
ND
TX
TX
ND
ND
NT
ND
ND
TX
TX
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
ND
ND
10
10
10
10
10
77
68
10
ND
ND
ND
93
90
ND
65
10
31
12
ND
ND
95
80
48
ND
24
ND
ND
ND
ND
ND
63
ND
25
ND
ND
ND
96
ND
ND
10
37
ND
ND
10
95
11
10
11
10
95
10
ND
10
10
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
NT
ND
NT
NT
TX
NT
ND
ND
NT
NT
NT
ND
TX
ND
ND
ND
ND
ND
NT
ND
TX
ND
ND
ND
NT
ND
ND
NT
TX
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGH?
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 ] NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=450 CHEM=PAH-T TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
136
CONC EFFECT RATIO SITE SAMPLE
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
59140.0
62220.0
62220.
84600.
108600.
220000.
254100.
528031.
640000.0
** 369.6 1 IH-1-04 TOX 0.0
NE . 10 MB-1-01 NOT 75.8
NEC-MAX NO EFFECT
** 37.3 2 BR-1-01 TOX 89.5
** 678.8 1 IH-1-03 TOX 1.4
—Slc2—
** 1588.1 1 IH-1-06 TOX 1.4
** 3300.2 1 IH-1-07 TOX 0.0
—aet5—
TX
NT
TX
TX
TX
TX
ND
ND
96
96
68
ND
ND
IvT
KD
ND
ND
10
0.
0.
ND
ND
ND
NT
NT
NT
ND
-------
JNUPIV
CONC I
60.0
60.0
60.0
60.0
60.0
60.0
61.0
63.0
64.0
66.0
66.0
66.0
67.0
73.0
75.0
80.0
80.0
82.0
84.0
127.0
137.0
191.0
192.0
231.4
312.0
536.0
552.0
653.0
653.0
786.0
811.0
811.0
818.0
922.4
1049.0
1280.0
1346.0
1442.0
2120.0
2160.0
2380.0
2380.0
2530.0
2760.0
2900.0
3040.0
3160.0
3369.0
3720.0
4140.9
5200.0
5200.0
5658.3
7204.5
11000.0
11040.0
11040.0
13000.0
23400.0
24000.0
33600.0
33600.0
33600.0
36100.0
282031.0
,uun-
3FFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
NC
* *
NE
NE
NC
NE
NE
NE
NE
NE
NE
**
NC
**
* *
NE
* it
**
420000.0
APPENDIX 4a: ASCENDING DATA TABLE- >ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=451 CHEM=PAH-L TEST=CR14 SAMPTYP=bottom sediment - total
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
3 SR-1-10
8 CF-1-03
8 CF-1-05
5 WH-l-CO
7 MR-1-01
8 CF-1-04
7 MR-l-CO
8 CF-1-02
7 MR-1-07
7 MR-1-17
7 MR-1-02
NERM-50% NO EFFECT
7 MR-1-25
7 MR-1-19
1.7 7 MR-1-11
5 WH-l-RE
8 CF-1-01
TEL-SR(ERL*NERM)
—telm—
3 SR-1-03
~erl —
3.0 3 SR-1-06
ERL-15% EFFECT
0.1 2 BR-1-08
6.3 5 WH-1-02
GL-ERL-15% EFFECT
2 BR-1-09
GL-TEL-SR(ERL*NERM)
GL-NERM-50% NO EFFECT
4 SR-3-06
0.1 2 BR-1-07
—pelm—
4 SR-3-05
4 SR-3-16
4 SR-3-02
NERH-85% NO EFFECT
4 SR-3-08
4 SR-3-01
GL-NERH-85% NO EFFECT
4 SR-3-24
—erm—
26.2 5 WH-1-01
0.3 2 BR-1-03
PEL-SR (ERM*NERH)
—aet4—
—aet2~
GL-PEL-SR(ERM*NERH)
ERM-50% EFFECT
—aet6—
184.0 1 IH-1-04
GL-ERM-50% EFFECT
—aet3—
390.0 1 IH-1-03
—aetl—
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
601.7 1 IH-1-06
4700.5 1 IH-1-07
—aet5—
137
iimem
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
: - coca
SURV
100.0
100.0
100.0
100.0
107.4
100.0
90.3
84.0
96.3
100.0
117.9
109.9
100.0
79.0
116.4
122.4
113.4
138.8
111.9
70.2
85.7
95.1
104.5
18.7
38.0
51.4
105.0
103.3
47.9
104.9
102.7
100.6
95.1
96.7
102.2
8.6
62.8
J. UWJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
Lis>=nc
GROW
10
10
10
10
11
10
10
10
11
ND
11
11
10
11
11
12
11
11
10
75
ND
13
10
52
97
ND
10
11
10
11
12
12
11
10
11
ND
87
j/g —
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
TOX
NOT
TOX
TOX
2.0 TX ND ND ND ND
2.7 TX ND ND ND ND
67.8 NT 10 NT ND ND
0.0 TX ND ND ND ND
0.0 TX ND ND ND ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 I **>4
138
wur
CONC
60.0
60.0
60.0
60.0
60.0
60.0
60.0
61.0
66.0
191.0
191.0
289.0
312.0
363.5
387.5
534.5
536.0
552.0
653.0
696.0
786.0
786.0
786.0
811.0
818.0
1280.0
1346.0
1442.0
2120.0
2160.0
2380.0
2530.0
2530.0
2530.0
2760.0
2919.5
2919.5
3040.0
3040.0
3040.0
3160.0
3369.0
3369.0
3369.0
3720.0
5200.0
5200.0
11000.0
11040.0
13000.0
23400.0
24000.0
33600.0
36100.0
282031.0
420000.0
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
* *
* *
•**
NE
* *
SG
NE
NE
NE
NE
NE
**
* *
* *
* *
* *
* *
* *
RATIO SITE
9
9
9
4
3
1
2
3
5
5
.
9
.
.
3
3.0 3
9
13.1 2
.
6.3 5
13.6 2
4
22.4 2
.
1.0 4
4
4
4
4
.
.
4
.
26.2 5
62.0 2
.
184.0 1
.
390.0 1
560.0 2
601.7 1
4700.5 1
.
LJ TeST=MA14 SAMPTYP=DOtt
SAMPLE
TR-l-CO
TR-1-02
TR-1-01
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-10
WH-l-CO
WH-l-RE
NERM-50% NO EFFECT
TR-1-03
— telm —
GL-NERM-50% NO EFFECT
TEL-SR (ERL*NERM)
GL-TEL-SR (ERL*NERM)
SR-1-03
— erl—
SR-1-06
TR-1-04
BR-1-08
GL-ERL-15% EFFECT
ERL- 15% EFFECT
WH-1-02
BR-1-09
SR-3-06
BR-1-07
— pelm —
SR-3-05
SR-3-16
SR-3-02
SR-3-08
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
SR-3-01
PEL-SR (ERM*NERH)
GL - PEL- SR ( ERM*NERH )
SR-3-24
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— erm —
WH-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
BR-1-03
— aet4 —
— aet2 —
~aet6 —
IH-1-04
— aet3 —
IH-1-03
— aetl —
BR-1-01
IH-1-06
IH-1-07
— aet5 —
A4-J"t£il u - UU t.d
roxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
100
100
100
100
100
100
100
101
100
100
87
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.5
.A UW.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
na-nc
GROW
ND
ND
ND
10
10
10
10
10
10
14
ND
:/g —
TOXG
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
MATURE TOXM
ND
ND
ND
10
10
10
10
33
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
ND
NOT
NOT
NOT
TOX
TOX
115.6 NT 95
NT
116.2 NT
113.3 NT
35.0 TX
77.3 TX
10
10
13
85
NT
NT
NT
TX
23
12
14
ND
68
NT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
12
93
113
40
83
111
86
104
111
105
110
.5
.4
.7
.0
.4
.8
.4
.5
.8
.9
.4
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
87
ND
85
11
90
94
85
94
10
10
10
NT
ND
TX
NT
TX
NT
TX
NT
NT
NT
NT
0.
ND
22
ND
0.
74
0.
22
16
51
61
NT
ND
TX
ND
TX
NT
TX
TX
NT
NT
NT
NT
NT
ND
NT
TOX
TOX
TOX
TOX
TOX
0
1
100
1
0
.0
.4
.0
.4
.0
TX
TX
NT
TX
TX
ND
96
85
68
ND
ND
NT
TX
NT
ND
ND
0.
0.
0.
ND
ND
NT
TX
NT
ND
-------
1NUI»1Vi
CONC !
0.0
48.0
52.0
60.0
60.0
60.0
60.0
60.0
60.0
60.0
60.0
60.0
60.0
61.0
63.0
64.0
66.0
66.0
66.0
66.0
67.0
70.0
73.0
73.0
73.0
75.0
76.4
80.0
80.0
80.0
84.0
127.0
127.0
135.0
137.0
191.0
192.0
230.0
240.0
289.0
312.0
380.0
480.0
536.0
536.0
552.0
643.0
653.0
653.0
696.0
744.1
786.0
811.0
818.0
1033.0
1176.6
1280.0
1346.0
1442.0
2120.0
2120.0
2160.0
2380.0
2530.0
2530.0
2760.0
2919.5
3040.0
3040.0
3160.0
3369.0
3369.0
3720.0
5200.0
5200.0
11000.0
11040.0
SFFEC
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
SG
SG
NE
SG
NE
NE
SG
NE
*
**
* *
NE
NE
NE
* *
NE
* *
NE
NE
* *
SG
NE
*
NE
NE
NE
NE
NE
NE
* *
* *
* it
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=451 CHEM=PAH-L TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE • C
11 TB-l-RE
6 UM-l-RE
6 UM-1-01
9 TR-l-CO
9 TR-1-02
9 TR-1-01
1.7 11 TB-1-03
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
8 CF-l-CO
8 CF-1-06
2 BR-l-CO
1.0 3 SR-1-10
1.0 8 CF-1-03
8 CF-1-05
5 WH-l-CO
6 UM-l-CO
0.9 7 MR-1-01
8 CF-1-04
7 MR-l-CO
11 TB-1-04
6 UM-1-02
8 CF-1-02
NERM-50% NO EFFECT
1.0 7 MR-1-07
TEL-SR(ERL*NERM)
1.1 7 MR-1-17
1.1 7 MR-1-02
ERL-15% EFFECT
7 MR-1-25
1.7 7 MR-1-19
10 MB-1-03
6 UM-1-03
1.8 7 MR-1-11
5 WH-l-RE
3.0 8 CF-1-01
6.6 11 TB-1-01
6.9 11 TB-1-02
9 TR-1-03
—telm—
10 MB-l-RE
10 MB-1-02
8.9 3 SR-1-03
GL-ERL-15% EFFECT
—erl—
10 MB-1-04
10.9 3 SR-1-06
ERM-50% EFFECT
9 TR-1-04
GL-TEL-SR (ERL'NERM)
2 BR-1-08
6.3 5 WH-1-02
1.9 2 BR-1-09
GL-NERM-50% NO EFFECT
PEL-SR(ERM*NERH)
4 SR-3-06
3.2 2 BR-1-07
—pelm—
4 SR-3-05
NERH-85% NO EFFECT
4 SR-3-16
4 SR-3-02
4 SR-3-08
GL-NERH-85% NO EFFECT
4 SR-3-01
GL-PEL-SR(ERM*NERH)
4 SR-3-24
GL-NEC-MAX NO EFFECT
—erm—
26.2 5 WH-1-01
GL-ERM-50% EFFECT
8.8 2 BR-1-03
—aet4—
—aet2—
—aet6—
184.0 1 IH-1-04
139
nmem
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
; - to
SUR
100.
86.
119.
100.
100.
81.
52.
100.
100.
100.
100.
120.
100.
100.
123.
114.
100.
100.
108.
128.
100.
93.
117.
102.
91.
115.
109.
109.
114.
95.
114.
90.
109.
64.
0.
11.
98.
100.
97.
96.
95.
10.
82.
97.
36.
88.
100.
80.
96.
96.
103.
88.
ua
V
0
5
3
0
0
4
3
0
0
0
0
3
0
0
0
9
0
0
1
4
0
2
9
7
9
1
3
3
0
5
9
7
5
9
0
4
6
0
0
2
5
3
9
4
5
2
0
3
1
1
8
3
J. U1MJ
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
Lia=nt
GROW
10
ND
ND
ND
ND
ND
97
10
10
10
10
10
10
97
82
98
10
ND
79
10
10
10
ND
94
91
92
92
95
89
ND
ND
58
11
73
ND
72
ND
ND
ND
91
ND
60
ND
10
74
92
92
85
94
10
10
92
j/g —
TOXG
NT
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
ND
TX
NT
NT
NT
ND
NT
TX
TX
TX
NT
TX
ND
ND
TX
NT
TX
ND
TX
ND
ND
ND
TX
ND
TX
ND
NT
TX
NT
NT
TX
NT
NT
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
10
10
10
10
90
10
10
93
77
ND
ND
68
80
10
ND
ND
48
31
65
95
12
63
ND
ND
24
ND
25
ND
ND
ND
ND
ND
10
ND
37
ND
10
ND
10
96
10
11
95
10
95
TOXM
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
ND
ND
NT
TX
NT
NT
NT
NT
ND
ND
TX
ND
TX
ND
ND
ND
ND
ND
NT
ND
TX
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
NOT
NOT
TOX
TOX
TOX
97.4 NT
102.6 NT
71.7 TX
79.0 TX
94
10
NT
NT
91 NT
85 TX
0.0 TX ND ND
11
10
ND
10
ND
NT
NT
ND
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 140
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=451 CHEM=PAH-L TEST=HA28 SAMPTYP=bottom sediment - total UNITS=nc/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TCXG MATURE TOXM
13000.0 . . —aet3—
23400.0 ** 390.0 1 IH-1-03 TOX 1.4 TX 96 NT 0. NT
24000.0 . . —aetl—
29380.0 NE . 10 MB-1-01 NOT 75.8 NT ND ND ND ND
29380.0 . . NEC-MAX NO EFFECT
33600.0 ** 79.4 2 BR-1-01 TOX 89.5 TX 96 NT 10 NT
36100.0 ** 601.7 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
282031.0 ** 4700.5 1 IH-1-07 TOX 0.0 TX ND ND ND ND
420000.0 . . —aet5—
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 | **>4
141
NUMUUiJii-^3^ umsra-rAn-
CONC EFFECT RATIO SITE
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
105.0
108.0
112.0
140.0
151.0
153.0
164.0
171.0
197.0
197.5
198.0
252.0
309.8
486.0
486.0
520.0
655.0
680.0
874.0
1440.0
1700.0
2430.0
2620.0
2730.0
2813.7
2840.0
2900.0
2900.0
2960.0
3300.0
3589.0
3850.0
3850.0
4700.0
5129.0
5650.0
5925.0
6200.0
6675.0
9300.0
9600.0
10122.5
12000.0
13000.0
16881.7
17000.0
26614.5
48100.0
48100.0
51000.0
51000.0
51000.0
69000.0
69000.0
85200.0
218000.0
220000.0
246000.0
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NC
NE
NE
* *
NC
NE
NC
* *
NE
* *
* *
**
.
.
.
.
1.2
1.6
.
.
.
.
.
3.0
.
0.2
.
.
16.4
0.3
.
.
0.5
.
481.0
.
.
,
.
.
852.0
2180.0
2460.0
4
3
7
7
1
8
8
2
5
8
8
7
7
7
3
7
8
8
7
5
5
7
8
4
4
3
4
3
4
4
2
4
2
5
2
4
2
.
.
1
2
1
1
1
n rnoi— ci\x^t 3/u'ir A ir--jjtj^^
SAMPLE
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-01
IH-l-CO
CF-l-CO
CF-1-05
BR-l-CO
WH-l-CO
CF-1-03
CF-1-06
MR-1-17
MR-1-25
MR-1-07
SR-1-10
MR-1-02
CF-1-04
NERM-50% NO EFFECT
CF-1-02
MR-1-11
TEL-SR(ERL*NERM)
WH-1-02
ERL-15% EFFECT •
WH-l-RE
— telm —
MR-1-19
CF-1-01
SR-3-06
— erl—
SR-3-01
SR-1-03
GL-NERM-50% NO EFFECT
GL-TEL-SR (ERL*NERM)
SR-3-16
SR-1-06
GL-ERL-15% EFFECT
SR-3-02
SR-3-05
BR-1-08
SR-3-08
NERH-85% NO EFFECT
BR-1-09
WH-1-01
BR-1-07
GL-NERH-85% NO EFFECT
SR-3-24
— pelm —
BR-1-03
— erm —
PEL-SR (ERM*NERH)
— aet4 —
— aet6 —
GL-PEL-SR (ERM'NERH)
— aet2 —
ERM- 50% EFFECT
IH-1-04
GL-ERM-50% EFFECT
BR-1-01
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— aet3 —
— aetl —
IH-1-03
IH-1-06
— aet5 —
IH-1-07
nmem
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
; - t1
SU
100
100
100
117
100
100
96
100
100
84
107
122
138
116
90
113
109
79
70
51
85
111
95
103
96
104
102
18
100
104
38
95
105
8
47
102
62
oca
RV
.0
.0
.0
.9
.0
.0
.3
.0
.0
.0
.4
.4
.8
.4
.3
.4
.9
.0
.2
.4
.7
.9
.1
.3
.7
.5
.7
.7
.6
.9
.0
.1
.0
.6
.9
.2
.8
1 U1MJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
NT
NT
LTS-HC
GROW
10
10
10
11
10
10
11
10
ND
10
11
12
11
11
10
11
11
11
75
ND
ND
10
13
11
10
10
12
52
12
11
97
11
10
ND
10
11
87
j/g --
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
TX
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
NOT
TOX
TOX
TOX
2.0 TX ND ND ND
67.8 NT 10 NT ND
2.7 TX ND
0.0 TX ND
ND
ND
0.0 TX ND ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGH1:'
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
142
IMUJttt
CONC J
100.0
100.0
100.0
100.0
100.0
105.0
109.0
164.0
178.0
486.0
520.0
520.0
655.0
980.0
1228.0
1440.0
1685.8
1700.0
1803.0
2430.0
2620.0
2840.0
2900.0
2900.0
2900.0
2960.0
2960.0
3300.0
3355.0
3355.0
3589.0
3850.0
4089.5
4353.8
4700.0
5129.0
5650.0
5650.0
5650.0
6200.0
6200.0
6200.0
6675.0
9300.0
9600.0
12000.0
13000.0
17000.0
48100.0
51000.0
69000.0
69000.0
85200.0
218000.0
220000.0
246000.0
-UU£i='
3FFEC1:
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
*
NE
SG
NE
**
NE
* *
**
**
NE
* *
**
**
**
* *
**
ID-; i-niira-j
r RATIO i
,
1.6
.
.
.
3.0
.
t
1.2
35.9
47.0
16.4
56.5
93.0
481.0
510.0
.
852.0
2180.0
2460.0
fArl-
3ITE
9
4
3
1
2
5
9
3
9
5
5
.
4
9
4
3
4
3
4
4
9
2
4
2
5
2
4
2
1
2
.
1
1
1
H TES1-HA.L4 5AMFTIf=r>Ott"
1 SAMPLE
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
WH-l-CO
TR-1-02
SR-1-10
TR-1-01
WH-1-02
WH-l-RE
NERM-50% NO EFFECT
— telm—
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
SR-3-06
GL-TEL-SR(ERL*NERM)
— erl—
TR-1-03
SR-3-01
SR-1-03
SR-3-16
SR-1-06
GL-ERL-15% EFFECT
ERL- 15% EFFECT
SR-3-02
GL-NERH-85% NO EFFECT
SR-3-05
TR-1-04
NERH-85% NO EFFECT
BR-1-08
SR-3-08
GL-PEL-SR (ERM'NERH)
PEL-SR(ERM'NERH)
BR-1-09
WH-1-01
BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
SR-3-24
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
— pelm —
BR-1-03
— erm —
— aet4 —
— aet6 —
— aet2 —
IH-1-04
BR-1-01
— aet3 —
— aetl —
IH-1-03
IH-1-06
— aet5 —
IH-1-07
CEN
iJ.it(dJ 1, — L.V L.Q
raXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
100
100
100
100
100
100
100
101
100
40
100
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.^ um.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
L1O — 1U
GROW
ND
10
10
10
10
10
ND
10
ND
11
14
.i/y --
TOXG
ND
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
MATURE TOXM
ND
10
10
10
10
ND
ND
33
ND
ND
ND
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
111.8 NT
87.5 NT
116.2 NT
115.6 NT
111.8 NT
12.5 TX
105.9 NT
104.5 NT
93.4 NT
113.7 NT
110.4 NT
83.4 NT
35.0 TX
86.4 NT
113.3 NT
77.3 TX
94
ND
10
95
10
87
10
94
ND
85
10
90
13
85
10
85
0.0 TX ND
100.0 NT 85
1.4 TX
1.4 TX
0.0 TX
96
68
ND
NT
ND
NT
NT
NT
NT
NT
NT
ND
TX
NT
TX
NT
TX
NT
TX
ND
TX
NT
NT
ND
74
ND
12
23
16
0.
51
22
ND
22
61
0.
ND
0.
14
68
ND
0.
0.
0.
ND
NT
ND
NT
NT
NT
NT
NT
TX
ND
TX
NT
TX
ND
TX
NT
NT
ND
TX
NT
NT
ND
-------
rguri^
CONC I
20.1
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
100.0
105.0
105.0
108.0
109.0
112.0
139.0
140.0
151.0
153.0
164.0
170.0
170.0
171.0
178.0
180.0
193.0
197.0
198.0
210.0
219.0
240.0
252.0
398.0
486.0
486.0
520.0
616.0
655.0
680.0
823.0
874.0
969.7
1408.0
1440.0
1700.0
1747.0
1803.0
1935.0
2338.4
2400.0
2430.0
2499.0
2620.0
2840.0
2900.0
2956.0
2960.0
3130.0
3300.0
3355.0
3589.0
3589.0
3850.0
4503.1
4700.0
5129.0
5650.0
5650.0
6200.0
6200.0
6675.0
9300.0
9600.0
12000.0
13000.0
17000.0
32840.0
-uua-
3FFEC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
SG
NE
SG
SG
SG
SG
NE
SG
NE
NE
SG
NE
*
NE
SG
NE
NE
* *
NE
**
NE
NE
NE
NE
NE
NE
**
NE
**
NE
NE
NE
NE
NE
NE
*
it it
*
NE
**
NE
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=452 CHEM=PAH-H TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE
11 TB-l-RE
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-l-CO
0.8 7 MR-1-01
1 IH-l-CO
8 CF-l-CO
8 CF-1-05
2 BR-l-CO
5 WH-l-CO
6 OM-l-CO
0.8 8 CF-1-03
9 TR-1-02
8 CF-1-06
6 UM-l-RE
1.1 7 MR-1-17
7 MR-1-25
1.2 7 MR-1-07
1.6 3 SR-1-10
1.3 11 TB-1-02
ERL-15% EFFECT
1.4 7 MR-1-02
9 TR-1-01
1.4 11 TB-1-03
TEL-SR (ERL*NERM)
8 CF-1-04
8 CF-1-02
1.6 11 TB-1-01
NERM-50% NO EFFECT
11 TB-1-04
2.0 7 MR-1-11
6 UM-1-01
1.6 5 WH-1-02
GL-ERL-15% EFFECT
5 WH-l-RE
6 OM-1-02
—telm—
5.4 7 MR-1-19
6 UM-1-03
6.2 8 CF-1-01
GL-TEL-SR (ERL*NERM)
10 MB-1-03
4 SR-3-06
~~erl—
ERM-50% EFFECT
9 TR-1-03
GL-NERM-50% NO EFFECT
PEL-SR(ERM*NERH)
10 MB-1-02
4 SR-3-01
10 MB-l-RE
26.2 3 SR-1-03
4 SR-3-16
29.0 3 SR-1-06
10 MB-1-04
4 SR-3-02
NERH-85% NO EFFECT
4 SR-3-05
9 TR-1-04
2 BR-1-08
GL-NERH-85% NO EFFECT
4 SR-3-08
GL-PEL-SR(ERM*NERH)
2.5 2 BR-1-09
16.4 5 WH-1-01
3.1 2 BR-1-07
GL-ERM-50% EFFECT
4 SR-3-24
GL-NEC-MAX NO EFFECT
—pelm—
5.0 2 BR-1-03
—erm—
—aet4—
—aet6—
~~aet2~-
10 MB-1-01
143
nmeni: - tota
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
100.
100.
100.
100.
100.
108.
100.
100.
114.
100.
100.
100.
123.
100.
120.
86.
115.
109.
91.
100.
11.
109.
81.
52.
128.
102.
0.
93.
90.
119.
36.
109.
117.
114.
114.
64.
95.
100.
98.
97.
97.
100.
96.
96.
10.
95.
103.
96.
82.
97.
88.
88.
71.
80.
0
0
0
0
0
1
0
0
9
0
0
0
0
0
3
5
1
3
9
0
4
3
4
3
4
7
0
2
7
3
5
5
9
0
9
9
5
0
6
0
4
0
2
1
3
5
8
1
9
4
3
2
7
3
J. UJN,
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
iTi-nc
GROW
10
ND
10
10
10
79
10
10
98
10
10
ND
82
ND
10
ND
92
95
91
97
72
92
ND
97
10
94
ND
10
58
ND
74
11
ND
89
ND
73
ND
92
ND
ND
94
ND
91
10
60
ND
10
94
ND
10
92
92
91
85
j/g —
TOXG
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
TX
ND
NT
ND
TX
NT
TX
TX
TX
TX
ND
NT
NT
NT
ND
NT
TX
ND
TX
NT
ND
TX
ND
TX
ND
NT
ND
ND
NT
ND
TX
NT
TX
ND
NT
NT
ND
NT
NT
NT
NT
TX
MATURE
ND
ND
10
10
10
68
10
10
77
10
ND
ND
93
ND
90
ND
65
12
31
10
ND
95
ND
ND
80
48
ND
ND
24
ND
ND
ND
ND
63
ND
25
ND
96
ND
ND
11
ND
10
95
37
ND
10
11
ND
10
95
10
ND
10
TOXM
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
NT
ND
NT
NT
TX
NT
ND
NT
ND
ND
NT
NT
ND
ND
TX
ND
ND
ND
ND
NT
ND
TX
ND
NT
ND
ND
NT
ND
NT
NT
TX
ND
NT
NT
ND
NT
NT
NT
ND
NT
NOT
TOX
NOT
102.6 NT
79.0 TX
10
NT
85 TX
75.8 NT ND
ND
10
10
ND
NT
NT
ND
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT 144
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=452 CHEM=PAH-H TEST=HA28 SAMPTYP=bottom sediment - total UNITS=n
-------
APPENDIX 4a: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO DRY WEIGHT
INCLUDES NBS AND OTHER (—) SECs
NE no effect | NC<1 j NG=1 | SG 1-2 | * 2-4 | **>4
145
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
20.0
21.0
21.6
22.7
27.0
30.0
31.6
50.0
50.0
70.0
82.0
82.0
112.0
123.0
130.0
150.0
180.0
189.0
194.0
194.0
244.7
730.0
730.0
730.0
740.0
840.0
1000.0
1100.0
3100.0
8900.0
10600.0
NE
NE
NE
NE
NE
NG
NG
NG
NE
NE
NE
NE
NE
NG
NE
NG
NE
NE
NE
NE
*
NE
NE
NE
* *
NE
* *
* *
* *
9
4
3
7
7
1.0 7
1.0 7
1.0 7
1
8
8
8
8
1.0 8
8
1.0 8
2
6
5
6
2.5 7
5
6
6
.
7.5 7
.
6
13.4 5
36.5 7
f f
163.3 5
.
GL-SECs NOT REPORTED
TR-l-CO
SR-3-CO
SR-l-CO
MR-l-CO
MR-1-25
MR-1-19
MR-1-17
MR-1-02
IH-l-CO
CF-l-CO
CF-1-06
CF-1-05
CF-1-04
CF-1-03
CF-1-02
CF-1-01
BR-l-CO
NERM-50% NO EFFECT
UM-l-RE
— telm —
— erl—
WH-l-CO
UM-l-CO
TEL-SR(ERL*NERM)
MR-1-07
ERL- 15% EFFECT
— slcl—
WH-l-RE
NERH-85% NO EFFECT
UM-1-01
UM-1-03
— aet4 —
MR-1-11
— erm —
— pelm —
UM-1-02
NEC -MAX NO EFFECT
PEL-SR (ERM*NERH)
WH-1-01
MR-1-01
ERM- 50% EFFECT
— aet5 —
— eqp —
— aet3 —
— aet2 —
— aetl —
WH-1-02
— slc2—
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
100.
100.
100.
100.
109.
114.
115.
109.
100.
100.
120.
114.
128.
123.
102.
64.
100.
86.
100.
100.
.
91.
109.
119.
114.
90.
.
117.
71.
108.
36.
0
0
0
0
3
0
1
3
0
0
3
9
4
0
7
9
0
5
0
0
9
5
3
9
7
9
7
1
5
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
ND
10
10
10
95
89
92
92
10
10
10
98
10
82
94
73
10
ND
10
ND
91
11
ND
ND
58
ND
91
79
74
ND
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
ND
NT
ND
TX
NT
ND
ND
TX
ND
NT
TX
TX
ND
10
10
10
12
63
65
95
10
10
90
77
80
93
48
25
10
ND
ND
ND
31
ND
ND
ND
24
ND
ND
68
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
ND
TX
ND
ND
ND
TX
ND
ND
NT
ND
-------
Appendix 4b PAH or PCB data grouped by chemical, test type, sample type, toxicity response, and
sediment concentrations normalized to total organic carbon (TOC; in ascending order).
See legend for Appendix 4a for a description of the headings. An example is included
for benzo[a]pyrene. The computer disk that accompanies the report contains the
electronic version of this entire appendix (file name: "apdx4b.wp").
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
1=404 CHEM=Naphthalene TEST=CR14 SAMPTYP=bottom sediment - total UNIT£=ng/g
,Jffll_Ul«
CONC I
149.3
322.6
347.8
600.0
666.7
833.3
852.9
875.0
882.4
928.6
1000.0
1000.0
1000.0
1000.0
1157.9
1166.7
1166.7
1356.1
1444.4
1545.5
1600.0
1600.0
1615.4
1875.0
1884.6
1909.1
2619.0
2619.0
3157.9
3157.9
3470.6
4055.2
4324.3
5207.5
6944.4
7250.0
7931.0
8235.3
14285.7
14285.7
19230.8
20898.1
23500.0
25250.0
27000.0
30571.3
37876.9
56818.2
56818.2
64285.7
73275.9
80000.0
94805.2
224719.1
224719.1
i=*U<
3FFE(
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
*
•*
NC
*
NE
NE
NE
NC
NE
NE
NC
NE
**
* *
**
NE
**
NE
224719.1
8 CF-1-06
8 CF-1-04
8 CF-1-01
3 SR-1-10
7 MR-1-07
8 CF-l-CO
5 WH-l-RE
7 MR-1-25
8 CF-1-02
8 CF-1-03
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
7 MR-1-17
3 SR-1-03
8 CF-1-05
NERM-50% NO EFFECT
1.1 7 MR-1-11
7 MR-l-CO
5 WH-l-CO
7 MR-1-01
7 MR-1-19
7 MR-1-02
TEL-SR(ERL*NERM)
2 BR-1-09
2.8 3 SR-1-06
ERL-15% EFFECT
2.6 5 WH-1-02
GL-ERL-15% EFFECT
0.0 2 BR-1-08
GL-TEL-SR(ERL*NERM)
3.5 5 WH-1-01
GL-NERM-50% NO EFFECT
4 SR-3-08
4 SR-3-24
4 SR-3-16
0.1 2 BR-1-07
4 SR-3-05
NERH-85% NO EFFECT
4 SR-3-02
PEL-SR(ERM*NERH)
0.3 2 BR-1-03
GL-NERH-85% NO EFFECT
4 SR-3-01
ERM-50% EFFECT
GL-PEL-SR(ERM*NERH)
56.8 1 IH-1-07
GL-ERM-50% EFFECT
64.3 1 IH-1-04
73.3 1 IH-1-06
4 SR-3-06
94.8 1 IH-1-03
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
seam
?OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
nent - i
SURV
107.4
109.9
95.1
90.3
116.4
100.0
85.7
138.8
79.0
84.0
100.0
100.0
100.0
100.0
122.4
104.5
96.3
70.2
100.0
100.0
117.9
111.9
113.4
105.0
18.7
51.4
38.0
8.6
95.1
102.2
102.7
47.9
104.9
100.6
62.8
96.7
0.0
2.0
0.0
103.3
2.7
67.8
:otai
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
TX
NT
TX
NT
UJN1TC
GROW
11
11
13
10
11
10
ND
11
11
10
10
10
10
10
12
10
11
75
10
ND
11
10
11
10
52
ND
97
ND
11
11
12
10
11
12
87
10
ND
ND
ND
11
ND
10
-ng/c
TOXG
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
TX
ND
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
ND
NT
ND
NT
j
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
JNUMi;ULUS=4U4 i
CONG EFFECT
600
852
1000
1000
1000
1000
1000
1166
1600
1600
1909
2000
2047
2619
2619
2619
2642
2666
3157
3333
3333
3470
4324
5750
6944
7250
7931
8235
14285
15867
15867
16306
16758
17468
19230
19230
23500
27000
56818
64285
73275
80000
80000
80000
94805
224719
.0
.9
.0
.0
.0
.0
.0
.7
.0
.0
.1
.0
.1
.0
.0
.0
.7
.7
.9
.3
.3
.6
.3
.0
.4
.0
.0
.3
.7
.6
.6
.9
.2
.5
.8
.8
.0
.0
.2
.7
.9
.0
.0
.0
.2
.1
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
*
NE
NE
*
*
NE
NE
NE
NE
**
NC
NE
**
NE
**
**
**
NE
**
* *
on£.js=j>japi
RATIO £
.
.
,
.
.
.
.
.
.
1.9
.
.
2.8
.
2.6
3.5
3.5
8.2
0.7
.
.
.
23.5
.
56.8
64.3
73.3
.
.
.
94.8
224.7
iui<
5IT1
3
5
9
4
3
1
2
3
5
2
9
3
.
5
9
9
2
5
9
4
4
4
2
4
4
2
4
1
1
1
4
1
2
seaxn
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
aent. - i
SURV
101.6
100.0
100.0
100.0
100.0
100.0
100.0
115.6
100.0
83.4
100.0
.O^dJ.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
uiMir:
GROW
10
14
ND
10
10
10
10
95
10
90
ND
>=ng/t
TOXG
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
ND
j
MATURE
33
ND
ND
10
10
10
10
23
ND
0.
ND
TOXM
NT
ND
ND
NT
NT
NT
NT
NT
ND
TX
ND
TOX
12.5 TX
87
NT
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=Naphthalene TEST=HA14 SAMPTYP=bottom sediment - total
SR-1-10
WH-l-RE
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
SR-1-03
WH-l-CO
GL-NERM-50% NO EFFECT
BR-1-09
TR-1-01
GL-TEL-SR(ERL*NERM)
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
TEL-SR(ERL'NERM)
NERM-50% NO EFFECT
WH-1-02
TR-1-03
TR-1-02
BR-1-08
WH-1-01
TR-1-04
SR-3-08
SR-3-24
SR-3-16
BR-1-07
SR-3-05
GL-ERM-50% EFFECT
ERM-50% EFFECT
PEL-SR(ERM*NERH)
NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
SR-3-02
GL-NERH-85% NO EFFECT
BR-1-03
SR-3-01
IH-1-07
IH-1-04
IH-1-06
SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-03
BR-1-01
NOT 105.9 NT 10 NT
0.
51
NT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
40.0
87.5
100.0
113.7
35.0
93.4
110.4
113.3
111.8
86.4
104.5
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
11
ND
ND
85
13
ND
10
10
10
85
94
NT
ND
ND
TX
NT
ND
NT
NT
NT
TX
NT
ND
ND
ND
22
ND
ND
61
14
16
0.
22
ND
ND
ND
TX
ND
ND
NT
NT
NT
TX
TX
NT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
77,
116.
0.
0.
1.
Ill,
1,
100,
.3
.2
.0
.0
.4
.8
.4
.0
TX
NT
TX
TX
TX
NT
TX
NT
85
10
ND
ND
68
94
96
85
TX
NT
ND
ND
NT
NT
NT
TX
68
12
ND
ND
0.
74
0.
0.
NT
NT
ND
ND
NT
NT
NT
TX
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
JNUniXU
CONC
2.0
149.3
322.6
347.8
600.0
666.7
697.7
750.0
833.3
852.9
875.0
882.4
909.1
909.1
928.6
928.6
1000.0
1000.0
1000.0
1000.0
1000.0
1090.9
1111.1
1133.3
1133.3
1149.9
1157.9
1166.7
1166.7
1166.7
1444.4
1545.5
1600.0
1600.0
1600.0
1615.4
1833.3
1875.0
1909.1
1950.0
2000.0
2619.0
2619.0
2654.2
2689.8
3157.9
3333.3
3333 .3
3470.6
3636.4
3636.4
4324.3
5000.0
5134.6
5750.0
6944.4
7250.0
7250.0
7931.0
8235.3
14285.7
15555.6
19230.8
19230.8
21258.5
23500.0
23500.0
27000.0
56818.2
64285.7
73275.9
80000.0
80000.0
80000.0
94805.2
JB=«U
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
- NUMCODE=404 CHEM=Naphthalene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SDRV TOXS GROW TOXG MATURE TOXM
224719.1 ** 100.5 2 BR-1-01 TOX 89.5 TX 96 NT 10 NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=406 CHEM=Acenaphthene TEST=HA28 SAMPTYP=bottom sediment - total UNIT3=ng/g
GL-SECs NOT REPORTED
6 UM-1-01
8 CF-1-06
7 MR-1-25
8 CF-1-04
6 OM-1-02
10 MB-1-03
0.6 7 MR-1-11
10 MB-l-RE
6 UM-1-03
5 WH-l-RE
0.7 7 MR-1-07
6 UM-l-RE
10 MB-1-02
0.9 7 MR-1-17
8 CF-1-02
0.9 5 WH-1-02
1.3 8 CF-1-03
ERL-15% EFFECT
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
1.3 8 CF-1-01
1.3 7 MR-1-19
8 CF-l-CO
8 CF-1-05
ERM-50% EFFECT
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
2.0 7 MR-1-02
PEL-SR(ERM*NERH)
10 MB-1-04
9 TR-1-01
NERH-85% NO EFFECT
9 TR-1-03
9 TR-1-02
5.4 5 WH-1-01
9 TR-1-04
10 MB-1-01
NEC-MAX NO EFFECT
DIUIW»(JU11=
CONC ]
46.5
149.3
312.5
322.6
333.3
333.3
370.4
375.0
409.1
411.8
416.7
500.0
500.0
526.3
588.2
614.0
714.3
714.3
719.0
723.7
724.6
769.2
833.3
833.3
884.6
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000,0
1000.0
1000.0
1250.0
1330.1
1450.0
2000.0
2000.0
3333.3
3333.3
3783.8
7000.0
31111.1
31111.1
-1UC
3FFEI
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NC
NE
NC
SG
SG
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
*
NE
NE
NE
NE
* *
NE
NE
LI OdAJ
?OXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
SURV
119.3
120.3
109.3
128.4
117.9
95.5
90.7
100.0
114.9
109.5
91.9
86.5
97.0
115.1
102.7
36.5
123.0
64.9
114.0
100.0
114.9
100.0
100.0
100.0
100.0
100.0
100.0
108.1
100.0
100.0
109.3
95.5
81.4
98.6
100.0
71.7
82.9
75.8
i,isua.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
L Ui^-L .
GROW
ND
10
95
10
ND
ND
58
ND
ND
11
91
ND
ND
92
94
74
82
73
89
10
98
10
10
ND
ND
10
10
79
10
10
92
ND
ND
ND
ND
91
ND
ND
L 3— jiy i
TOXG
ND
NT
NT
NT
ND
ND
TX
ND
ND
NT
TX
ND
ND
TX
NT
TX
TX
TX
TX
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
TX
ND
ND
ND
ND
NT
ND
ND
,y
MATURE
ND
90
12
80
ND
ND
24
ND
ND
ND
31
ND
ND
65
48
ND
93
25
63
10
77
10
ND
ND
ND
10
10
68
10
10
95
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
NT
NT
NT
ND
ND
TX
ND
ND
ND
TX
ND
ND
NT
NT
ND
NT
TX
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
iNUJMUV
CONC I
144.9
149.3
312.5
322.6
370.4
416.7
526.3
558.8
588.2
700.0
714.3
769.2
833.3
833.3
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1250.0
1266.7
1543.9
1812.7
2090.9
2516.0
2875.2
2941.2
3285.7
3285.7
3285.7
6944.4
7250.0
7931.0
8235.3
14107.1
14285.7
14285.7
16903.1
19230.8
20000.0
20000.0
20000.0
20112.0
20224.7
20224.7
27000.0
27586.2
31168.8
45945.9
80000.0
80000.0
80000.0
693181.8
JUC,— '
SFFEI
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
*
NE
NE
NE
SG
* *
NE
NE
*
NE
NE
* *
* *
* *
NE
**
:=Fluorene
'=bottom
8 CF-1-01
8 CF-1-06
7 MR-1-25
8 CF-1-04
0.5 7 MR-1-11
7 MR-1-07
7 MR-1-17
5 WH-l-RE
8 CF-1-02
3 SR-1-10
8 CF-1-03
7 MR-1-19
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
7 MR-1-02
3 SR-1-03
2.0 5 WH-1-02
TEL-SR(ERL*NERM)
2 BR-1-09
GL-NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM)
0.4 2 BR-1-08
3.3 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-08
4 SR-3-24
4 SR-3-16
1.1 2 BR-1-07
14.1 1 IH-1-04
4 SR-3-05
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
4 SR-3-02
2.6 2 BR-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
GL-PEL-SR (ERM'NERH)
2 BR-1-01
GL-NERH-85% NO EFFECT
4 SR-3-01
27.6 1 IH-1-06
31.2 1 IH-1-03
58.9 5 WH-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
693.2 1 IH-1-07
;eaim«
?OXIC
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
snt -
SU
95
107
138
109
70
116
122
85
79
90
84
111
100
96
100
100
100
100
117
100
100
113
104
51
105
38
18
95
102
102
47
2
104
100
62
67
96
0
2
8
103
CO
RV
.1
.4
.8
.9
.2
.4
.4
.7
.0
.3
.0
.9
.0
.3
.0
.0
.0
.0
.9
.0
.0
.4
.5
.4
.0
.0
.7
.1
.2
.7
.9
.0
.9
.6
.8
.8
.7
.0
.7
.6
.3
cai i
TOXS
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
TX
NT
JJMJ.TS:
GROW
13
11
11
11
75
11
12
ND
11
10
10
10
10
11
10
ND
10
10
11
10
10
11
10
ND
10
97
52
11
11
12
10
ND
11
12
87
10
10
ND
ND
ND
11
=ng/g
TOXG
NT
NT
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
NT
TX
NT
NT
ND
ND
ND
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1 TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
0.0 TX ND ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=408 CHEM=Fluorene TEST=HA14 SAMPTYP=bottom sediment - total
5 WH-l-RE
3 SR-1-10
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
3 SR-1-03
GL-NERM-50% NO EFFECT
2.0 5 WH-1-02
GL-TEL-SR (ERL*NERM)
9 TR-1-01
2.1 2 BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
2.9 2 BR-1-08
3.3 3 SR-1-06
9 TR-1-02
4 SR-3-08
4 SR-3-24
4 SR-3-16
8.2 2 BR-1-07
9 TR-1-03
9 TR-1-04
14.1 1 IH-1-04
0.7 4 SR-3-05
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
GL-ERM-50% EFFECT
ERM-50% EFFECT
GL-PEL-SR(ERM*NERH)
4 SR-3-02
GL-NERH-85% NO EFFECT
20.0 2 BR-1-03
20.2 2 BR-1-01
4 SR-3-01
27.6 1 IH-1-06
31.2 1 IH-1-03
58.9 5 WH-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
693.2 1 IH-1-07
JNUBUA
CONC I
558.8
700.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1266.7
1266.7
1543.9
1627.4
2000.0
2090.9
2090.9
2090.9
2361.3
2666.7
2941.2
3285.7
3333.3
6944.4
7250.0
7931.0
8235.3
9666.7
12750.0
14107.1
14285.7
16758.2
16905.3
17053.6
17053.6
18109.5
19230.8
19230.8
20000.0
20224.7
27000.0
27586.2
31168.8
45945.9
80000.0
80000.0
80000.0
693181.8
lUC.-1-.
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
*
*
NE
NE
NE
NE
**
NE
NE
* it
NC
NE
* *
* *
NE
**
**
**
NE
**
.eaimt
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
int: -
SUR
100.
101.
100.
100.
100.
100.
100.
100.
115.
40.
100.
83.
113.
12.
100.
110.
113.
111.
86.
87.
93.
0.
104.
to
V
0
6
0
0
0
0
0
0
6
0
0
4
7
5
0
4
3
8
4
5
4
0
5
tai i
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
JJMO.TS:
GROW
14
10
10
ND
10
10
10
10
95
11
ND
90
85
87
ND
10
10
10
85
ND
ND
ND
94
•ng/g
TOXG
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
TX
TX
NT
ND
NT
NT
NT
TX
ND
ND
ND
NT
MATURE
ND
33
ND
ND
10
10
10
10
23
ND
ND
0.
22
0.
ND
61
14
16
0.
ND
ND
ND
22
TOXM
ND
NT
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
TX
NT
ND
NT
NT
NT
TX
ND
ND
ND
TX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
105.9 NT 10
77.3
100.0
116.2
1.4
1.4
35.0
111.8
TX
NT
NT
TX
TX
TX
NT
85
85
10
68
96
13
94
NT
TX
TX
NT
NT
NT
NT
NT
0.0 TX ND ND
51
68
0.
12
0.
0.
ND
74
ND
NT
NT
TX
NT
NT
NT
ND
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
jMunut
CONC E
2.0
144.9
149.3
209.3
312.5
322.6
370.4
416.7
500.0
526.3
558.8
588.2
700.0
714.3
769.2
818.2
833.3
833.3
888.9
909.1
909.1
909.1
909.1
909.1
953.5
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1033.3
1250.0
1266.7
1543.9
1543.9
1625.0
1666.7
2000.0
2090.9
2130.9
2941.2
2941.2
3285.7
3285.7
3333.3
5000.0
5000.0
5635.8
6944.4
7250.0
7931.0
8235.3
9666.7
9666.7
12750.0
14107.1
14285.7
17053.6
18109.5
19230.8
19230.8
20000.0
20224.7
27000.0
27586.2
31168.8
33333.3
45945.9
80000.0
80000.0
80000.0
;UE=4
=408 CHEM=Fluorene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
0.3
0.6
0.7
0.9
0.7
1.3
1.3
2.0
2.0
1.6
2.0
1.3
2.0
1.1
3.3
11.0
4.2
14.1
10.1
10.3
27.6
31.2
58.9
11
6
11
11
11
7
5
6
9
4
3
7
1
2
10
7
3
5
10
10
9
2
9
11
10
4
4
4
2
9
9
1
4
2
2
4
1
1
10
5
4
TB-l-RE
CF-1-01
CF-1-06
UM-1-01
MR-1-25
CF-1-04
MR-1-11
MR-1-07
UM-l-RE
MR-1-17
WH-l-RE
CF-1-02
SR-1-10
CF-1-03
MR-1-19
UM-1-03
CF-l-CO
CF-1-05
UM-1-02
TB-1-04
TB-1-03
TB-1-02
MR-l-CO
ERL-15% EFFECT
TEL-SR(ERL*NERM)
WH-l-CO
UM-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
MR-1-01
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
MB-1-03
MR-1-02
SR-1-03
WH-1-02
GL-ERL-15% EFFECT
MB-l-RE
MB-1-02
TR-1-01
BR-1-09
GL-TEL-SR (ERL*NERM)
BR-1-08
GL-NERM-50% NO EFFECT
SR-1-06
ERM-50% EFFECT
TR-1-02
TB-1-01
MB-1-04
PEL-SR(ERM*NERH)
SR-3-08
SR-3-24
SR-3-16
BR-1-07
TR-1-03
NERH-85% NO EFFECT
TR-1-04
IH-1-04
SR-3-05
GL-ERM-50% EFFECT
GL-PEL-SR(ERM*NERH)
SR-3-02
GL-NERH-85% NO EFFECT
BR-1-03
BR-1-01
SR-3-01
IH-1-06
IH-1-03
MB-1-01
WH-1-01
SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
;eo.ime
'OXIC
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
snt. - ct
SURV
100.0
64.9
120.3
119.3
109.3
128.4
90.7
91.9
86.5
115.1
109.5
102.7
100.0
123.0
114.0
114.9
100.0
114.9
117.9
93.2
52.3
11.4
100.0
100.0
100.0
100.0
100.0
100.0
108.1
100.0
100.0
95.5
109.3
96.2
36.5
100.0
97.0
81.4
88.2
97.4
10.3
100.0
0.0
95.5
88.3
102.6
96.1
80.3
98.6
82.9
0.0
96.1
103.8
79.0
89.5
97.4
1.4
1.4
75.8
71.7
100.0
JCd-L I
TOXS
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
NT
TX
TX
NT
TX
NT
JIN A 1» =
GROW
10
73
10
ND
95
10
58
91
ND
92
11
94
97
82
89
ND
10
98
ND
10
97
72
10
10
ND
ND
10
10
79
10
10
ND
92
91
74
ND
ND
ND
92
10
60
ND
ND
ND
92
10
10
85
ND
ND
ND
94
10
85
96
94
68
96
ND
91
92
"9 '9
TOXG
NT
TX
NT
ND
NT
NT
TX
TX
ND
TX
NT
NT
TX
TX
TX
ND
NT
NT
ND
NT
NT
TX
NT
NT
ND
ND
NT
NT
TX
NT
NT
ND
TX
TX
TX
ND
ND
ND
NT
NT
TX
ND
ND
ND
NT
NT
NT
TX
ND
ND
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
NT
MATURE
ND
25
90
ND
12
80
24
31
ND
65
ND
48
10
93
63
ND
10
77
ND
ND
ND
ND
10
ND
ND
ND
10
10
68
10
10
ND
95
10
ND
ND
ND
ND
10
10
37
ND
ND
ND
95
10
95
10
ND
ND
ND
11
10
10
10
11
0.
0.
ND
ND
96
TOXM
ND
TX
NT
ND
NT
NT
TX
TX
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
ND
ND
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
ND
ND
ND
ND
NT
NT
TX
ND
ND
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
--- NUMCODE=408 CHEM=Fluorene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
693181.8 ** 693.2 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
10
NE no effect | NC<1 | NG=1 | SG 1-2
2-4
**>4
NUMCODE=409 CHEM=Phenanthrene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
7 MR-1-25
8 CF-1-04
8 CF-1-03
7 MR-1-07
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
7 MR-1-17
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
8 CF-1-02
NERM-50% NO EFFECT
8 CF-1-01
1.2 7 MR-1-11
TEL-SR(ERL*NERM)
3 SR-1-10
5 WH-l-RE
7 MR-1-02
7 MR-1-19
3.1 5 WH-1-02
ERL-15% EFFECT
3 SR-1-03
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
GL-TEL-SR(ERL*NERM)
3.7 3 SR-1-06
GL-ERL-15% EFFECT
2 BR-1-09
4 SR-3-24
4 SR-3-01
0.9 2 BR-1-08
NERH-85% NO EFFECT
15.1 5 WH-1-01
PEL-SR(ERM*NERH)
4 SR-3-02
1.3 2 BR-1-07
ERM-50% EFFECT
4 SR-3-05
GL-NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
60.7 1 IH-1-04
GL-ERM-50% EFFECT
2 BR-1-01
2.2 2 BR-1-03
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
85.3 1 IH-1-06
90.9 1 IH-1-03
375.0 1 IH-1-07
CONC !
149.3
500.0
516.1
714.3
791.7
833.3
833.3
909.1
947.4
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1058.8
1123.6
1188.4
2148.1
2626.7
2700.0
2941.2
3125.0
4846.2
6140.4
6140.4
11333.3
15862.1
15986.6
16111.1
17230.6
18571.4
18571.4
24545.5
25000.0
27000.0
27058.8
27058.8
29729.7
36913.5
39230.8
40000.0
50357.1
51428.6
51428.6
55878.9
60714.3
60714.3
68539.3
70000.0
80000.0
80000.0
80000.0
85344.8
90909.1
375000.0
i— *±v:
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
*
NE
NE
NE
*
NE
NE
NE
NC
* *
NE
SG
NE
**
NE
*
NE
**
* *
**
i seaimenc -
mic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
107
138
109
84
116
100
96
100
122
100
100
100
117
100
100
79
95
70
90
85
113
111
51
104
102
95
18
105
102
96
38
8
100
47
.4
.8
.9
.0
.4
.0
.3
.0
.4
.0
.0
.0
.9
.0
.0
.0
.1
.2
.3
.7
.4
.9
.4
.5
.7
.1
.7
.0
.2
.7
.0
.6
.6
.9
cotaj
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
I UIMXJ
GROW
11
11
11
10
11
10
11
10
12
ND
10
10
11
10
10
11
13
75
10
ND
11
10
ND
10
12
11
52
10
11
10
97
ND
12
10
is-ng/
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
ND
NT
NT
g
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
104.9 NT 11
NT
2.0 TX
ND ND
67.8
62.8
103.3
NT
NT
NT
0.0 TX
2.7 TX
0.0 TX
10
87
11
ND
ND
ND
NT
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX -,j: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC C&RBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
11
NUKKJUUJ
CONC I
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
2000.0
2700.0
2941.2
3333.3
3333.3
6140.4
7137.3
7868.0
11333.3
11513.0
15862.1
16111.1
18571.4
18571.4
18571.4
24545.5
25000.0
27000.0
27000.0
27058.8
29729.7
37263.5
39230.8
40000.0
51428.6
51428.6
51428.6
60714.3
61412.0
68539.3
70000.0
73333.3
73333.3
80000.0
80000.0
85344.8
90909.1
137500.0
137500.0
375000.0
£=«U» 1
3FFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NE
*
**
NE
NE
* *
**
NE
**
SG
**
**
**
NE
NE
**
**
NE
**
LiiEM- rnenam
RATIO SITJ
5
9
4
3
1
2
9
3
5
9
3.1 5
,
3
.
4
4
3.7 3
.
24.5 2
4
4
,
27.1 2
15.1 5
4
40.0 2
1.8 4
60.7 1
68.5 2
70.0 2
9
4
,
85.3 1
90.9 1
9
.
375.0 1
WH-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
IH-l-CO
BR-l-CO
TR-1-01
SR-1-10
WH-l-RE
TR-1-02
NERM-50% NO EFFECT
WH-1-02
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
SR-1-03
GL-TEL-SR (ERL*NERM)
SR-3-16
SR-3-08
SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-09
SR-3-24
SR-3-01
GL-NERH-85% NO EFFECT
BR-1-08
WH-1-01
GL-PEL-SR (ERM*NERH)
SR-3-02
BR-1-07
SR-3-05
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-04
PEL-SR(ERM*NERH)
BR-1-01
BR-1-03
TR-1-03
NERH-85% NO EFFECT
SR-3-06
GL-NEC-MAX NO EFFECT
IH-1-06
IH-1-03
TR-1-04
NEC-MAX NO EFFECT
IH-1-07
L ^euj
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
LiueiiL. -
SURV
100.0
100.0
100.0
100.0
100.0
100.0
100.0
101.6
100.0
100.0
uui~a.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
L UL1XJ
GROW
10
ND
10
10
10
10
ND
10
14
ND
: a=ng /
TOXG
NT
ND
NT
NT
NT
NT
ND
NT
NT
ND
,g
MATURE
ND
ND
10
10
10
10
ND
33
ND
ND
TOXM
ND
ND
NT
NT
NT
NT
ND
NT
ND
ND
TOX 40.0 TX 11 NT ND ND
NOT 115.6 NT 95 NT 23 NT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
111
110
12
83
113
116
113
35
105
86
104
0
100
77
87
111
1
1
93
.8
.4
.5
.4
.3
.2
.7
.0
.9
.4
.5
.0
.0
.3
.5
.8
.4
.4
.4
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
10
10
87
90
10
10
85
13
10
85
94
ND
85
85
ND
94
68
96
ND
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
ND
TX
rx
MD
NJT
.*JT
TO
:ID
16
61
0.
0.
14
12
22
ND
51
0.
22
ND
0.
68
ND
74
0.
0.
ND
NT
NT
NT
TX
NT
NT
TX
ND
NT
TX
TX
ND
TX
NT
ND
NT
NT
NT
ND
TOX
0.0 TX
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=409 CHEM=Phenanthrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
11 TB-l-RE
6 UM-1-01
8 CF-1-06
6 UM-1-02
10 MB-1-03
10 MB-l-RE
6 UM-l-RE
7 MR-1-25
8 CF-1-04
1.1 8 CF-1-03
1.1 7 MR-1-07
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
1.3 7 MR-1-17
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.4 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
ERL-15% EFFECT
TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
8 CF-1-02
1.8 8 CF-1-01
10 MB-1-02
9 TR-1-01
3.0 7 MR-1-11
6 UM-1-03
2.7 3 SR-1-10
1.5 11 TB-1-03
5 WH-l-RE
4.4 7 MR-1-02
9 TR-1-02
11 TB-1-04
6.9 7 MR-1-19
3.1 5 WH-1-02
GL-ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
11.3 3 SR-1-03
ERM-50% EFFECT
10 MB-1-04
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
9.0 11 TB-1-02
18.6 3 SR-1-06
PEL-SR(ERM*NERH)
1.7 2 BR-1-09
4 SR-3-24
4 SR-3-01
2 BR-1-08
15.1 5 WH-1-01
4 SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
2.9 2 BR-1-07
GL-ERM-50% EFFECT
4 SR-3-05
60.7 1 IH-1-04
4.9 2 BR-1-01
5.0 2 BR-1-03
9 TR-1-03
4 SR-3-06
GL-NEC-MAX NO EFFECT
85.3 1 IH-1-06
90.9 1 IH-1-03
55.0 11 TB-1-01
9 TR-1-04
10 MB-1-01
NEC-MAX NO EFFECT
12
CONC 1
2.0
46.5
149.3
333.3
333.3
375.0
500.0
500.0
516.1
714.3
791.7
833.3
833.3
909.1
947.4
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1014.6
1029.4
1058.8
1188.4
1666.7
2000.0
2148.1
2681.8
2700.0
2727.3
2941.2
3125.0
3333.3
3636.4
4846.2
6140.4
6140.4
9907.7
11333.3
13848.5
15000.0
15862.1
15986.6
16111.1
16363.6
18571.4
23308.5
24545.5
25000.0
27000.0
27058.8
29729.7
39230.8
39230.8
39230.8
39613.5
40000.0
40000.0
51428.6
60714.3
68539.3
70000.0
73333.3
80000.0
80000.0
85344.8
90909.1
100000.0
137500.0
222222.2
222222.2
SFFEl
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
*
NE
*
SG
NE
**
NE
NE
**
*
* *
NE
NE
NE
**
* *
SG
NE
NE
NE
**
NE
*
NE
**
**
**
NE
NE
**
* *
**
NE
NE
LI O tSU.-LUltni U
roxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
100
119
120
117
95
100
86
109
128
123
91
100
114
100
115
100
100
100
100
100
108
100
100
102
64
97
81
90
114
100
52
109
109
100
93
114
36
96
95
96
88
11
10
88
102
97
97
71
103
80
96
0
89
79
98
100
1
1
0
82
75
.0
.3
.3
.9
.5
.0
.5
.3
.4
.0
.9
.0
.9
.0
.1
.0
.0
.0
.0
.0
.1
.0
.0
.7
.9
.0
.4
.7
.9
.0
.3
.5
.3
.0
.2
.0
.5
.2
.5
.1
.3
.4
.3
.2
.6
.4
.4
.7
.8
.3
.1
.0
.5
.0
.6
.0
.4
.4
.0
.9
.8
Ul^t-Ct,
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
TX
NT
TX
NT
TX
TX
TX
NT
NT
TX
TX
TX
NT
NT
1. UJU.L.
GROW
10
ND
10
ND
ND
ND
ND
95
10
82
91
10
98
10
92
10
ND
ND
10
10
79
10
10
94
73
ND
ND
58
ND
97
97
11
92
ND
10
89
74
91
ND
10
92
72
60
92
10
94
10
91
10
85
94
ND
96
85
ND
92
68
96
ND
ND
ND
10— Jjy /
TOXG
NT
ND
NT
ND
ND
ND
ND
NT
NT
TX
TX
NT
NT
NT
TX
NT
ND
ND
NT
NT
TX
NT
NT
NT
TX
ND
ND
TX
ND
TX
NT
NT
TX
ND
NT
TX
TX
TX
ND
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
TX
ND
NT
NT
NT
ND
ND
ND
u
MATURE TOXM
ND
ND
90
ND
ND
ND
ND
12
80
93
31
10
77
10
65
ND
ND
ND
10
10
68
10
10
48
25
ND
ND
24
ND
10
ND
ND
95
ND
ND
63
ND
10
ND
95
95
ND
37
10
10
11
10
ND
10
10
11
ND
10
10
ND
96
0.
0.
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
NT
NT
NT
TX
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
TX
ND
ND
TX
ND
NT
ND
ND
NT
ND
ND
NT
ND
NT
ND
NT
NT
ND
TX
NT
NT
NT
NT
ND
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 13
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
- NUMCODE=409 CHEM=Phenanthrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
375000.0 ** 375.0 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
CONC I
149.3
231.9
312.5
322.6
370.4
416.7
526.3
529.4
588.2
714.3
800.0
833.3
833.3
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1250.0
1567.2
1809.5
2200.0
2456.1
2456.1
2456.1
3756.4
4545.5
5744.9
5945.9
6944.4
7058.8
7250.0
7931.0
14117.6
14285.7
14285.7
18898.2
19101.1
19230.8
19230.8
21926.5
25000.0
25000.0
25000.0
27000.0
29310.3
31168.8
55000.0
80000.0
80000.0
80000.0
1477272.7
JKt — •*.
SFFEI
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
NE
**
NE
NC
NE
NE
SG
NE
NE
NE
**
NE
* *
**
**
NE
**
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=410 CHEM=Anthracene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=
8 CF-1-06
8 CF-1-01
7 MR-1-25
8 CF-1-04
0.5 7 MR-1-11
7 MR-1-07
7 MR-1-17
5 WH-l-RE
8 CF-1-02
8 CF-1-03
3 SR-1-10
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-19
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
7 MR-1-02
TEL-SR (ERL*NERM)
1.4 3 SR-1-06
3 SR-1-03
3.2 5 WH-1-02
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
2 BR-1-09
GL-NERM-50% NO EFFECT
7.8 5 WH-1-01
4 SR-3-08
0.9 2 BR-1-08
4 SR-3-24
4 SR-3-16
1.7 2 BR-1-07
4 SR-3-05
NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
2 BR-1-01
4 SR-3-02
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
25.0 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
4 SR-3-01
29.3 1 IH-1-06
31.2 1 IH-1-03
6.7 2 BR-1-03
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
1477.3 1 IH-1-07
14
seair
'OXIC
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
nent - \
SURV
107.4
95.1
138.8
109.9
70.2
116.4
122.4
85.7
79.0
84.0
90.3
100.0
96.3
100.0
100.0
100.0
100.0
111.9
117.9
100.0
100.0
113.4
18.7
104.5
51.4
105.0
8.6
95.1
38.0
102.2
102.7
47.9
104.9
67.8
100.6
2.0
96.7
0.0
2.7
62.8
103.3
;ocaj.
TOXS
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
UW-LTi
GROW
11
13
11
11
75
11
12
ND
11
10
10
10
11
10
ND
10
10
10
11
10
10
11
52
10
ND
10
ND
11
97
11
12
10
11
10
12
ND
10
ND
ND
87
11
>-ng/c
TOXG
NT
NT
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
ND
TX
NT
j
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
0.0 TX ND ND
ND
ND
-------
seuiiueiiL - t
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
100
101
100
100
100
100
100
100
12
100
115
.0
.6
.0
.0
.0
.0
.0
.0
.5
.0
.6
otai
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
UMJ.T:
GROW
14
10
10
ND
10
10
10
10
87
ND
95
3-ng/g
TOXG
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
NT
MATURE TOXM
ND
33
ND
ND
10
10
10
10
0.
ND
23
ND
NT
ND
ND
NT
NT
NT
NT
NT
ND
NT
TOX
40.0 TX
11
NT
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTA. JRGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=410 CHEM=Anthracene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
5 WH-l-RE
3 SR-1-10
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
1.4 3 SR-1-06
9 TR-1-01
3 SR-1-03
GL-NERM-50% NO EFFECT
GL-TEL-SR(ERL*NERM)
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
3.2 5 WH-1-02
GL-ERL-15% EFFECT
ERL-15% EFFECT
9 TR-1-04
9 TR-1-03
9 TR-1-02
4.5 2 BR-1-09
7.8 5 WH-1-01
4 SR-3-08
7.1 2 BR-1-08
4 SR-3-24
4 SR-3-16
14.1 2 BR-1-07
0.7 4 SR-3-05
GL-ERM-50% EFFECT
ERM-50% EFFECT
PEL-SR(ERM*NERH)
NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
19.1 2 BR-1-01
4 SR-3-02
GL-NERH-85% NO EFFECT
25.0 1 IH-1-04
4 SR-3-01
29.3 1 IH-1-06
31.2 1 IH-1-03
55.0 2 BR-1-03
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
1477.3 1 IH-1-07
15
1NUJXH-UJ
CONC 1
529.4
800.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1809.5
2000.0
2200.0
2200.0
2324.5
2350.0
2402.5
2456.1
2456.1
2456.1
2500.0
3333.3
3333.3
4545.5
5945.9
6944.4
7058.8
7250.0
7931.0
14117.6
14285.7
16609.4
16609.4
16683.6
16758.2
17872.1
19101.1
19230.8
19230.8
25000.0
27000.0
29310.3
31168.8
55000.0
80000.0
80000.0
80000.0
1477272.7
JCi=l±.
SFFEl
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
*
NE
NE
NE
**
* *
NE
* *
NE
NE
* *
NC
**
NE
* *
NE
**
* *
**
NE
* *
ND
ND
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
93
87
100
83
35
110
113
113
111
86
104
100
105
0
116
1
1
77
111
.4
.5
.0
.4
.0
.4
.7
.3
.8
.4
.5
.0
.9
.0
.2
.4
.4
.3
.8
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
ND
ND
ND
90
13
10
85
10
10
85
94
85
10
ND
10
68
96
85
94
ND
ND
ND
TX
NT
NT
TX
NT
NT
TX
NT
TX
NT
ND
NT
NT
NT
TX
NT
ND
ND
ND
0.
ND
61
22
14
16
0.
22
0.
51
ND
12
0.
0.
68
74
ND
ND
ND
TX
ND
NT
TX
NT
NT
TX
TX
TX
NT
ND
NT
NT
NT
NT
NT
TOX
0.0 TX ND ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=410 CHEM=Anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE C
11 TB-l-RE
6 UM-1-01
8 CF-1-06
0.4 8 CF-1-01
7 MR-1-25
8 CF-1-04
6 UM-1-02
10 MB-1-03
0.6 7 MR-1-11
10 MB-l-RE
6 UM-1-03
0.7 7 MR-1-07
6 UM-l-RE
0.9 7 MR-1-17
5 WH-l-RE
8 CF-1-02
1.3 8 CF-1-03
0.8 3 SR-1-10
10 MB-1-02
8 CF-l-CO
8 CF-1-05
11 TB-1-04
2.0 11 TB-1-03
2.0 11 TB-1-02
7 MR-l-CO
TEL-SR (ERL*NERM)
NERM-50% NO EFFECT
ERL-15% EFFECT
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-19
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
2.0 7 MR-1-02
1.8 3 SR-1-06
9 TR-1-01
2.2 3 SR-1-03
GL-ERL-15% EFFECT
3.2 5 WH-1-02
9 TR-1-04
9 TR-1-03
9 TR-1-02
GL-TEL-SR (ERL*NERM)
1.1 2 BR-1-09
ERM-50% EFFECT
11.0 11 TB-1-01
PEL-SR{ERM*NERH)
7.8 5 WH-1-01
4 SR-3-08
GL-NERM-50% NO EFFECT
10 MB-1-04
2 BR-1-08
4 SR-3-24
NERH-85% NO EFFECT
4 SR-3-16
3.5 2 BR-1-07
4 SR-3-05
GL-ERM-50% EFFECT
GL-PEL-SR (ERM*NERH)
4.7 2 BR-1-01
4 SR-3-02
GL-NERH-85% NO EFFECT
10 MB-1-01
25.0 1 IH-1-04
4 SR-3-01
29.3 1 IH-1-06
31.2 1 IH-1-03
13.6 2 BR-1-03
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
16
jMurauui
CONC 1
2.0
46.5
149.3
231.9
312.5
322.6
333.3
333.3
370.4
375.0
409.1
416.7
500.0
526.3
529.4
588.2
714.3
800.0
833.3
833.3
833.3
909.1
909.1
909.1
909.1
909.1
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1250.0
1809.5
2000.0
2200.0
2200.0
2456.1
2500.0
3333.3
3333.3
3908.7
4545.5
4545.5
5000.0
5740.6
5945.9
6944.4
6944.4
7000.0
7058.8
7250.0
7250.0
7931.0
14117.6
14285.7
16609.4
17872.1
19101.1
19230.8
19230.8
22222.2
25000.0
27000.0
29310.3
31168.8
55000.0
80000.0
80000.0
80000.0
JC-4J
SFFEC
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
NC
NE
NC
NE
NE
SG
NC
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
*
SG
NE
*
*
NE
NE
NE
SG
* *
* *
NE
NE
NE
NE
NE
*
NE
* *
NE
NE
* *
NE
* *
* *
* *
NE
St£U.LlUeiJL. - U
'OXIC SURV
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
100
119
120
64
109
128
117
95
90
100
114
91
86
115
109
102
123
100
97
100
114
93
52
11
100
100
100
100
100
100
114
108
100
100
109
10
81
96
36
82
98
100
88
0
71
88
95
97
102
96
80
96
89
103
75
0
97
1
1
79
100
.0
.3
.3
.9
.3
.4
.9
.5
.7
.0
.9
.9
.5
.1
.5
.7
.0
.0
.0
.0
.9
.2
.3
.4
.0
.0
.0
.0
.0
.0
.0
.1
.0
.0
.3
.3
.4
.2
.5
.9
.6
.0
.2
.0
.7
.3
.5
.4
.6
.1
.3
.1
.5
.8
.8
.0
.4
.4
.4
.0
.0
(JL.CLJL
TOXS
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
TX
TX
TX
NT
UlXJ.lh
GROW
10
ND
10
73
95
10
ND
ND
58
ND
ND
91
ND
92
11
94
82
97
ND
10
98
10
97
72
10
10
ND
ND
10
10
89
79
10
10
92
60
ND
91
74
ND
ND
ND
92
ND
91
92
ND
10
10
10
85
94
96
10
ND
ND
94
68
96
85
92
3=uy / y
TOXG
NT
ND
NT
TX
NT
NT
ND
ND
TX
ND
ND
TX
ND
TX
NT
NT
TX
TX
ND
NT
NT
NT
NT
TX
NT
NT
ND
ND
NT
NT
TX
TX
NT
NT
TX
TX
ND
TX
TX
ND
ND
ND
NT
ND
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
ND
ND
NT
NT
NT
TX
NT
MATURE
ND
ND
90
25
12
80
ND
ND
24
ND
ND
31
ND
65
ND
48
93
10
ND
10
77
ND
ND
ND
10
ND
ND
ND
10
10
63
68
10
10
95
37
ND
10
ND
ND
ND
ND
10
ND
ND
95
ND
10
10
95
10
11
10
10
ND
ND
11
0.
0.
10
96
TOXM
ND
ND
NT
TX
NT
NT
ND
ND
TX
ND
ND
TX
ND
NT
ND
NT
NT
NT
ND
NT
NT
ND
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
ND
ND
ND
ND
NT
ND
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 17
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=410 CHEM=Anthracene TEST=HA28 SAMPTYP=bottom sediment - total ONITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
1477272.7 ** 1477.3 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
18
NE no effect I NC<1 | NG=1 | SG 1-2 | * 2-4
*>4
NUMCODE=411 CHEM=Fluoranthene TEST=CR14 SAMPTYP=bottom sediment -
8 CF-1-06
7 MR-1-25
8 CF-1-03
8 CF-l-CO
8 CF-1-05
8 CF-1-04
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-07
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
7 MR-1-17
8 CF-1-02
0.8 5 WH-1-02
NERM-50% NO EFFECT
8 CF-1-01
0.9 7 MR-1-11
3 SR-1-10
5 WH-l-RE
7 MR-1-02
3 SR-1-03
TEL-SR(ERL*NERM)
2.1 3 SR-1-06
7 MR-1-19
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
GL-TEL-SR (ERL*NERM)
4 SR-3-01
11.2 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-24
4 SR-3-02
NERH-85% NO EFFECT
1.0 2 BR-1-08
4 SR-3-05
2 BR-1-09
GL-NERH-85% NO EFFECT
1.2 2 BR-1-07
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
4 SR-3-06
2 BR-1-01
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
85.7 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
2.0 2 BR-1-03
111.7 1 IH-1-03
120.7 1 IH-1-06
454.5 1 IH-1-07
iMuriuwuj:
CONC I
194.0
375.0
714.3
833.3
833.3
838.7
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1105.3
1294.1
1929.8
2008.4
2087.0
2518.5
3600.0
3823.5
4875.0
6333.3
7367.6
7619.0
10230.8
14482.8
14482.8
16111.1
19784.5
27000.0
27027.0
27027.0
27027.0
30000.0
38461.5
38461.5
44705.9
45000.0
54545.5
54545.5
58235.3
58951.5
70203.8
80000.0
84269.7
84269.7
84269.7
85714.3
90357.1
90357.1
95000.0
111688.3
120689.7
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
*
NE
NE
NE
NE
* *
NE
NE
NC
NE
NE
SG
NE
NE
* *
*
* *
* *
454545.5
i seaiment - cocaj
'OXIC SURV TOXS
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
107
138
84
100
96
109
100
100
100
100
116
117
100
100
122
79
51
95
70
90
85
113
104
18
111
102
95
96
8
102
100
38
104
105
47
103
67
2
62
2
0
0
.4
.8
.0
.0
.3
.9
.0
.0
.0
.0
.4
.9
.0
.0
.4
.0
.4
.1
.2
.3
.7
.4
.5
.7
.9
.7
.1
.7
.6
.2
.6
.0
.9
.0
.9
.3
.8
.0
.8
.7
.0
.0
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
TX
TX
TX
. UJNJ.J
GROW
11
11
10
10
11
11
10
ND
10
10
11
11
10
10
12
11
ND
13
75
10
ND
11
10
52
10
12
11
10
ND
11
12
97
11
10
10
11
10
ND
87
ND
ND
ND
.&=ng/g
TOXG MATURE
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=411 CHEM=Fluoranthene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
0.8 5 WH-1-02
3 SR-1-10
5 WH-l-RE
GL-NERM-50% NO EFFECT
9 TR-1-01
NERM-50% NO EFFECT
3 SR-1-03
2.1 3 SR-1-06
9 TR-1-02
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
4 SR-3-16
4 SR-3-08
4 SR-3-01
11.2 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-24
GL-NERH-85% NO EFFECT
4 SR-3-02
44.7 2 BR-1-08
1.5 4 SR-3-05
GL-PEL-SR(ERM*NERH)
54 5 2 BR-1-09
58.2 2 BR-1-07
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
GL-ERM-50% EFFECT
ERM-50% EFFECT
4 SR-3-06
GL-NEC-MAX NO EFFECT
84.3 2 BR-1-01
85.7 1 IH-1-04
95.0 2 BR-1-03
111.7 1 IH-1-03
120.7 1 IH-1-06
9 TR-1-03
9 TR-1-04
NEC-MAX NO EFFECT
454.5 1 IH-1-07
19
CONC I
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1929.8
3600.0
3823.5
3823.5
6200.0
6266.7
6333.3
7619.0
9666.7
10165.6
13014.2
14482.8
16111.1
27000.0
27027.0
27027.0
27027.0
30000.0
30000.0
38461.5
44705.9
45000.0
46233.9
54545.5
58235.3
59230.8
64964.1
71252.5
71252.5
80000.0
80000.0
84269.7
85714.3
95000.0
111688.3
120689.7
130000.0
177500.0
177500.0
454545.5
i — *± A.
3FFEI
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
*
NE
NE
NE
NE
* *
NE
NE
**
SG
**
**
NE
* *
* *
* *
**
**
NE
NE
* *
.1 seuj
?OXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
Lineii u
SU
100
100
100
100
100
100
40
101
100
100
115
12
100
111
110
116
35
113
105
113
104
83
86
RV
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.6
.5
.0
.8
.4
.2
.0
.3
.9
.7
.5
.4
.4
UUL<3.
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
L UNX.
GROW
10
ND
10
10
10
10
11
10
14
ND
95
87
ND
10
10
10
13
10
10
85
94
90
85
L-a-ng/
TOXG
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
g
MATURE
ND
ND
10
10
10
10
ND
33
ND
ND
23
0.
ND
16
61
12
ND
14
51
22
22
0.
0.
TOXM
ND
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
NT
ND
NT
NT
NT
ND
NT
NT
TX
TX
TX
TX
NOT
111.8 NT 94
NT
74
NT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
100.0
0.0
77.3
1.4
1.4
87.5
93.4
NT
TX
TX
TX
TX
NT
NT
85
ND
85
96
68
ND
ND
TX
ND
TX
NT
NT
ND
ND
0.
ND
68
0.
0.
ND
ND
TX
ND
NT
NT
NT
ND
ND
TOX
0.0 TX
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=411 CHEM=Fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE C
20
iNurauuur
CONC I
2.0
194.0
375.0
714.3
833.3
833.3
838.7
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1105.3
1186.0
1294.1
1818.2
1928.6
1929.8
2087.0
2087.0
2518.5
2727.3
2824.8
3600.0
3823.5
3823.5
4545.5
4875.0
4944.4
5000.0
5000.0
6000.0
6200.0
6333.3
6333.3
7000.0
7619.0
7619.0
8333.3
9577.3
9666.7
10230.8
14482.8
14482.8
16111.1
17118.4
27000.0
27027.0
30000.0
36000.0
38461.5
38461.5
44705.9
44705.9
45000.0
54545.5
56439.4
58235.3
71252.5
80000.0
80000.0
84269.7
85714.3
95000.0
111111.1
111688.3
120689.7
130000.0
177500.0
177500.0
SFFEC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
SG
NE
NE
NC
NE
NC
*
*
SG
*
NE
NE
* *
NE
*
NE
NE
NE
it *
NE
it *
NE
NE
* *
NE
NE
NE
* *
NE
NE
NE
NE
NE
*
*
NE
*
**
*• *
NE
* it
* *
NE
NE
0.9
1.6
1.6
1.7
0.8
0.8
2.6
3.9
1.2
3.6
7.6
2.2
6.3
7.6
15.9
11.2
2.4
2.5
3.7
85.7
4.2
111.7
120.7
11
8
7
7
5
6
9
4
3
7
7
1
2
7
6
8
11
6
5
8
7
11
3
5
11
7
6
11
10
6
9
3
10
3
10
9
7
4
4
5
4
10
4
2
1
2
10
1
1
9
9
TB-l-RE
CF-1-06
MR-1-25
CF-1-03
CF-l-CO
CF-1-05
CF-1-04
MR-l-CO
WH-l-CO
UM-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
MR-1-07
MR-1-01
IH-l-CO
BR-l-CO
MR-1-17
UM-1-01
CF-1-02
TB-1-03
UM-l-RE
WH-1-02
CF-1-01
ERL-15% EFFECT
MR-1-11
TB-1-02
TEL-SR(ERL*NERM)
SR-1-10
WH-l-RE
NERM-50% NO EFFECT
TB-1-04
MR-1-02
UM-1-02
TB-1-01
MB-l-RE
UM-1-03
TR-1-01
SR-1-03
GL-ERL-15% EFFECT
MB-1-03
SR-1-06
ERM-50% EFFECT
MB-1-02
GL-TEL-SR(ERL*NERM)
TR-1-02
MR-1-19
SR-3-16
GL-NERM-50% NO EFFECT
SR-3-08
PEL-SR(ERM*NERH)
SR-3-01
WH-1-01
SR-3-24
MB-1-04
SR-3-02
NERH-85% NO EFFECT
BR-1-08
GL-NERH-85% NO EFFECT
SR-3-05
BR-1-09
GL-PEL-SR (ERM*NERH)
BR-1-07
GL-ERM-50% EFFECT
SR-3-06
GL-NEC-MAX NO EFFECT
BR-1-01
IH-1-04
BR-1-03
MB-1-01
IH-1-03
IH-1-06
TR-1-03
TR-1-04
NEC-MAX NO EFFECT
i seaiment. - uuuetj
'OXIC SURV TOXS
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
100.
120.
109.
123.
100.
114.
128.
100.
100.
100.
100.
100.
100.
91.
108.
100.
100.
115.
119.
102.
52.
86.
36.
64.
90.
11.
100.
109.
93.
109.
117.
0.
100.
114.
81.
96.
95.
10.
97.
100.
114.
96.
88.
97.
71.
102.
95.
103.
97.
96!
88.
80.
100.
89.
0.
79.
75.
1.
1.
98.
82.
0
3
3
0
0
9
4
0
0
0
0
0
0
9
1
0
0
1
3
7
3
5
5
9
7
4
0
5
2
3
9
0
0
9
4
2
5
3
0
0
0
1
3
4
7
6
5
8
4
1
2
3
0
5
0
0
8
4
4
6
9
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
NT
TX
TX
NT
NT
. UiM-i. J
GROW
10
10
95
82
10
98
10
10
10
ND
ND
10
10
91
79
10
10
92
ND
94
37
ND
74
73
58
72
97
11
10
92
ND
ND
ND
ND
ND
91
ND
60
ND
ND
89
10
92
94
91
10
ND
10
10
94
92
85
92
96
ND
85
ND
96
68
ND
ND
.o=lig/ y
TOXG MATURE
NT
NT
NT
TX
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
TX
NT
NT
TX
ND
NT
NT
ND
TX
TX
TX
TX
TX
NT
NT
TX
ND
ND
ND
ND
ND
TX
ND
TX
ND
ND
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
TX
NT
NT
ND
TX
ND
NT
NT
ND
ND
ND
90
12
93
10
77
80
10
ND
ND
ND
10
10
31
68
10
10
65
ND
48
ND
ND
ND
25
24
ND
10
ND
ND
95
ND
ND
ND
ND
ND
10
ND
37
ND
ND
63
95
95
11
ND
10
ND
10
10
11
10
10
96
10
ND
10
ND
0.
0.
ND
ND
TOXM
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
ND
ND
ND
TX
TX
ND
NT
ND
ND
NT
ND
ND
ND
ND
ND
NT
ND
TX
ND
ND
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 21
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
- NUMCODE=411 CHEM=Fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
454545.5 ** 454.5 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
22
i>< UJ«H.
CONC I
149.3
437.5
580.6
714.3
833.3
833.3
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1083.3
1235.3
1684.2
1892.8
2101.4
2105.3
2259.3
2764.7
3625.0
4400.0
6971.3
11076.9
18333.3
25675.7
25675.7
25675.7
25768.7
25862.1
25862.1
27000.0
27142.9
27777.8
34090.9
40588.2
45000.0
45000.0
54615.4
60545.1
62857.1
62857.1
64705.9
68539.3
71556.6
80000.0
80000.0
80000.0
81460.1
81460.1
98214.3
105000.0
207792.2
344827.6
625000.0
.\JLId-
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NC
NE
NE
NE
NE
NE
**
NE
NE
*
NE
NE
SG
NE
NE
NE
SG
NE
NE
* *
*
* *
* *
**
NE no effect | NC<1 | NG=1 | SG 1-2 * 2-4 | **>4
NUMCODE=412 CHEM=Pyrene TEST=CR14 SAMPTYP=bottom sediment - total
8 CF-1-06
7 MR-1-25
8 CF-1-04
8 CF-1-03
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
7 MR-1-07
8 CF-1-02
7 MR-1-17
NERM-50% NO EFFECT
8 CF-1-01
1.1 5 WH-1-02
0.8 7 MR-1-11
5 WH-l-RE
7 MR-1-02
3 SR-1-10
TEL-SR (ERL*NERM)
7 MR-1-19
3 SR-1-03
13.6 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR (ERL*NERM)
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-01
3.4 3 SR-1-06
4 SR-3-08
2 BR-1-09
1.2 2 BR-1-08
4 SR-3-24
NERH-85% NO EFFECT
4 SR-3-02
PEL-SR (ERM*NERH)
4 SR-3-05
GL-NERH-85% NO EFFECT
1.9 2 BR-1-07
2 BR-1-01
GL-PEL-SR (ERM*NERH)
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
GL-ERM-50% EFFECT
ERM-50% EFFECT
98.2 1 IH-1-04
3.0 2 BR-1-03
207.8 1 IH-1-03
344.8 1 IH-1-06
625.0 1 IH-1-07
iaiment - cot
X3XIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
107
138
109
84
100
96
100
100
100
100
117
100
100
116
79
122
95
51
70
85
113
90
111
104
8
102
96
18
95
105
38
102
100
104
47
67
.4
.8
.9
.0
.0
.3
.0
.0
.0
.0
.9
.0
.0
.4
.0
.4
.1
.4
.2
.7
.4
.3
.9
.5
.6
.7
.7
.7
.1
.0
.0
.2
.6
.9
.9
.8
di± Ul'
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
^xrs=i
GROW
11
11
11
10
10
11
10
ND
10
10
11
10
10
11
11
12
13
ND
75
ND
11
10
10
10
ND
12
10
52
11
10
97
11
12
11
10
10
ig/g
TOXG MATURE
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
TX
ND
NT
NT
NT
NT
ND
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
TOX
TOX
TOX
TOX
TOX
103.3 NT 11
2.0 TX
62.8 NT
2.7 TX
0.0 TX
0.0 TX
ND
87
ND
ND
ND
NT
ND
TX
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=412 CHEM=Pyrene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
23
CONC :
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
2105.3
2764.7
3333.3
4400.0
5600.0
5600.0
11366.7
11991.0
17083.5
18333.3
25675.7
25675.7
25675.7
25862.1
27000.0
27142.9
27777 .8
34090.9
40588.2
45000.0
45000.0
53960.8
54615.4
62857.1
64705.9
64705.9
64705.9
68539.3
71947.7
80000.0
80000.0
80000.0
90000.0
98214.3
105000.0
147500.0
147500.0
207792.2
344827.6
625000.0
^-WUr/
EFFEi
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
* *
NE
NE
*
NE
* *
**
NE
NE
SG
* *
**
NE
NE
**
* *
NE
**
* *
* *
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
1.1 5 WH-1-02
5 WH-l-RE
9 TR-1-02
3 SR-1-10
9 TR-1-01
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL*NERM)
3 SR-1-03
13.6 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-16
4 SR-3-01
3.4 3 SR-1-06
4 SR-3-08
34.1 2 BR-1-09
40.6 2 BR-1-08
4 SR-3-24
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM'NERH)
4 SR-3-02
1.7 4 SR-3-05
64.7 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
68.5 2 BR-1-01
PEL-SR(ERM*NERH)
4 SR-3-06
NERH-85% NO EFFECT
GL-NEC-MAX NO EFFECT
9 TR-1-03
98.2 1 IH-1-04
105.0 2 BR-1-03
9 TR-1-04
NEC-MAX NO EFFECT
207.8 1 IH-1-03
344.8 1 IH-1-06
625.0 1 IH-1-07
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
.1 <« I.
SUI
100.
100.
100.
100.
100.
100.
40.
100.
100.
101.
100.
115.
35.
111.
116.
12.
110.
83.
113.
113.
105.
104.
86.
100.
111.
87.
0.
77.
93.
1.
1.
0.
~\J\.
IV
.0
0
0
0
0
0
0
0
0
6
0
6
0
8
2
5
4
4
7
3
9
5
4
0
8
5
0
3
4
4
4
0
.O.J. LJ
TOX£
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
! GROW
10
ND
10
10
10
10
11
14
ND
10
ND
95
13
10
10
87
10
90
85
10
10
94
85
85
94
ND
ND
85
ND
96
68
ND
uy/g -
TOXG
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
NT
ND
ND
TX
ND
NT
NT
ND
MATURE
ND
ND
10
10
10
10
ND
ND
ND
33
ND
23
ND
16
12
0.
61
0.
22
14
51
22
0.
0.
74
ND
ND
68
ND
0.
0.
ND
; TOXM
ND
ND
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
ND
NT
NT
NT
NT
TX
TX
NT
NT
TX
TX
TX
NT
ND
ND
NT
ND
NT
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
24
WUjatUlJE=S
CONC EFFECT
2.
149.
437.
580.
714.
833.
833.
909.
1000.
1000.
1000.
1000.
1000.
1000.
1000.
1000.
1083.
1235.
1684.
1767.
1857.
2101.
2101.
2105.
2259.
2646.
2764.
3333.
3333.
3625.
3636.
3636.
4400.
4400.
5222.
5600.
6181.
6363.
7000.
7500.
10000.
10784.
11076.
18333.
18333.
22000.
25000.
25675.
25862.
26431.
27000.
27142.
27777.
31643.
34090.
40588.
45000.
54615.
54615.
54615.
59446.
62857.
64705.
64705.
68539.
80000.
80000.
90000.
98214.
100000.
105000.
147500.
147500.
207792.
344827.
0
3
5
6
3
3
3
1
0
0
0
0
0
0
0
0
3
3
2
4
1
4
4
3
3
7
7
3
3
0
4
4
0
0
2
0
8
6
0
0
0
1
9
3
3
0
0
7
1
0
0
9
8
0
9
2
0
4
4
4
9
1
9
9
3
0
0
0
3
0
0
0
0
2
6
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
NE
*
NE
NE
*
SG
*
NE
NE
* *
SG
SG
* *
NE
NE
NE
NE
NE
NE
NE
**
**
NE
* *
* *
NE
NE
* *
NE
SG
NE
NE
NE
NE
*
*
NE
NE
**
NE
* *
NE
**
**
iz i_tmra-
RATIO
1
1
1
2
2
1
3
5
1
1
4
16
18
7
13
27
1
3
3
98
5
207
344
.0
.
.
.5
.6
.5
.9
.1
.4
.
.4
.1
.1
.4
.5
.3
.9
.6
.1
.6
.
.1
.3
.2
.0
.8
.8
fyrene rr.o i — HA^ o a^rir i 1 e =jju u i
SITE SAMPLE
11
8
7
8
8
8
8
7
5
6
9
4
3
7
1
2
7
8
7
6
6
8
5
7
5
9
.
7
11
11
3
.
6
9
6
11
10
10
10
.
7
3
10
11
5
4
4
3
4
2
2
4
4
4
2
2
4
9
1
10
2
9
1
1
TB-l-RE
CF-1-06
MR- 1-2 5
CF-1-04
CF-1-03
CF-l-CO
CF-1-05
MR-l-CO
WH-l-CO
DM-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
MR-1-01
IH-l-CO
BR-l-CO
MR-1-07
CF-1-02
MR-1-17
UM-1-01
UM-l-RE
CF-1-01
ERL-15% EFFECT
WH-1-02
MR-1-11
TEL-SR(ERL*NERM)
WH-l-RE
TR-1-02
NERM-50% NO EFFECT
MR-1-02
TB-1-03
TB-1-02
SR-1-10
GL-ERL-15% EFFECT
UM-1-02
TR-1-01
UM-1-03
TB-1-04
MB-1-03
MB-l-RE
MB-1-02
GL-TEL-SR (ERL*NERM)
MR-1-19
SR-1-03
ERM-50% EFFECT
MB-1-04
TB-1-01
WH-1-01
SR-3-16
GL-NERM-50% NO EFFECT
SR-3-01
SR-1-06
SR-3-08
PEL-SR(ERM*NERH)
BR-1-09
BR-1-08
SR-3-24
SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
SR-3-05
BR-1-07
GL-ERM-50% EFFECT
BR-1-01
SR-3-06
GL-NEC-MAX NO EFFECT
TR-1-03
IH-1-04
MB-1-01
BR-1-03
TR-1-04
NEC -MAX NO EFFECT
IH-1-03
IH-1-06
£UXiU*£llL - UUl_
?OXIC SURV
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
100
120
109
128
123
100
114
100
100
100
100
100
100
108
100
100
91
102
115
119
86
64
36
90
109
100
109
52
11
100
117
81
114
93
95
100
97
114
96
95
0
71
96
97
10
88
88
97
102
103
96
80
89
100
98
0
75
79
82
1
1
.0
.3
.3
.4
.0
.0
.9
.0
.0
.0
.0
.0
.0
.1
.0
.0
.9
.7
.1
.3
.5
.9
.5
.7
.5
.0
.3
.3
.4
.0
.9
.4
.9
.2
.5
.0
.0
.0
.2
.5
.0
.7
.1
.4
.3
.3
.2
.4
.6
.8
.1
.3
.5
.0
.6
.0
.8
.0
.9
.4
.4
.d.L ui
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
TX
TX
MJ. ra=j
GROW
10
10
95
10
82
10
98
10
10
ND
ND
10
10
79
10
10
91
94
92
ND
ND
73
74
58
11
ND
92
97
72
97
ND
ND
ND
10
ND
ND
ND
89
91
ND
ND
91
10
94
60
92
92
10
10
10
94
85
96
92
ND
ND
ND
85
ND
96
68
iS/ 9 -
TOXG
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
TX
NT
TX
ND
ND
TX
TX
TX
NT
ND
TX
NT
TX
TX
ND
ND
ND
NT
ND
ND
ND
TX
TX
ND
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
ND
ND
ND
TX
ND
NT
NT
MATURE TOXM
ND
90
12
80
93
10
77
10
ND
ND
ND
10
10
68
10
10
31
48
65
ND
ND
25
ND
24
ND
ND
95
ND
ND
10
ND
ND
ND
ND
ND
ND
ND
63
10
ND
ND
ND
95
11
37
95
10
10
10
10
11
10
10
96
ND
ND
ND
10
ND
0.
0.
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
TX
NT
NT
ND
ND
TX
ND
TX
ND
ND
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
NT
NT
ND
ND
ND
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 25
NE no effect I NC<1 I NG=1 I SG 1-2 i * 2-4 I **>4
NUMCODE=412 CHEM=Pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
625000.0 ** 625.0 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
26
nurai.yL>c=^.
CONC I
149.3
419.4
481.5
526.3
588.2
614.0
656.3
666.7
714.3
833.3
833.3
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1205.9
1289.9
1500.0
2375.0
3779.6
5666.7
6230.8
8620.7
8620.7
11097.4
12222.2
13243.2
14090.9
14285.7
14285.7
14285.7
15294.1
17250.0
17250.0
19230.8
24285.7
27000.0
27000.0
27647.1
30661.5
34000.0
38360.1
39325.8
54500.0
54500.0
75000.0
80000.0
80000.0
80000.0
94805.2
137931.0
284090.9
u unnj
SFFECT
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
**
NE
* *
NC
NE
NE
NE
NE
SG
SG
NE
* *
NE
**
**
**
KL=r>enz \-n
TOXG'
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
ND
ND
ND
g/g —
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA14 SAMPTYP=bottom sediment - total
CONC EFFECT RATIO SITE SAMPLE i
0.6 5 WH-1-02
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
5 WH-l-RE
3 SR-1-10
GL-NERM-50% NO EFFECT
9 TR-1-01
NERM-50% NO EFFECT
9 TR-1-02
GL-TEL-SR (ERL*NERM)
3 SR-1-03
TEL-SR(ERL*NERM)
4 SR-3-16
4 SR-3-08
12.0 5 WH-1-01
14.1 2 BR-1-09
GL-ERL-15% EFFECT
ERL-15% EFFECT
5.2 3 SR-1-06
15.3 2 BR-1-08
4 SR-3-24
4 SR-3-02
GL-NERH-85% NO EFFECT
1.0 4 SR-3-05
GL-PEL-SR(ERM*NERH)
4 SR-3-01
27.6 2 BR-1-07
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
GL-ERM-50% EFFECT
ERM-50% EFFECT
9 TR-1-04
9 TR-1-03
34.0 2 BR-1-03
39.3 2 BR-1-01
75.0 1 IH-1-04
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
94.8 1 IH-1-03
137.9 1 IH-1-06
284.1 1 IH-1-07
27
614.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1205.9
1500.0
1500.0
2000.0
2666.7
3333.3
4597.4
5666.7
6129.9
8620.7
12222.2
13243.2
14090.9
14090.9
14090.9
14285.7
15294.1
17250.0
19230.8
19230.8
24285.7
24346.7
27000.0
27647.1
29750.0
30282.0
30823.5
30823.5
32500.0
33333.3
34000.0
39325.8
75000.0
80000.0
80000.0
80000.0
94805.2
137931.0
284090.9
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
* *
**
* *
* *
NE
NE
SG
NE
* *
NE
NE
it it
* *
**
NE
•**
**
* *
TOXIC
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
^•Wt AAbldl W
SURV
40
100
100
100
100
100
100
100
101
100
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
100.0
115.6
111.
.8
110.4
35.0
83.
12.
113.
113.
105.
104.
116.
86.
93!
87.
77.
100.
0.
111.
1.
1.
0.
,4
5
7
3
9
5
2
4
4
5
3
0
0
8
4
4
0
i_u
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
TX
i-aj. unj.ra-1
GROW TOXG
11
10
ND
10
10
10
10
14
10
ND
ND
95
10
10
13
90
87
85
10
10
94
10
85
ND
ND
85
85
ND
94
96
68
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
ND
ND
TX
TX
ND
NT
NT
NT
ND
ig/g
MATURE TOXM
ND
ND
ND
10
10
10
10
ND
33
ND
ND
23
16
61
ND
0.
0.
22
14
51
22
12
0.
ND
ND
68
0.
ND
74
0.
0.
ND
ND
ND
ND
NT
NT
NT
NT
ND
NT
ND
ND
NT
NT
NT
ND
TX
NT
TX
NT
NT
TX
NT
TX
ND
ND
NT
TX
ND
NT
NT
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
28
149.3
419.4
481.5
500.0
526.3
588.2
614.0
627.9
656.3
666.7
714.3
2.0 NE . 11 TB-l-RE
NE . 8 CF-1-06
NE . 8 CF-1-04
NC 0.6 7 MR-1-11
NE . 6 UM-l-RE
NC 0.7 7 MR-1-17
NE . 8 CF-1-02
NC 0.6 5 WH-1-02
NE . 6 UM-1-01
NE . 7 MR-1-25
NC 0.9 7 MR-1-07
SG 1.3 8 CF-1-03
NE . 8 CF-l-CO
NE . 8 CF-1-05
NC 1.0 11 TB-1-02
NE . 7 MR-l-CO
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 9 TR-l-CO
NE . 4 SR-3-CO
NE . 3 SR-l-CO
SG 1.3 7 MR-1-01
NE . 1 IH-l-CO
NE . 2 BR-l-CO
NERM-50% NO EFFECT
TEL-SR (ERL*NERM)
NE . 5 WH-l-RE
* 2.3 8 CF-1-01
ERL-15% EFFECT
SG 1.5 3 SR-1-10
NE . 11 TB-1-04
SG 2.0 11 TB-1-03
NE . 9 TR-1-01
* 3.0 7 MR-1-02
NE . 6 UM-1-02
NE . 6 UM-1-03
NE . 10 MB-1-03
NE . 9 TR-1-02
NE . 10 MB-1-02
NE . 10 MB-l-RE
** 5.7 3 SR-1-03
GL-ERL-15% EFFECT
** 8.0 7 MR-1-19
GL-TEL-SR (ERL*NERM)
NE . 4 SR-3-16
GL-NERM-50% NO EFFECT
NE . 4 SR-3-08
** 12.0 5 WH-1-01
SG 1.7 2 BR-1-09
ERM-50% EFFECT
** 14.3 3 SR-1-06
NE . 2 BR-1-08
PEL-SR(ERM*NERH)
NE . 4 SR-3-24
NE . 10 MB-1-04
NE . 4 SR-3-02
NERH-85% NO EFFECT
NE . 4 SR-3-05
GL-NERH-85% NO EFFECT
NE . 4 SR-3-01
GL-PEL-SR (ERM*NERH)
* 3.4 2 BR-1-07
GL-ERM-50% EFFECT
NE . 9 TR-1-04
NE . 9 TR-1-03
NE . 10 MB-1-01
** 4.2 2 BR-1-03
** 4.8 2 BR-1-01
** 49.4 11 TB-1-01
** 75.0 1 IH-1-04
NE . 4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
** 94.8 1 IH-1-03
137931.0 ** 137.9 1 IH-1-06
833.3
833.3
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1135.7
1205.9
1289.9
1289.9
1500.0
1818.2
1818.2
2000.0
2375.0
2444.4
3090.9
3300.0
3333.3
3333.3
3750.0
5666.7
5666.7
6230.8
6989.
8620.
8620.
12222.
13243.
14090.
14090.
14285.
15294.1
16461.4
17250.0
18000.0
19230.8
19230.8
24285.7
24285.7
27000.0
27360.0
27647.1
30823.5
32500.0
33333.3
33333.3
34000.0
39325.8
45000.0
75000.0
80000.0
80000.0
80000.0
94805.2
.U1U bt
roxic
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
£uj.meuu
SURV
100.0
120.3
128.4
90.7
86.5
115.1
102.7
36.5
119.3
109.3
91.9
123.0
100.0
114.9
11.4
100.0
100.0
100.0
100.0
100.0
100.0
108.1
100.0
100.0
109.5
64.9
100.0
93.2
52.3
81.4
109.3
117.9
114.9
95.5
100.0
97.0
100.0
96.2
114.0
96.1
88.3
71.7
88.2
10.3
97.4
102.6
95.5
103.8
96.1
97.4
80.3
82.9
98.6
75.8
79.0
89.5
0.0
0.0
100.0
1.4
1.4
- uvi
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
TX
TX
NT
TX
TX
.aj. ui
GROW
10
10
10
58
ND
92
94
74
ND
95
91
82
10
98
72
10
10
ND
ND
10
10
79
10
10
11
73
97
10
97
ND
92
ND
ND
ND
ND
ND
ND
91
89
10
92
91
92
60
10
10
ND
10
94
94
85
ND
ND
ND
85
96
ND
ND
92
96
68
yj.io-i
TOXG
NT
NT
NT
TX
ND
TX
NT
TX
ND
NT
TX
TX
NT
NT
TX
NT
NT
ND
ND
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
ND
TX
ND
ND
ND
ND
ND
ND
TX
TX
NT
NT
NT
NT
TX
NT
NT
ND
NT
NT
NT
TX
ND
ND
ND
TX
NT
ND
ND
NT
NT
NT
19 /y
MATURE
ND
90
80
24
ND
65
48
ND
ND
12
31
93
10
77
ND
10
ND
ND
ND
10
10
68
10
10
ND
25
10
ND
ND
ND
95
ND
ND
ND
ND
ND
ND
10
63
95
95
ND
10
37
10
10
ND
10
11
11
10
ND
ND
ND
10
10
ND
ND
96
0.
0.
TOXM
ND
NT
NT
TX
ND
NT
NT
ND
ND
NT
TX
NT
NT
NT
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
TX
NT
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
ND
NT
TX
NT
NT
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
ND
ND
NT
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 29
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
NUMCODE=413 CHEM=Benz(a)anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
284090.9 ** 284.1 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
30
CONC I
149.3
645.2
714.3
833.3
833.3
894.7
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1111.1
1125.0
1250.0
1443.8
1637.7
1647.1
1647.1
1929.8
2400.0
3000.0
4918.7
8769.2
9310.3
12222.2
12222.2
13333.3
14311.0
15000.0
16756.8
16756.8
16756.8
19230.8
21363.6
21363.6
23571.4
23809.5
25882.4
27000.0
27000.0
31954.0
35922.7
40588.2
44943.8
47794.1
47794.1
55000.0
80000.0
80000.0
80000.0
92857.1
111688.3
224137.9
443181.8
JVC* — *.
!FFE<
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
* *
NE
NE
NE
**
SG
NE
SG
NE
*
NE
* *
**
**
**
NE no effect | NC<1 | NG=1 | SG 1-2 2-4
NUMCODE=414 CHEM=Chrysene TEST=CR14 SAMPTYP=bottom
8 CF-1-06
8 CF-1-04
8 CF-1-03
8 CF-l-CO
8 CF-1-05
7 MR-1-17
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
0.5 7 MR-1-11
7 MR-1-07
7 MR-1-25
NERM-50% NO EFFECT
8 CF-1-01
5 WH-l-RE
8 CF-1-02
1.5 5 WH-1-02
3 SR-1-10
7 MR-1-02
TEL-SR(ERL*NERM)
7 MR-1-19
4 SR-3-16
4 SR-3-08
GL-NERM-50% NO EFFECT
3 SR-1-03
GL-TEL-SR(ERL*NERM)
4 SR-3-24
12.7 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-02
2 BR-1-09
NERH-85% NO EFFECT
4 SR-3-05
4.3 3 SR-1-06
1.2 2 BR-1-08
4 SR-3-01
GL-NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
1.8 2 BR-1-07
2 BR-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
2.5 2 BR-1-03
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
92.9 1 IH-1-04
111.7 1 IH-1-03
224.1 1 IH-1-06
443.2 1 IH-1-07
*>4
;eaim«
'OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
:nt - «
SURV
107.4
109.9
84.0
100.0
96.3
122.4
100.0
100.0
100.0
100.0
117.9
100.0
100.0
70.2
116.4
138.8
95.1
85.7
79.0
51.4
90.3
113.4
111.9
102.7
95.1
104.5
102.2
8.6
100.6
105.0
104.9
18.7
38.0
96.7
47.9
67.8
62.8
103.3
2.0
2.7
0.0
0.0
Jtai i
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
TX
TX
TX
TX
JINX r&=
GROW
11
11
10
10
11
12
10
ND
10
10
11
10
10
75
11
11
13
ND
11
ND
10
11
10
12
11
10
11
ND
12
10
11
52
97
10
10
10
87
11
ND
ND
ND
ND
ng/g
TOXG
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
TX
NT
NT
NT
ND
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
ND
ND
ND
ND
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 [ * 2-4 | **>4
NUMCODE=414 CHEM=Chrysene TEST=HA14 SAMPTYP=bottom sediment - total ONITS-ng/g
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
5 WH-l-RE
1.5 5 WH-1-02
3 SR-1-10
9 TR-1-02
GL-NERM-50% NO EFFECT
9 TR-1-01
NERM-50% NO EFFECT
4 SR-3-16
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
4 SR-3-08
3 SR-1-03
4 SR-3-24
12.7 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-02
GL-NERH-85% NO EFFECT
21.4 2 BR-1-09
1.0 4 SR-3-05
4.3 3 SR-1-06
25.9 2 BR-1-08
4 SR-3-01
GL-PEL-SR(ERM*NERH)
40.6 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
44.9 2 BR-1-01
PEL-SR(ERM*NERH)
55.0 2 BR-1-03
9 TR-1-03
NERH-85% NO EFFECT
4 SR-3-06
GL-NEC-MAX NO EFFECT
92.9 1 IH-1-04
111.7 1 IH-1-03
9 TR-1-04
NEC-MAX NO EFFECT
224.1 1 IH-1-06
443.2 1 IH-1-07
31
CONC 1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1647.1
1929.8
2400.0
3333.3
5855.2
6800.0
6800.0
9310.3
9905.2
10674.5
12222.2
13333.3
15000.0
16756.8
16756.8
16756.8
19230.8
19230.8
21363.6
23571.4
23809.5
25882.4
27000.0
27938.2
40588.2
40588.2
40588.2
44943.8
53302.7
55000.0
70000.0
70000.0
80000.0
80000.0
92857.1
111688.3
112500.0
112500.0
224137.9
443181.8
JLJCi— '
3FFEI
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
**
NE
* *
SG
* *
* *
NE
* *
* *
**
NE
NE
•*•*
* *
NE
* *
**
?OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
100
100
100
100
100
100
100
40
101
100
100
111
110
115
113
35
105
83
104
12
113
116
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.8
.4
.6
.3
.0
.9
.4
.5
.5
.7
.2
>i_cij. i
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
JLVJ. J.t3-
GROW
10
ND
10
10
10
10
14
11
10
ND
ND
10
10
95
10
13
10
90
94
87
85
10
-jiy/y
TOXG
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
MATURE TOXM
ND
ND
10
10
10
10
ND
ND
33
ND
ND
16
61
23
14
ND
51
0.
22
0.
22
12
ND
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
NT
NT
NT
NT
ND
NT
TX
TX
NT
TX
NT
TOX
TOX
TOX
NOT
NOT
86.4 NT 85 TX
100.0 NT 85 TX
77.3 TX
87.5 NT
111.8 NT
85
ND
94
TX
ND
NT
0.
0.
68
ND
74
TX
TX
NT
ND
NT
TOX
TOX
NOT
TOX
TOX
0,
1.
93,
1,
0,
.0
.4
.4
.4
.0
TX
TX
NT
TX
TX
ND
96
ND
68
ND
ND
NT
ND
NT
ND
ND
0.
ND
0.
ND
ND
NT
ND
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
32
NE no effect | NC<1 | NG=1 | SG 1-2
2-4 **>4
CONC I
2.0
149.3
645.2
714.3
833.3
833.3
894.7
909.1
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1111.1
1125.0
1125.0
1232.6
1250.0
1637.7
1637.7
1642.4
1647.1
1647.1
1647.1
1714.3
1818.2
1929.8
2400.0
2400.0
3000.0
3333.3
4333.3
4545.5
5000.0
5000.0
5083.2
5666.7
6800.0
8769.2
9310.3
10766.3
12222.2
13333.3
15000.0
16756.8
16756.8
19230.8
20261.8
21363.6
23571.4
23809.5
24500.0
24500.0
25882.4
25882.4
27000.0
32411.7
33333.3
40588.2
40588.2
44943.8
55000.0
70000.0
80000.0
80000.0
92857.1
111688.3
112500.0
112500.0
224137.9
'i/Ci— -3
!FFEC
NE
NE
NE
NC
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NC
NE
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
NE
SG
*
*
NE
NE
NE
* *
NE
NE
NE
**
NE
NE
* *
NE
**
NE
SG
NE
**
NE
NE
NE
NE
*
*
* *
NE
NE
* *
* *
NE
* *
NUMCODE=414 CHEM=Chrysene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE <
11 TB-l-RE
8 CF-1-06
8 CF-1-04
0.9 8 CF-1-03
8 CF-l-CO
8 CF-1-05
0.8 7 MR-1-17
1.0 11 TB-1-03
1.0 11 TB-1-02
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
0.9 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
1.0 7 MR-1-11
1.0 7 MR-1-07
10 MB-l-RE
6 UM-1-01
7 MR-1-25
2.0 8 CF-1-01
ERL-15% EFFECT
TEL-SR(ERL*NERM)
5 WH-l-RE
8 CF-1-02
NERM-50% NO EFFECT
6 UM-l-RE
11 TB-1-04
1.5 5 WH-1-02
2.4 3 SR-1-10
GL-ERL-15% EFFECT
2.8 7 MR-1-02
9 TR-1-02
6 UM-1-02
6 UM-1-03
5.5 11 TB-1-01
10 MB-1-02
GL-TEL-SR (ERL*NERM>
10 MB-1-03
9 TR-1-01
8.1 7 MR-1-19
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
13.3 3 SR-1-03
4 SR-3-24
12.7 5 WH-1-01
ERM-50% EFFECT
4 SR-3-02
PEL-SR(ERM*NERH)
1.6 2 BR-1-09
4 SR-3-05
23.8 3 SR-1-06
10 MB-1-04
NERH-85% NO EFFECT
2 BR-1-08
GL-NERH-85% NO EFFECT
4 SR-3-01
GL-PEL-SR (ERM*NERH)
10 MB-1-01
3.0 2 BR-1-07
GL-ERM-50% EFFECT
3.3 2 BR-1-01
4.1 2 BR-1-03
9 TR-1-03
4 SR-3-06
GL-NEC-MAX NO EFFECT
92.9 1 IH-1-04
111.7 1 IH-1-03
9 TR-1-04
NEC-MAX NO EFFECT
224.1 1 IH-1-06
ieaiment. - total. L
'OXIC SURV TOXS
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
100
120
128
123
100
114
115
52
11
100
100
100
100
100
100
108
100
100
90
91
100
119
109
64
109
102
86
93
36
100
109
100
117
114
0
97
95
81
114
96
88
96
102
71
103
88
96
10
95
97
97
75
80
89
79
98
100
0
1
82
.0
.3
.4
.0
.0
.9
.1
.3
.4
.0
.0
.0
.0
.0
.0
.1
.0
.0
.7
.9
.0
.3
.3
.9
.5
.7
.5
.2
.5
.0
.3
.0
.9
.9
.0
.0
.5
.4
.0
.1
.3
.2
.6
.7
.8
.2
.1
.3
.5
.4
.4
.8
.3
.5
.0
.6
.0
.0
.4
.9
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
TX
NT
GROW TOXG MATURE
10
10
10
82
10
98
92
97
72
10
10
ND
ND
10
10
79
10
10
58
91
ND
ND
95
73
11
94
ND
10
74
97
92
ND
ND
ND
ND
ND
ND
ND
89
10
92
91
10
91
10
92
94
60
ND
10
94
ND
85
96
85
ND
92
ND
96
ND
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
ND
ND
NT
NT
TX
NT
NT
TX
TX
ND
ND
NT
TX
NT
NT
ND
NT
TX
TX
TX
ND
ND
ND
ND
ND
ND
ND
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
ND
NT
NT
ND
TX
NT
TX
ND
NT
ND
NT
ND
ND
90
80
93
10
77
65
ND
ND
10
ND
ND
ND
10
10
68
10
10
24
31
ND
ND
12
25
ND
48
ND
ND
ND
10
95
ND
ND
ND
ND
ND
ND
ND
63
95
95
10
10
ND
10
10
11
37
ND
10
11
ND
10
10
10
ND
96
ND
0.
ND
TOXM
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
TX
TX
ND
ND
NT
TX
ND
NT
ND
ND
ND
NT
NT
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
TX
ND
NT
NT
ND
NT
NT
NT
ND
NT
ND
NT
ND
TOX
1.4 TX
68
NT
0.
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 33
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
— NUMCODE=414 CHEM=Chrysene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
443181.8 ** 443.2 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=CR14 SAMPTYP=bottom sediment - total UNITS=
8 CF-1-06
7 MR-1-25
8 CF-1-04
0.3 7 MR-1-11
7 MR-1-07
0.4 5 WH-1-02
7 MR-1-17
3 SR-1-10
8 CF-1-03
8 CF-l-CO
8 CF-1-05
8 CF-1-02
7 MR-l-CO
5 WH-l-CO
4 SR-3-CO '
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
5 WH-l-RE
8 CF-1-01
7 MR-1-02
TEL-SR(ERL*NERM)
7 MR-1-19
4 SR-3-08
4 SR-3-16
GL-NERM-50% NO EFFECT
3 SR-1-03
2.7 3 SR-1-06
GL-TEL-SR(ERL*NERM)
4 SR-3-24
11.3 S WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-05
4 SR-3-02
2 BR-1-09
NERH-85% NO EFFECT
0.7 2 BR-1-08
0.8 2 BR-1-03
GL-NERH-85% NO EFFECT
4 SR-3-01
1.3 2 BR-1-07
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM*NERH)
2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
125.0 1 IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
129.9 1 IH-1-03
215.5 1 IH-1-06
238.6 1 IH-1-07
34
jNuriv-.uiJ.ci-
CONC I
149.3
312.5
322.6
370.4
416.7
438.6
526.3
600.0
714.3
833.3
833.3
882.4
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1205.9
1217.4
1250.0
3526.0
3692.3
6944.4
7931.0
8632.2
9333.3
10000.0
10359.5
11000.0
12432.4
12432.4
12432.4
15714.3
19230.8
20000.0
20000.0
20588.2
23500.0
25250.0
27000.0
36470.6
50000.0
56180.5
65168.5
80000.0
80000.0
80000.0
125000.0
125000.0
125000.0
129870.1
215517.2
-*±a. /
SFFEC
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
* *
NE
NE
NE
NC
NC
NE
SG
NE
NE
* *
**
**
238636.4
im sediment -
'OXIC SURV
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
107.
138.
109.
70.
116.
51.
122.
90.
84.
100.
96.
79.
100.
100.
100.
100.
117.
100.
100.
85.
95.
113.
111.
95.
102.
104.
18.
102.
8.
104.
100.
105.
38.
62.
96.
47.
67.
103.
2.
2.
0.
0.
4
8
9
2
4
4
4
3
0
0
3
0
0
0
0
0
9
0
0
7
1
4
9
1
7
5
7
2
6
9
6
0
0
8
7
9
8
3
0
7
0
0
tote
TOXS
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
TX
TX
TX
i± UHJ
GROW
11
11
11
75
11
ND
12
10
10
10
11
11
10
ND
10
10
11
10
10
ND
13
11
10
11
12
10
52
11
ND
11
12
10
97
87
10
10
10
11
ND
ND
ND
ND
.a.£>=iig/y
TOXG MATURE
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
TX
NT
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
35
NE no effect | NC<1 | NG=1 | SG 1-2
2-4
**>4
wurn-UJJjs-'
CONC El
438.6
600.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1205.9
3333.3
4075.2
4800.0
4800.0
6944.4
7117.9
7725.0
7931.0
9333.3
10000.0
11000.0
12432.4
12432.4
12432.4
15500.0
15714.3
19230.8
19230.8
19230.8
20000.0
20588.2
23500.0
26483.2
26483.2
26666.7
27000.0
36470.6
36470.6
36470.6
65168.5
80000.0
80000.0
80000.0
125000.0
129870.1
215517.2
238636.4
i-L/
•TEC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
* *
NE
NC
NE
**
* *
**
NE
NE
**
**
NE
**
**
* *
**
=417 CHEM=Benzo (a)pyrene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
0.4 5 WH-1-02
3 SR-1-10
5 WH-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
5 WH-l-RE
9 TR-1-02
GL-NERM-50% NO EFFECT
9 TR-1-01
NERM-50% NO EFFECT
4 SR-3-08
GL-TEL-SR(ERL*NERM)
TEL-SR(ERL*NERM)
4 SR-3-16
3 SR-1-03
2.7 3 SR-1-06
4 SR-3-24
11.3 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
9 TR-1-04
0.7 4 SR-3-05
4 SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
20.0 2 BR-1-09
20.6 2 BR-1-08
23.5 2 BR-1-03
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
9 TR-1-03
4 SR-3-01
36.5 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
65.2 2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
125.0 1 IH-1-04
129.9 1 IH-1-03
215.5 1 IH-1-06
238.6 1 IH-1-07
>m seuunenc -
'OXIC SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
40
101
100
100
100
100
100
100
100
100
100
110
111
115
12
113
35
93
104
105
83
113
77
87
116
86
100
111
0
1
- 1
0
.0
.6
.0
.0
.0
.0
.0
.0
.0
.0
.0
.4
.8
.6
.5
.3
.0
.4
.5
.9
.4
.7
.3
.5
.2
.4
.0
.8
.0
.4
.4
.0
cote
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
TX
11 UJMJ
GROW
11
10
10
ND
10
10
10
10
14
ND
ND
10
10
95
87
10
13
ND
94
10
90
85
85
ND
10
85
85
94
ND
96
68
ND
.rs-ng/g
TOXG MATURE
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
TX
TX
ND
NT
TX
TX
NT
ND
NT
NT
ND
ND
33
ND
ND
10
10
10
10
ND
ND
ND
61
16
23
0.
14
ND
ND
22
51
0.
22
68
ND
12
0.
0.
74
ND
0.
0.
ND
TOXM
ND
NT
ND
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
NT
TX
TX
NT
ND
NT
TX
TX
NT
ND
NT
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
36
NE no effect I NC<1 I NG=1 I SG 1-2
2-4
*>4
INUl'lWULTC,-
CONC I
2.0
149.3
312.5
322.6
370.4
416.7
438.6
526.3
600.0
697.7
714.3
833.3
833.3
882.4
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1102.9
1158.8
1205.9
1217.4
1217.4
1250.0
1250.0
1428.6
1666.7
1818.2
1818.2
2900.0
3111.1
3333 .3
3692.3
3727.3
4075.2
4800.0
5000.0
6383.7
6944.4
7931.0
9000.0
9333.3
10000.0
10000.0
11000.0
11111.1
11216.2
12432.4
13185.3
15500.0
15500.0
15714.3
19230.8
20000.0
20588.2
20588.2
23500.0
26666.7
27000.0
27401.9
36470.6
36470.6
65168.5
80000.0
80000.0
80000.0
125000.0
129870.1
215517.2
3FFE<
NE
NE
NE
NE
NC
NC
NC
NC
NC
NE
SG
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
*
NE
NE
NE
NE
SG
NE
NE
NE
* *
NE
NE
* *
NE
NE
NE
* *
* *
NE
NE
* *
NE
NE
NE
SG
NE
*
NE
NE
*
**
NE
**
**
**
=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total
11 TB-l-RE
8 CF-1-06
7 MR-1-25
8 CF-1-04
0.6 7 MR-1-11
0.7 7 MR-1-07
0.4 5 WH-1-02
0.9 7 MR-1-17
0.6 3 SR-1-10
6 UM-1-01
1.2 8 CF-1-03
8 CF-l-CO
8 CF-1-05
8 CF-1-02
1.0 11 TB-1-03
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
5 WH-l-RE
2.0 8 CF-1-01
ERL-15% EFFECT
2.0 7 MR-1-02
10 MB-l-RE
6 UM-l-RE
10 MB-1-02
11 TB-1-04
2.0 11 TB-1-02
10 MB-1-03
6 UM-1-02
9 TR-1-02
6.0 7 MR-1-19
6 UM-1-03
GL-NERM-50% NO EFFECT
9 TR-1-01
5.5 11 TB-1-01
GL-TEL-SR (ERL*NERM)
4 SR-3-08
4 SR-3-16
10 MB-1-04
9.3 3 SR-1-03
10.0 3 SR-1-06
GL-ERL-15% EFFECT
4 SR-3-24
10 MB-1-01
ERM-50% EFFECT
11.3 5 WH-1-01
PEL-SR(ERM*NERH)
9 TR-1-04
NERH-85% NO EFFECT
4 SR-3-05
4 SR-3-02
1.9 2 BR-1-09
2 BR-1-08
GL-NERH-85% NO EFFECT
2.2 2 BR-1-03
9 TR-1-03
4 SR-3-01
GL-PEL-SR(ERM*NERH)
3.4 2 BR-1-07
GL-ERM-50% EFFECT
6.0 2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
125.0 1 IH-1-04
129.9 1 IH-1-03
215.5 1 IH-1-06
>m sec
'OXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
nmen
su:
100
120
109
128
90
91
36
115
100
119
123
100
114
102
52
100
100
100
100
100
100
108
100
100
109
64
109
100
86
97
93
11
95
117
100
114
114
81
0
88
96
95
96
10
102
75
71
82
96
103
88
97
79
98
97
80
89
100
0
1
1
u -
RV
.0
.3
.3
.4
.7
.9
.5
.1
.0
.3
.0
.0
.9
.7
.3
.0
.0
.0
.0
.0
.0
.1
.0
.0
.5
.9
.3
.0
.5
.0
.2
.4
.5
.9
.0
.0
.9
.4
.0
.3
.1
.5
.2
.3
.6
.8
.7
.9
.1
.8
.2
.4
.0
.6
.4
.3
.5
.0
.0
.4
.4
tote
TOXS
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
TX
TX
TX
l± U1\J
GROW
10
10
95
10
58
91
74
92
97
ND
82
10
98
94
97
10
10
ND
ND
10
10
79
10
10
11
73
92
ND
ND
ND
10
72
ND
ND
ND
89
ND
ND
ND
92
10
ND
91
60
10
ND
91
ND
94
10
92
10
85
ND
94
85
96
92
ND
96
68
Lrs=ng
TOXG
NT
NT
NT
NT
TX
TX
TX
TX
TX
ND
TX
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
NT
TX
TX
ND
ND
ND
NT
TX
ND
ND
ND
TX
ND
ND
ND
NT
NT
ND
TX
TX
NT
ND
NT
ND
NT
NT
NT
NT
TX
ND
NT
TX
NT
NT
ND
NT
NT
/g —
MATURE
ND
90
12
80
24
31
ND
65
10
ND
93
10
77
48
ND
10
ND
ND
ND
10
10
68
10
10
ND
25
95
ND
ND
ND
ND
ND
ND
ND
ND
63
ND
ND
ND
95
95
ND
10
37
10
ND
ND
ND
11
10
10
10
10
ND
11
10
10
96
ND
0.
0.
TOXM
ND
NT
NT
NT
TX
TX
ND
NT
NT
ND
NT
NT
NT
NT
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
TX
NT
ND
ND
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
NT
NT
ND
NT
TX
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 37
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEM=Benzo(a)pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
238636.4 ** 238.6 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
38
NE no effect | NC<1
NG=1
SG 1-2
2-4
*>4
NUMCODE=418 CHEM=Indeno (1,2, .,d)pyrene TEST=CR14 SAMPTYP=bottom sediment - total DNITS=ng/g ----
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
149.3
312.5
322.6
416.7
481.5
526.3
526.3
588.2
714.3
833.3
833.3
884.1
909.1
941.2
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1250.0
2307.7
2847.5
4588.2
6944.4
7097.2
7250.0
7333.3
7585.8
7619.0
7931.0
8108.1
8108.1
8108.1
10000.0
14285.7
14285.7
14705.9
19230.8
23115.4
26000.0
27000.0
36770.1
42696.6
46772.9
80000.0
80000.0
80000.0
94642.9
94642.9
94642.9
94805.2
125000.0
189655.2
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
*
NE
* *
NE
NE
NC
NE
SG
NE
NE
NE
* *
* *
* *
**
.
_
0.5
0.5
t
0.3
.
.
2.4
8.4
0.8
t
1.5
94.6
94.8
125.0
189.7
8
7
8
7
7
5
7
8
8
8
8
8
7
5
5
4
3
3
7
1
2
7
7
2
4
4
3
3
4
5
2
4
2
4
2
4
2
4
.
1
1
1
1
CF-1-06
MR-1-25
CF-1-04
MR-1-07
MR-1-11
WH-1-02
MR-1-17
CF-1-02
CF-1-03
CF-l-CO
CF-1-05
CF-1-01
MR-l-CO
WH-l-RE
WH-l-CO
SR-3-CO
SR-l-CO
SR-1-10
MR-1-01
IH-l-CO
BR-l-CO
NERM-50% NO EFFECT
MR-1-02
MR-1-19
TEL-SR(ERL*NERM)
BR-1-08
SR-3-08
GL-NERM-50% NO EFFECT
SR-3-24
SR-1-03
GL-TEL-SR (ERL*NERM)
SR-1-06
SR-3-16
WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
BR-1-09
SR-3-05
NERH-85% NO EFFECT
BR-1-07
SR-3-02
GL-NERH-85% NO EFFECT
BR-1-03
SR-3-01
PEL-SR(ERM*NERH)
BR-1-01
GL-PEL-SR (ERM*NERH)
SR-3-06
NEC -MAX NO EFFECT
GL-NEC-MAX NO EFFECT
IH-1-04
GL-ERM-50% EFFECT
ERM-50% EFFECT
IH-1-03
IH-1-07
IH-1-06
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
107
138
109
116
70
51
122
79
84
100
96
95
100
85
100
100
100
90
117
100
100
113
111
38
95
102
104
18
102
8
105
104
47
100
62
96
67
103
2
2
0
0
.4
.8
.9
.4
.2
.4
.4
.0
.0
.0
.3
.1
.0
.7
.0
.0
.0
.3
.9
.0
.0
.4
.9
.0
.1
.2
.5
.7
.7
.6
.
.
.0
.9
.
.9
.6
.
.8
.7
.
.8
.
.3
.
.0
.7
.0
.0
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
TX
11
11
11
11
75
ND
12
11
10
10
11
13
10
ND
ND
10
10
10
11
10
10
11
10
97
11
11
10
52
12
ND
10
11
10
12
87
10
10
11
ND
ND
ND
ND
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
TX
NT
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
39
NUMCODE=418 CHEM=Indeno (1,2,3-c,d)pyrene TEST=HA14 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
526.3
941.2
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
2000.0
3333.3
3333.3
3972.2
4588.2
5039.5
5501.3
6944.4
7250.0
7333.3
7619.0
7619.0
7619.0
7931.0
8108.1
10000.0
14285.7
14705.9
19230.8
19230.8
22360.7
26000.0
26000.0
26000.0
26495.3
27000.0
27000.0
42696.6
53333.3
72500.0
80000.0
80000.0
80000.0
94642.9
94805.2
125000.0
189655.2
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
it *
NE
NE
NE
*
NE
**
* *
NC
* *
NE
**
NE
**
NE
NE
NE
* *
**
* *
**
0.5 5
5
5
9
4
3
3
1
2
9
9
.
4.6 2
.
4
4
3
2.4 3
4
8.4 5
10.0 2
0.7 4
14.7 2
4
.
26.0 2
4
.
42.7 2
9
9
4
.
94.6 1
94.8 1
125.0 1
189.7 1
WH-1-
WH-1-
WH-1-
TR-1-
SR-3-
SR-1-
SR-1-
IH-1-
BR-1-
TR-1-
TR-1-
NE1
GL-
BR-1-
TE3
GL
SR-3-
SR-3-
SR-1-
SR-1-
GL-
EK
SR-3-
WH-1-
BR-1-
SR-3
BR-1-
SR-3-
GL
GL-
BR-1
GL-
ER1
PE;
SR-3-
NE1
BR-1-
TR-1
TR-1
SR-3-
NEI
GL-
IH-1
IH-1
IH-1
IH-1
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
-1-08
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL'NERM)
.-3-08
.-3-24
.-1-03
.-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
.-3-16
:-i-oi
.-1-09
.-3-05
-1-07
.-3-02
GL-NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
.-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
PEL-SRIERM*NERH)
.-3-01
NERH-85% NO EFFECT
:-l-Ol
L-l-03
1-1-04
L-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
40.
100.
100.
100.
100.
100.
101.
100.
100.
100.
100.
113.
110.
113.
115.
12.
111.
35.
83.
104.
86.
105.
0
0
0
0
0
0
6
0
0
0
0
7
4
3
6
5
8
0
4
5
4
9
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
11
14
10
ND
10
10
10
10
10
ND
ND
85
10
10
95
87
10
13
90
94
85
10
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
ND
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
ND
ND
ND
ND
10
10
33
10
10
ND
ND
22
61
14
23
0.
16
ND
0.
22
0.
51
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
NT
NT
NT
NT
NT
ND
TX
TX
TX
NT
TOX
NOT
77.3 TX
116.2 NT
85
10
TX
NT
68
12
NT
NT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
100.0
87.5
93.4
111.8
0.0
1.4
0.0
1.4
NT
NT
NT
NT
TX
TX
TX
TX
85
ND
ND
94
ND
96
ND
68
TX
ND
ND
NT
ND
NT
ND
NT
0.
ND
ND
74
ND
0.
ND
0.
TX
ND
ND
NT
ND
NT
ND
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
40
NUMCODE=418 CHEM=Indeno (1,2,3-c,d)pyrene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE
CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
149.3
312.5
322.6
416.7
481.5
500.0
526.3
526.3
588.2
651.2
714.3
833.3
833 .3
884.1
909.1
941.2
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1062.5
1250.0
1666.7
2000.0
2307.7
2681.8
2777.8
2794.1
3333.3
4000.0
4588.2
4613.9
4800.0
6944.4
7250.0
7333.3
7619.0
7619.0
7931.0
8108.1
8555.6
8555.6
8801.3
9054.1
10000.0
14285.7
14705.9
19230.8
19230.8
22360.7
26000.0
26000.0
27000.0
42696.6
53333.3
72500.0
80000.0
80000.0
80000.0
94642.9
94805.2
125000.0
189655.2
NE
NE
NE
NC
NC
NE
NC
NC
NE
NE
SG
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NG
SG
NE
NE
NE
*
NE
NE
*
NE
NE
NE
NE
NE
NE
NE
NE
**
* *
NE
* *
NE
«
NE
**
NE
* *
NE
* *
NE
NE
NE
* *
* *
* *
* *
0.7
0.8
0.5
0.9
1.3
1.6
.
1.0
1.6
.
.
2.0
3.8
7.3
7.6
8.4
3.6
5.3
9.3
15.3
.
94.6
94.8
125.0
189.7
8
7
8
7
7
6
5
7
8
6
8
8
8
8
7
5
5
6
9
4
3
3
7
1
2
.
10
7
10
9
7
6
6
9
10
2
.
10
4
4
3
3
.
4
5
10
2
4
2
4
2
4
2
9
9
4
1
1
1
1
CF-1-06
MR-1-25
CF-1-04
MR-1-07
MR-1-11
UM-l-RE
WH-1-02
MR-1-17
CF-1-02
UM-1-01
CF-1-03
CF-l-CO
CF-1-05
CF-1-01
MR-l-CO
WH-l-RE
WH-l-CO
UM-l-CO
TR-l-CO
SR-3-CO
SR-l-CO
SR-1-10
MR-1-01
IH-l-CO
BR-l-CO
TEL-SR (ERL*NERM) @
NERM-50% NO EFFECT
ERL-15% EFFECT @
MB-l-RE
MR-1-02
MB-1-02
TR-1-01
MR-1-19
UM-1-03
UM-1-02
GL-NERM-50% NO EFFECT
TR-1-02
MB-1-03
BR-1-08
GL-TEL-SR (ERL'NERM)
MB-1-04
SR-3-08
SR-3-24
SR-1-03
SR-1-06
GL-ERL-15% EFFECT
SR-3-16
WH-1-01
MB-1-01
NERH-85% NO EFFECT
PEL-SR (ERM*NERH)
ERM-50% EFFECT
BR-1-09
SR-3-05
BR-1-07
SR-3-02
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
BR-1-03
GL-ERM-50% EFFECT
SR-3-01
BR-1-01
TR-1-03
TR-1-04
SR-3-06
NEC-MAX NO EFFECT
GL -NEC -MAX NO EFFECT
IH-1-04
IH-1-03
IH-1-07
IH-1-06
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
120.3
109.3
128.4
91.9
90.7
86.5
36.5
115.1
102.7
119.3
123.0
100.0
114.9
64.9
100.0
109.5
100.0
100.0
100.0
100.0
100.0
100.0
108.1
100.0
100.0
.
.
.
100.0
109.3
97.0
81.4
114.0
114.9
117.9
100.0
95.5
97.4
95.5
88.3
102.6
96.2
10.3
96.1
71.7
75.8
88.2
96.1
80.3
103.8
79.0
97.4
89.5
98.6
82.9
100.0
0.0
1.4
0.0
1.4
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
TX
NT
TX
NT
TX
NT
NT
NT
TX
TX
TX
TX
10
95
10
91
58
ND
74
92
94
ND
82
10
98
73
10
11
10
ND
ND
10
10
97
79
10
10
ND
92
ND
ND
89
ND
ND
ND
ND
10
ND
92
10
91
60
10
91
ND
92
94
85
10
85
94
96
ND
ND
92
ND
96
ND
68
NT
NT
NT
TX
TX
ND
TX
TX
NT
ND
TX
NT
NT
TX
NT
NT
NT
ND
ND
NT
NT
TX
TX
NT
NT
ND
TX
ND
ND
TX
ND
ND
ND
ND
NT
ND
NT
NT
TX
TX
NT
NT
ND
NT
NT
TX
NT
TX
NT
NT
ND
ND
NT
ND
NT
ND
NT
90
12
80
31
24
ND
ND
65
48
ND
93
10
77
25
10
ND
ND
ND
ND
10
10
10
68
10
10
ND
95
ND
ND
63
ND
ND
ND
ND
10
ND
95
10
10
37
95
ND
ND
10
11
10
10
10
11
10
ND
ND
96
ND
0.
ND
0.
NT
NT
NT
TX
TX
ND
ND
NT
NT
ND
NT
NT
NT
TX
NT
ND
ND
ND
ND
NT
NT
NT
NT
NT
NT
ND
NT
ND
ND
NT
ND
ND
ND
ND
NT
ND
NT
NT
NT
TX
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
NT
ND
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h, Dperylene TEST=CR14 SAMPTYP=bottom sediment - total
CONC EFFECT RATIO SITE SAMPLE C
283.6 NE . 8 CF-1-06
370.4 NC 0.4 7 MR-1-11
416.7 NE . 7 MR-1-07
437.5 NE . 7 MR-1-25
526.3 NC 0.6 5 WH-1-02
526.3 NE . 7 MR-1-17
764.7 NE . 5 WH-l-RE
833.3 NE . 8 CF-l-CO
833.3 NE . 8 CF-1-05
898.6 NE . 8 CF-1-01
909.1 NE . 7 MR-l-CO
1000.0 NE . 5 WH-l-CO
1000.0 NE . 4 SR-3-CO
1000.0 NE . 3 SR-l-CO
1000.0 NE . 7 MR-1-01
1000.0 NE . 1 IH-l-CO
1000.0 NE . 2 BR-l-CO
1250.0 NE . 7 MR-1-02
1250.0 . . NERM-50% NO EFFECT
1285.7 NE . 8 CF-1-03
1300.0 NE . 3 SR-1-10
1384.6 NE . 7 MR-1-19
2064.5 NE . 8 CF-1-04
2470.6 NE . 8 CF-1-02
4154.7 . . TEL-SR(ERL*NERM)
5352.9 NC 0.3 2 BR-1-08
6944.4 NE . 4 SR-3-08
7097.2 . . GL-NERM-50% NO EFFECT
7250.0 NE . 4 SR-3-24
7931.0 NE . 4 SR-3-16
8108.1 ** 9.2 5 WH-1-01
9900.0 . . GL-TEL-SR (ERL*NERM)
10333.3 NE . 3 SR-1-03
10909.1 NE . 2 BR-1-09
13809.5 * 3.3 3 SR-1-06
13809.5 . - GL-ERL-15% EFFECT
13809.5 . . ERL-15% EFFECT
14285.7 NE . 4 SR-3-05
14285.7 . . NERH-85% NO EFFECT
15294.1 NC 0.8 2 BR-1-07
19230.8 NE . 4 SR-3-02
23115.4 . . GL-NERH-85% NO EFFECT
27000.0 NE . 4 SR-3-01
31000.0 SG 1.7 2 BR-1-03
40089.2 . . PEL-SR(ERM*NERH)
42696.6 NE . 2 BR-1-01
50994.9 . • GL-PEL-SR(ERM*NERH)
80000.0 NE . 4 SR-3-06
80000.0 . . NEC-MAX NO EFFECT
80000.0 . . GL-NEC-MAX NO EFFECT
112500.0 ** 112.5 1 IH-1-04
112500.0 . . GL-ERM-50% EFFECT
112500.0 . . ERM-50% EFFECT
124675.3 ** 124.7 1 IH-1-03
238636.4 ** 238.6 1 IH-1-07
241379.3 ** 241.4 1 IH-1-06
41
>U L.UIU
'OXIC
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
j>tJU.J.iutrii
SURV
107.4
70.2
116.4
138.8
51.4
122.4
85.7
100.0
96.3
95.1
100.0
100.0
100.0
100.0
117.9
100.0
100.0
113.4
84.0
90.3
111.9
109.9
79.0
38.0
95.1
102.2
102.7
8.6
104.5
105.0
18.7
104.9
47.9
100.6
96.7
62.8
67.8
103.3
2.0
2.7
0.0
0.0
L. - L
TOXS
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
TX
.uueti.
GROW
11
75
11
11
ND
12
ND
10
11
13
10
ND
10
10
11
10
10
11
10
10
10
11
11
97
11
11
12
ND
10
10
52
11
10
12
10
87
10
11
ND
ND
ND
ND
UIMX±£>:
TOXG i
NT
TX
NT
NT
ND
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
ND
ND
ND
ND
=«H/g
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h,iJperylene TEST=HA14 SAMPTYP=bottom sediment -
CONC EFFECT RATIO SITE SAMPLE C
42
526
764
1000
1000
1000
1000
1000
1000
1300
2000
3333
3333
4122
5198
5352
5781
6944
7250
7931
8108
8108
8108
10333
10909
13809
14285
15294
19230
19230
24416
27000
27000
28931
31000
31000
31000
42696
50000
65000
80000
80000
80000
112500
124675
238636
241379
.3
.7
.0
.0
.0
.0
.0
.0
.0
.0
.3
.3
.2
.8
.9
.3
.4
.0
.0
.1
.1
.1
.3
.1
.5
.7
.1
.8
.8
.3
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
.0
.0
.0
.3
.4
.3
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
**
NE
NE
NE
**
NE
**
*
NC
it *
NE
NE
**
**
NE
NE
NE
**
**
**
**
0.6
.
.
.
.
.
.
.
.
5.4
,
.
9.2
10.9
3.3
0.7
15.3
.
31.0
42.7
.
.
.
112.5
124.7
238.6
241.4
5
5
5
9
4
3
1
2
3
9
9
.
.
.
2
.
4
4
4
5
.
.
3
2
3
4
2
4
4
.
2
2
9
9
4
.
.
1
1
1
1
WH-1-
WH-1-
WH-1-
TR-1-
SR-3-
SR-1-
IH-1-
BR-1-
SR-1-
TR-1-
TR-1-
NE!
GL-
TE]
BR-1-
GL-
SR-3-
SR-3-
SR-3-
WH-1-
GL-
ER1
SR-1-
BR-1-
SR-1-
SR-3-
BR-1-
SR-3-
GL-
GL-
SR-3-
NE1
PEI
BR-1-
GL-
ER1
BR-1'
TR-1'
TR-1'
SR-3'
NEI
GL'
IH-1
IH-1
IH-1'
IH-1'
NERM-50% NO EFFECT
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
:-l-08
GL-TEL-SR(ERL*NERM)
1-3-08
1-3-24
1-3-16
i-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
1-1-03
1-1-09
1-1-06
1-3-05
1-1-07
1-3-02
GL-NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
1-3-01
NERH-85% NO EFFECT
PEL-SR(ERM*NERH)
.-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
.-1-01
.-1-03
.-1-04
1-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
)ttom
'OXIC
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
seux.
su:
40
100
100
100
100
100
100
100
101
100
100
113
110
113
111
35
115
83
12
104
86
105
men
RV
.0
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.7
.4
.3
.8
.0
.6
.4
.5
.5
.4
.9
.u - i
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
-UUdX
GROW
11
14
10
ND
10
10
10
10
10
ND
ND
85
10
10
10
13
95
90
87
94
85
10
urj j. i o
TOXG
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
ND
TX
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
=uu/U
MATURE
ND
ND
ND
ND
10
10
10
10
33
ND
ND
22
61
14
16
ND
23
0.
0.
22
0.
51
TOXM
ND
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
TX
NT
NT
NT
ND
NT
TX
NT
TX
TX
NT
NOT
TOX
116.2 NT
77.3 TX
10
85
NT
TX
12
68
NT
NT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
100.0
87.5
93.4
111.8
0.0
1.4
0.0
1.4
NT
NT
NT
NT
TX
TX
TX
TX
85
ND
ND
94
ND
96
ND
68
TX
ND
ND
NT
ND
NT
ND
NT
0.
ND
ND
74
ND
0.
ND
0.
TX
ND
ND
NT
ND
NT
ND
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo (g, h, Dperylene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=
CONC EFFECT RATIO SITE SAMPLE C
43
2.0
283.6
370.4
416.7
437.5
500.0
526.3
526.3
764.7
767.4
833.3
833.3
898.6
909.1
909.1
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1087.5
1165.9
1175.0
1250.0
1250.0
1285.7
1300.0
1384.6
1666.7
1818.2
2000.0
2064.
2470.
2777.
2909.
3333.
3333.
5000.0
5352.9
5352.9
6000.0
6588.0
6944.4
7250.0
7931.0
8108.1
8108.1
10333.3
10621.2
10909.1
11900.3
13333.3
13333.3
13809.5
14285.7
15294.1
19230.8
19230.8
21098.2
23147.1
27000.0
31000.0
42696.6
50000.0
65000.0
80000.0
80000.0
80000.0
112500.0
124675.3
238636.4
NE . 11 TB-l-RE
NE . 8 CF-1-06
NC 0.6 7 MR-1-11
NC 0.6 7 MR-1-07
NE . 7 MR-1-25
NE . 6 UM-l-RE
NC 0.6 5 WH-1-02
NC 0.8 7 MR-1-17
NE . 5 WH-l-RE
NE . 6 UM-1-01
NE . 8 CF-l-CO
NE . 8 CF-1-05
NC 0.7 8 CF-1-01
NE . 11 TB-1-04
SG 2.0 11 TB-1-02
NE . 7 MR-l-CO
NE . 5 WH-l-CO
NE . 6 UM-l-CO
NE . 9 TR-l-CO
NE . 4 SR-3-CO
NE . 3 SR-l-CO
SG 1.5 7 MR-1-01
NE . 1 IH-l-CO
NE . 2 BR-l-CO
NERM-50% NO EFFECT
TEL-SR(ERL'NERM)
NE . 10 MB-l-RE
SG 1.9 7 MR-1-02
ERL-15% EFFECT
NC 1.0 8 CF-1-03
SG 1.3 3 SR-1-10
* 2.1 7 MR-1-19
NE . 10 MB-1-02
* 4.0 11 TB-1-03
NE . 9 TR-1-01
NE . 8 CF-1-04
NE . 8 CF-1-02
NE . 6 UM-1-02
NE . 6 UM-1-03
NE . 9 TR-1-02
NE . 10 MB-1-03
** 11.0 11 TB-1-01
NE . 2 BR-1-08
GL-NERM-50% NO EFFECT
NE . 10 MB-1-04
GL-TEL-SR
NE . 4 SR-3-08
NE . 4 SR-3-24
NE . 4 SR-3-16
** 9.2 5 WH-1-01
GL-ERL-15% EFFECT
** 10.3 3 SR-1-03
ERM-50% EFFECT
* 3.4 2 BR-1-09
PEL-SR(ERM*NERH)
NE . 10 MB-1-01
NERH-85% NO EFFECT
** 13.8 3 SR-1-06
NE . 4 SR-3-05
** 4.8 2 BR-1-07
NE . 4 SR-3-02
GL-NERH-85% NO EFFECT
GL-PEL-SR (ERM*NERH)
GL-ERM-50% EFFECT
NE . 4 SR-3-01
** 9.8 2 BR-1-03
** 13.4 2 BR-1-01
NE . 9 TR-1-03
NE . 9 TR-1-04
NE . 4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
** 112.5 1 IH-1-04
** 124.7 1 IH-1-03
** 238.6 1 IH-1-07
i 1- l-Wlll OCUXiUCU
TOXIC SURV
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
100
120
90
91
109
86
36
115
109
119
100
114
64
93
11
100
100
100
100
100
100
108
100
100
100
109
123
100
114
97
52
81
128
102
117
114
100
95
0
97
95
88
102
96
71
96
88
75
10
96
80
103
97
79
89
98
82
100
0
1
0
.0
.3
.7
.9
.3
.5
.5
.1
.5
.3
.0
.9
.9
.2
.4
.0
.0
.0
.0
.0
.0
.1
.0
.0
.0
.3
.0
.0
.0
.0
.3
.4
.4
.7
.9
.9
.0
.5
.0
.4
.5
.3
.6
.1
.7
.2
.2
.8
.3
.1
.3
.8
.4
.0
.5
.6
.9
.0
.0
.4
.0
.U 1
TOXS
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
TX
NT
NT
TX
TX
NT
NT
NT
TX
TX
TX
-uuau.
GROW
10
10
58*
91
95
ND
74
92
11
ND
10
98
73
10
72
10
10
ND
ND
10
10
79
10
10
ND
92
82
97
89
ND
97
ND
10
94
ND
ND
ND
ND
ND
10
ND
92
10
10
91
91
92
ND
60
94
85
10
94
85
96
ND
ND
92
ND
96
ND
U1MJ. iO
TOXG
NT
NT
TX
TX
NT
ND
TX
TX
NT
ND
NT
NT
TX
NT
TX
NT
NT
ND
ND
NT
NT
TX
NT
NT
ND
TX
TX
TX
TX
ND
NT
ND
NT
NT
ND
ND
ND
ND
ND
NT
ND
NT
NT
NT
NT
TX
NT
ND
TX
NT
TX
NT
NT
TX
NT
ND
ND
NT
ND
NT
ND
-jiy/y
MATURE TOXM
ND
90
24
31
12
ND
ND
65
ND
ND
10
77
25
ND
ND
10
ND
ND
ND
10
10
68
10
10
ND
95
93
10
63
ND
ND
ND
80
48
ND
ND
ND
ND
ND
10
ND
95
10
95
ND
10
10
ND
37
11
10
10
11
10
10
ND
ND
96
ND
0.
ND
ND
NT
TX
TX
NT
ND
ND
NT
ND
ND
NT
NT
TX
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
ND
ND
ND
ND
ND
NT
ND
NT
NT
NT
ND
NT
NT
ND
TX
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 44
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=419 CHEM=Benzo(g,h,i)perylene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
241379.3 ** 241.4 1 IH-1-06 TOX 1.4 TX 68 NT 0. NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=420 CHEM=Benzo(b,k)fluoranthene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONG EFFECT RATIO SITE SAMPLE C
GL-SECs NOT REPORTED
0.1 5 WH-1-02
8 CF-1-06
7 MR-1-25
0.7 7 MR-1-07
8 CF-1-04
6 UM-l-RE
0.9 7 MR-1-17
1.1 7 MR-1-11
1.0 8 CF-1-03
ERL-15% EFFECT
8 CF-l-CO
8 CF-1-05
7 MR-l-CO
TEL-SR(ERL*NERM)
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
6 UM-1-01
1.7 8 CF-1-01
8 CF-1-02
ERM-50% EFFECT
5 WH-l-CO
6 UM-l-CO
2.0 7 MR-1-02
NERM-50% NO EFFECT
5 WH-l-RE
9 TR-1-02
11 TB-1-04
1.0 11 TB-1-03
1.0 11 TB-1-02
11 TB-l-RE
9 TR-1-01
PEL-SR(ERM*NERH)
10 MB-l-RE
10 MB-1-02
6 UM-1-03
6 UM-1-02
NERH-85% NO EFFECT
6.4 7 MR-1-19
2.6 11 TB-1-01
10 MB-1-03
9.8 5 WH-1-01
10 MB-1-04
10 MB-1-01
9 TR-1-03
9 TR-1-04
NEC-MAX NO EFFECT
45
245.6
298.5
625.0
833.3
838.7
1000.0
1052.6
1370.4
1428.6
1428.6
1666.7
1666.7
1818.2
1889.8
2000.0
2000.0
2000.0
2000.0
2000.0
2000.0
2279.1
2289.9
2352.9
2394.9
2500.0
2500.0
2500.0
2500.0
2588.2
3333.3
3636.4
3636.4
3636.4
4000.0
4200.0
4206.6
5000.0
5000.0
7227.3
7388.9
7388.9
7846.2
10000.0
11666.7
24864.9
25000.0
44444.4
130000.0
192500.0
192500.0
NC
NE
NE
NC
NE
NE
NC
SG
SG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
NE
*
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
**
*
NE
* *
NE
NE
NE
NE
JU l_ UUI
roxic
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
El St£UJ.Ulti
SURV
36.5
120.3
109.3
91.9
128.4
86.5
115.1
90.7
123.0
100.0
114.9
100.0
100.0
100.0
100.0
108.1
100.0
100.0
119.3
64.9
102.7
100.0
100.0
109.3
109.5
100.0
93.2
52.3
11.4
100.0
81.4
100.0
97.0
114.9
117.9
114.0
0.0
95.5
71.7
95.5
75.8
98.6
82.9
nit -
TOXS
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
t-oi^a.
GROW
74
10
95
91
10
ND
92
58
82
10
98
10
ND
10
10
79
10
10
ND
73
94
10
ND
92
11
ND
10
97
72
10
ND
ND
ND
ND
ND
89
ND
ND
91
ND
ND
ND
ND
1 UJNXX
TOXG
TX
NT
NT
TX
NT
ND
TX
TX
TX
NT
NT
NT
ND
NT
NT
TX
NT
NT
ND
TX
NT
NT
ND
TX
NT
ND
NT
NT
TX
NT
ND
ND
ND
ND
ND
TX
ND
ND
NT
ND
ND
ND
ND
s-ng/g
MATURE
ND
90
12
31
80
ND
65
24
93
10
77
10
ND
10
10
68
10
10
ND
25
48
ND
ND
95
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
63
ND
ND
ND
ND
ND
ND
ND
r
1 TOXM
ND
NT
NT
TX
NT
ND
NT
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
ND
TX
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=421 CHEM=Acenaphthylene TEST=HA28 SAMPTYP=bottom sediment - total 0NITS=ng/g
GL-SECs NOT REPORTED
0.3 8 CF-1-01
8 CF-1-06
6 UM-1-01
7 MR-1-25
0.5 5 WH-1-02
8 CF-1-04
5 WH-l-RE
0.6 7 MR-1-11
0.7 7 MR-1-07
6 DM-l-RE
0.9 7 MR-1-17
8 CF-1-02
1.3 8 CF-1-03
ERL-15% EFFECT
6 UM-1-03
1.3 7 MR-1-19
8 CF-l-CO
8 CF-1-05
TEL-SR(ERL*NERM)
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
ERM-50% EFFECT
6 UM-1-02
10 MB-1-03
2.0 7 MR-1-02
10 MB-l-RE
2.0 5 WH-1-01
10 MB-1-02
10 MB-1-04
9 TR-1-01
10 MB-1-01
PEL-SR(ERM*NERH)
9 TR-1-03
9 TR-1-02
4 SR-3-08
4 SR-3-24
NERH-85% NO EFFECT
4 SR-3-16
9 TR-1-04
4 SR-3-05
4 SR-3-02
4 SR-3-01
4 SR-3-06
NEC-MAX NO EFFECT
46
CONC I
144.9
149.3
162.8
312.5
315.8
322.6
323.5
370.4
416.7
500.0
526.3
588.2
714.3
714.3
727.3
769.2
833.3
833.3
845.2
909.1
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1000.0
1055.6
1066.7
1250.0
1250.0
1324.3
1500.0
1750.0
2000.0
2000.0
2755.1
3333.3
3333.3
6944.4
7250.0
7590.5
7931.0
8500.0
14285.7
19230.8
27000.0
80000.0
K4-L. V
!FFEC
NC
NE
NE
NE
NC
NE
NE
NC
NC
NE
NC
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
*
NE
*
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
>m sec
'OXIC
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
iimen
su:
64
120
119
109
36
128
109
90
91
86
115
102
123
114
114
100
114
100
100
100
100
100
100
108
100
100
117
95
109
100
71
97
95
81
75
98
100
88
102
96
82
96
103
97
100
c -
RV
.9
.3
.3
.3
.5
.4
.5
.7
.9
.5
.1
.7
.0
.9
.0
.0
.9
.0
.0
.0
.0
.0
.0
.1
.0
.0
.9
.5
.3
.0
.7
.0
.5
.4
.8
.6
.0
.3
.6
.1
.9
.1
.8
.4
.0
tot;
TOXS
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ax urj-
GROW
73
10
ND
95
74
10
11
58
91
ND
92
94
82
ND
89
10
98
10
10
ND
ND
10
10
79
10
10
ND
ND
92
ND
91
ND
ND
ND
ND
ND
ND
92
10
10
ND
94
10
94
92
Lis-ng
TOXG :
TX
NT
ND
NT
TX
NT
NT
TX
TX
ND
TX
NT
TX
ND
TX
NT
NT
NT
NT
ND
ND
NT
NT
TX
NT
NT
ND
ND
TX
ND
NT
ND
ND
ND
ND
ND
ND
NT
NT
NT
ND
NT
NT
NT
NT
/g
MATURE
25
90
ND
12
ND
80
ND
24
31
ND
65
48
93
ND
63
10
77
10
ND
ND
ND
10
10
68
10
10
ND
ND
95
ND
ND
ND
ND
ND
ND
ND
ND
95
10
95
ND
11
10
11
96
TOXM
TX
NT
ND
NT
ND
NT
ND
TX
TX
ND
NT
NT
NT
ND
NT
NT
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
ND
NT
NT
NT
NT
80000.0
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=422 CHEM=Dibenz(a,h)anthracene TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
GL-SECs NOT REPORTED
11 TB-l-RE
6 UM-1-01
8 CF-1-06
0.3 5 WH-1-02
0.5 8 CF-1-01
7 MR-1-25
8 CF-1-04
5 WH-l-RE
0.6 7 MR-1-11
0.7 7 MR-1-07
6 OM-l-RE
0.9 7 MR-1-17
8 CF-1-02
1.3 8 CF-1-03
1.3 7 MR-1-19
ERL-15% EFFECT
8 CF-l-CO
8 CF-1-05
TEL-SR(ERL*NERM)
11 TB-1-04
2.0 11 TB-1-02
7 MR-l-CO
5 WH-l-CO
6 UM-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.6 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
6 UM-1-03
ERM-50% EFFECT
6 UM-1-02
2.0 7 MR-1-02
4.0 11 TB-1-03
PEL-SR(ERM*NERH)
9 TR-1-01
10 MB-1-03
3.6 5 WH-1-01
10 MB-1-04
9 TR-1-02
10 MB-1-02
NERH-85% NO EFFECT
11.0 11 TB-1-01
10 MB-l-RE
10 MB-1-01
9 TR-1-03
9 TR-1-04
NEC-MAX NO EFFECT
47
2
46
149
210
260
312
322
352
370
416
500
526
588
714
769
769
833
833
877
909
909
909
1000
1000
1000
1000
1000
1000
1000
1000
1000
1045
1125
1222
1250
1818
1936
2000
2066
2405
2500
3333
3333
3333
5000
5375
9666
17666
23250
23250
.0
.5
.3
.5
.9
.5
.6
.9
.4
.7
.0
.3
.2
.3
.2
.2
.3
.3
.1
.1
.1
.1
.0
.0
.0
.0
.0
.0
.0
.0
.0
.5
.0
.2
.0
.2
.5
.0
.7
.4
.0
.3
.3
.3
.0
.0
.7
.7
.0
.0
NE
NE
NE
NC
NC
NE
NE
NE
NC
NC
NE
NC
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
*
*
NE
NE
*
NE
NE
NE
* *
NE
NE
NE
NE
)uuuiu a*su.LULeii
'OXIC SURV
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
100
119
120
36
64
109
128
109
90
91
86
115
102
123
114
100
114
93
11
100
100
100
100
100
100
108
100
100
114
117
109
52
81
95
71
95
100
97
0
100
75
98
82
.0
.3
.3
.5
.9
.3
.4
.5
.7
.9
.5
.1
.7
.0
.0
.0
.9
.2
.4
.0
.0
.0
.0
.0
.0
.1
.0
.0
.9
.9
.3
.3
.4
.5
.7
.5
.0
.0
.0
.0
.8
.6
.9
L ~ I
TOXS
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
.UL.C1J.
GROW
10
ND
10
74
73
95
10
11
58
91
ND
92
94
82
89
10
98
10
72
10
10
ND
ND
10
10
79
10
10
ND
ND
92
97
ND
ND
91
ND
ND
ND
ND
ND
ND
ND
ND
UIMJ. io=ny / y
TOXG MATURE
NT
ND
NT
TX
TX
NT
NT
NT
TX
TX
ND
TX
NT
TX
TX
NT
NT
NT
TX
NT
NT
ND
ND
NT
NT
TX
NT
NT
ND
ND
TX
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
90
ND
25
12
80
ND
24
31
ND
65
48
93
63
10
77
ND
ND
10
ND
ND
ND
10
10
68
10
10
ND
ND
95
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
NT
ND
TX
NT
NT
ND
TX
TX
ND
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
j
COi
2567
7343
8483
9500
11578
12214
13333
13666
14407
15181
15449
15941
16000
16000
16000
16000
16600
16600
17100
20911
22500
22754
31375
52995
62076
105200
169190
169190
169190
171981
172413
174818
177222
229675
231000
250818
257352
387142
387142
410769
411529
502025
519000
519000
581265
651000
651000
651000
950561
1056071
1360000
1360000
1360000
1410389
2190517
6000352
LNUni
NC I
.2
.8
.9
.0
.9
.3
.3
.7
.4
.8
.3
.2
.0
.0
.0
.0
.0
.0
.0
.8
.0
.4
.0
.9
.9
.0
.5
.5
.5
.2
.8
.0
.2
.7
.0
.2
.9
.9
.9
.2
.4
.9
.0
.0
.0
.0
.0
.0
.8
.4
.0
.0
.0
.6
.2
.3
-uur,-
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
NE
NE
* *
NE
NE
NC
NE
NE
SG
NE
SG
NE
* *
NE
* *
**
* *
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 j **>4
NUMCODE=450 CHEM=PAH-T TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
7 MR-1-25
8 CF-1-04
7 MR-1-07
7 MR-1-17
8 CF-1-03
8 CF-l-CO
8 CF-1-05
0.7 7 MR-1-11
7 MR-l-CO
8 CF-1-01
8 CF-1-02
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
7 MR-1-01
NERM-50% NO EFFECT
5 WH-l-CO
5 WH-l-RE
3 SR-1-10
1.2 5 WH-1-02
7 MR-1-02
TEL-SR(ERL*NERM)
7 MR-1-19
3 SR-1-03
3.5 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
12.1 5 WH-1-01
4 SR-3-24
2 BR-1-09
0.6 2 BR-1-08
4 SR-3-05
NERH-85% NO EFFECT
4 SR-3-02
1.0 2 BR-1-07
PEL-SR(ERM*NERH)
4 SR-3-01
GL-NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
1.6 2 BR-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
2 BR-1-01
66.0 1 IH-1-04
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
88.1 1 IH-1-03
136.9 1 IH-1-06
375.0 1 IH-1-07
48
iimeiit. - LULCL
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
107
138
109
116
122
84
100
96
70
100
95
79
100
100
100
100
117
100
85
90
51
113
111
104
18
102
95
8
102
105
38
104
100
47
.4
.8
.9
.4
.4
.0
.0
.3
.2
.0
.1
.0
.0
.0
.0
.0
.9
.0
.7
.3
.4
.4
.9
.5
.7
.7
.1
.6
.2
.0
.0
.9
.6
.9
J. U1NJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
TX
LlO=Ut
GROW
11
11
11
11
12
10
10
11
75
10
13
11
10
10
10
10
11
ND
ND
10
ND
11
10
10
52
12
11
ND
11
10
97
11
12
10
I'M ~-
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
NT
NT
NT
TX
NT
NT
ND
NT
NT
NT
NT
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
96.7 NT
62.8 NT
67.8 NT
2.0 TX
103.3 NT
2.7 TX
0.0 TX
0.0 TX
10
87
10
ND
11
ND
ND
ND
NT
TX
NT
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
;oxic SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
100
100
100
100
100
100
100
101
40
100
100
.0
.0
.0
.0
.0
.0
.0
.6
.0
.0
.0
-1- Ul> .
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
L J. & — ii\
GROW
ND
10
10
10
10
10
14
10
11
ND
ND
i/a
TOXG
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
MATURE TOXM
ND
10
10
10
10
ND
ND
33
ND
ND
ND
ND
NT
NT
NT
NT
ND
ND
NT
ND
ND
ND
NOT
TOX
115.6 NT
12.5 TX
95
87
NT
NT
APPENDIX 4b: ASCENDING *V.TA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no e. .ct | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
;=450 CHEM=PAH-T TEST=HA14 SAMPTYP=bottom sediment - total ONITS=ng/g
RATIO SITE SAMPLE CEN
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
5 WH-l-CO
5 WH-l-RE
3 SR-1-10
1.2 5 WH-1-02
9 TR-1-01
9 TR-1-02
NERM-50% NO EFFECT
3 SR-1-03
GL-NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
GL-TEL-SR(ERL'NERM)
3.5 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-16
4 SR-3-08
12.1 5 WH-1-01
4 SR-3-24
15 7 2 BR-1-09
l£.l 2 BR-1-08
0.9 4 SR-3-05
4 SR-3-02
GL-NERH-85% NO EFFECT
25.7 2 BR-1-07
GL-PEL-SR(ERM*NERH)
4 SR-3-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
PEL-SR(ERM*NERH)
NERH-85% NO EFFECT
40.7 2 BR-1-03
9 TR-1-03
59.4 2 BR-1-01
9 TR-1-04
66.0 1 IH-1-04
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
88.1 1 IH-1-03
136.9 1 IH-1-06
375.0 1 IH-1-07
49
INUm-UUC,;
CONC EFFEl
16000
16000
16000
16000
16000
17100
20911
22500
22754
47600
56333
80766
105200
105200
116897
133412
169190
169190
169190
172413
177222
229675
231000
250818
257352
387142
410769
410769
411529
467147
519000
531264
531264
568416
608166
651000
697333
950561
1012750
1056071
1360000
1360000
1360000
1410389
2190517
.0
.0
.0
.0
.0
.0
.8
.0
.4
.0
.3
.7
.0
.0
.2
.3
.5
.5
.5
.8
.2
.7
.0
.2
.9
.9
.2
.2
.4
.9
.0
.7
.7
.6
.7
.0
.3
.8
.0
.4
.0
.0
.0
.6
.2
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
*
NE
NE
it *
NE
* *
* *
NC
NE
**
NE
**
NE
**
NE
* *
NE
**
**
23
0.
NT
NT
6000352.3
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
111
110
35
113
83
113
104
105
86
116
77
87
100
93
0
111
1
1
0
.8
.4
.0
.3
.4
.7
.5
.9
.4
.2
.3
.5
.0
.4
.0
.8
.4
.4
.0
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
TX
10
10
" 13
10
90
85
94
10
85
10
85
ND
85
ND
ND
94
96
68
ND
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
ND
TX
ND
ND
NT
NT
NT
ND
16
61
ND
14
0.
22
22
51
0.
12
68
ND
0.
ND
ND
74
0.
0.
ND
NT
NT
ND
NT
TX
TX
TX
NT
TX
NT
NT
ND
TX
ND
ND
NT
NT
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TC -L ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | * ^4
NUMCODE=450 CHEM=PAH-T TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
11 TB-l-RE
7 MR-1-25
8 CF-1-04
0.8 7 MR-1-07
6 UM-1-01
1.0 7 MR-1-17
1.1 8 CF-1-03
8 CF-l-CO
6 UM-l-RE
8 CF-1-05
1.3 7 MR-1-11
7 MR-l-CO
1.4 8 CF-1-01
ERL-15% EFFECT
8 CF-1-02
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
1.5 7 MR-1-01
5 WH-l-CO
6 UM-l-CO
TEL-SR(ERL*NERM)
5 WH-l-RE
1.4 11 TB-1-03
1.4 3 SR-1-10
1.2 5 WH-1-02
GL-ERL-15% EFFECT
11 TB-1-04
NERM-50% NO EFFECT
2.8 7 MR-1-02
10 MB-l-RE
2.3 11 TB-1-02
6 UM-1-02
6 DM-1-03
9 TR-1-01
10 MB-1-02
10 MB-1-03
9 TR-1-02
5.5 7 MR-1-19
GL-TEL-SR (ERL*NERM)
6.6 3 SR-1-03
ERM-50% EFFECT
10.6 3 SR-1-06
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
10 MB-1-04
PEL-SR(ERM'NERH)
13.7 11 TB-1-01
12.1 5 WH-1-01
4 SR-3-24
1.8 2 BR-1-09
2 BR-1-08
4 SR-3-05
4 SR-3-02
NERH-85% NO EFFECT
GL-NERH-85% NO EFFECT
GL-PEL-SR(ERM*NERH)
3.0 2 BR-1-07
GL-ERM-50% EFFECT
4 SR-3-01
4.8 2 BR-1-03
10 MB-1-01
9 TR-1-03
7.0 2 BR-1-01
9 TR-1-04
66.0 1 IH-1-04
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
88.1 1 IH-1-03
136.9 1 IH-1-06
50
CONC I
2567.2
4022.0
7343.8
8483.9
9500.0
10465.1
11578.9
12214.3
13333.3
13357.1
13666.7
14407.4
15181.8
15449.3
15449.3
15941.2
16000.0
16000.0
16000.0
16000.0
16000.0
16600.0
17100.0
17100.0
20866.0
20911.8
21818.2
22500.0
22754.4
22754.4
28181.8
28181.8
31375.0
35987.5
37272.7
38277.8
43545.5
47600.0
48000.0
51166.7
56333.3
62076.9
63070.4
105200.0
105200.0
169190.5
172413.8
174818.0
177222.2
179950.0
207877.2
220000.0
229675.7
231000.0
250818.2
257352.9
387142.9
410769.2
410769.2
410769.2
411149.1
411529.4
411529.4
519000.0
651000.0
691333.3
697333.3
950561.8
1012750.0
1056071.4
1360000.0
1360000.0
1360000.0
1410389.6
2190517.2
..Wi-TCi-
5FFEC
NE
NE
NE
NE
NC
NE
SG
SG
NE
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
SG
SG
NE
*
NE
*
NE
NE
NE
NE
NE
NE
**
* *
**
NE
NE
NE
* *
* *
NE
SG
NE
NE
NE
*
NE
**
NE
NE
* *
NE
* *
NE
* *
* *
ixiiieii L. L.U ua
'OXIC SURV
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
120.
100.
109.
128.
91.
119.
115.
123.
100.
86.
114.
90.
100.
64.
102.
100.
100.
100.
100.
100.
108.
100.
100.
109.
52.
100.
36.
93.
109.
100.
11.
117.
114.
81.
97.
95.
100.
114.
96.
10.
96.
88.
95.
0.
71.
102.
88.
97.
96.
103.
80.
97.
79.
75.
98.
89.
82.
0.
100.
1.
1.
3
0
3
4
9
3
1
0
0
5
9
7
0
9
7
0
0
0
0
0
1
0
0
5
3
0
5
2
3
0
4
9
9
4
0
5
0
0
2
3
1
3
5
0
7
6
2
4
1
8
3
4
0
8
6
5
9
0
0
4
4
.X U1N J
TOXS
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
TX
NT
TX
TX
L 1 .3 — lit
GROW
10
10
95
10
91
ND
92
82
10
ND
98
58
10
73
94
ND
10
10
10
10
79
10
ND
11
97
97
74
10
92
ND
72
ND
ND
ND
ND
ND
ND
89
91
60
10
92
ND
ND
91
10
92
10
94
10
85
94
85
ND
ND
96
ND
ND
92
96
68
J/U
TOXG
NT
NT
NT
NT
TX
ND
TX
TX
NT
ND
NT
TX
NT
TX
NT
ND
NT
NT
NT
NT
TX
NT
ND
NT
NT
TX
TX
NT
TX
ND
TX
ND
ND
ND
ND
ND
ND
TX
TX
TX
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
TX
NT
TX
ND
ND
NT
ND
ND
NT
NT
NT
MATURE
90
ND
12
80
31
ND
65
93
10
ND
77
24
10
25
48
ND
10
10
10
10
68
ND
ND
ND
ND
10
ND
ND
95
ND
ND
ND
ND
ND
ND
ND
ND
63
10
37
95
95
ND
ND
ND
10
10
10
11
10
10
11
10
ND
ND
10
ND
ND
96
0.
0.
TOXM
NT
ND
NT
NT
TX
ND
NT
NT
NT
ND
NT
TX
NT
TX
NT
ND
NT
NT
NT
NT
NT
ND
ND
ND
ND
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
TX
NT
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
ND
ND
NT
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 51
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=450 CHEM=PAH-T TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
6000352.3 ** 375.0 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=451 CHEM=PAH-L TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
8 CF-1-04
7 MR-1-25
8 CF-1-01
7 MR-1-07
7 MR-1-17
8 CF-1-02
8 CF-1-03
8 CF-l-CO
0.8 7 MR-1-11
8 CF-1-05
5 WH-l-RE
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
7 MR-l-CO
NERM-50% NO EFFECT
3 SR-1-10
5 WH-l-CO
7 MR-1-01
7 MR-1-19
7 MR-1-02
TEL-SR(ERL*NERM)
2.3 5 WH-1-02
3 SR-1-03
3.1 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
2 BR-1-09
GL-TEL-SR(ERL*NERM)
0.3 2 BR-1-08
GL-NERM-50% NO EFFECT
4 SR-3-08
4 SR-3-16
4 SR-3-24
0.6 2 BR-1-07
NERH-85% NO EFFECT
14.9 5 WH-1-01
PEL-SR(ERM*NERH)
4 SR-3-05
4 SR-3-02
1.3 2 BR-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
32.9 1 IH-1-04
GL-PEL-SR(ERM*NERH)
4 SR-3-01
GL-NERH-85% NO EFFECT
50.6 1 IH-1-03
51.9 1 IH-1-06
2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
534.1 1 IH-1-07
52
ixuriv.
CONC I
895.5
2129.0
2625.0
2782.6
3125.0
4210.5
4294.1
4500.0
5000.0
5074.1
5333.3
5617.6
6000.0
6000.0
6000.0
6000.0
6090.9
6095.5
6100.0
6600.0
6600.0
9769.2
10000.0
13767.3
14228.1
17866.7
31095.2
31095.2
31095.2
37181.8
37917.0
46235.3
46235.3
70277.8
74482.8
76000.0
79176.5
79176.5
91054.1
123158.2
151428.6
183076.9
186000.0
191571.4
191571.4
197142.9
229942.9
276000.0
276000.0
303896.1
311206.9
377528.1
640000.0
640000.0
640000.0
3204897.7
.\JLICi-
!FFEC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
*
NE
NC
NE
NE
NE
NC
**
NE
NE
SG
**
NE
**
**
NE
NE
**
limenc
•OXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
: - tota
SURV
107.4
109.9
138.8
95.1
116.4
122.4
79.0
84.0
100.0
70.2
96.3
85.7
100.0
100.0
100.0
100.0
100.0
90.3
100.0
117.9
111.9
113.4
51.4
104.5
18.7
105.0
38.0
95.1
102.7
102.2
47.9
8.6
104.9
100.6
62.8
2.0
96.7
2.7
0.0
67.8
103.3
1 UJN-l
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
.To=nc
GROW
11
11
11
13
11
12
11
10
10
75
11
ND
10
10
10
10
10
10
ND
11
10
11
ND
10
52
10
97
11
12
11
10
ND
11
12
87
ND
10
ND
ND
10
11
j/g -
TOXG :
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
NT
ND
NT
NT
TX
ND
NT
ND
ND
NT
NT
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOX
0.0 TX ND ND
ND
ND
-------
nmeiu
XIXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
: - tote
SURV
100.0
100.0
100.0
100.0
100.0
100.0
101.6
100.0
100.0
40.0
115.6
11 UN.
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
LT5-IK
GROW
14
ND
10
10
10
10
10
10
ND
11
95
3/9 -
TOXG
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
MATURE
ND
ND
10
10
10
10
33
ND
ND
ND
23
TOXM
ND
ND
NT
NT
NT
NT
NT
ND
ND
ND
NT
NOT
TOX
100.0 NT ND
12.5 TX
87
ND
NT
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=451 CHEM=PAH-L TEST=HA14 SAMPTYP=bottom sediment -
5 WH-l-RE
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
3 SR-1-10
5 WH-l-CO
9 TR-1-01
2.3 5 WH-1-02
3 SR-1-03
GL-NERM-50% NO EFFECT
NERM-50% NO EFFECT
9 TR-1-02
GL-TEL-SR(ERL*NERM)
TEL-SR (ERL*NERM)
3.1 3 SR-1-06
GL-ERL-15% EFFECT
ERL-15% EFFECT
6.2 2 BR-1-09
7.7 2 BR-1-08
4 SR-3-08
4 SR-3-16
4 SR-3-24
13.2 2 BR-1-07
14.9 5 WH-1-01
9 TR-1-03
GL-ERM-50% EFFECT
ERM-50% EFFECT
0.8 4 SR-3-05
PEL-SR(ERM*NERH)
GL-PEL-SR(ERM'NERH)
9 TR-1-04
NERH-85% NO EFFECT
4 SR-3-02
GL-NERH-85% NO EFFECT
31.0 2 BR-1-03
32.9 1 IH-1-04
4 SR-3-01
50.6 1 IH-1-03
51.9 1 IH-1-06
62.9 2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
534.1 1 IH-1-07
53
CONC EFFE<
5617
6000
6000
6000
6000
6000
6100
6600
12000
14228
17866
17866
18933
20000
23570
24263
31095
31095
31095
37181
46235
70277
74482
76000
79176
91054
96333
138527
138527
151428
157265
159251
174000
178538
183076
183076
186000
197142
276000
303896
311206
377528
640000
640000
640000
3204897
.6
.0
.0
.0
.0
.0
.0
.0
.0
.1
.7
.7
.3
.0
.5
.9
.2
.2
.2
.8
.3
.8
.8
.0
.5
.1
.3
.0
.0
.6
.4
.7
.0
.5
.9
.9
.0
.9
.0
.1
.9
.1
.0
.0
.0
.7
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
*
**
**
NE
NE
NE
* *
**
NE
NC
NE
NE
**
* *
NE
**
**
**
NE
**•
ND
0.
ND
NT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
83.4
113.7
110.4
111.8
113.3
86.4
35.0
87.5
104.5
93.4
105.9
77.3
0.0
116.2
1.4
1.4
100.0
111.8
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
TX
TX
NT
NT
90
85
10
10
10
85
13
ND
94
ND
10
85
ND
10
96
68
85
94
TX
TX
NT
NT
NT
TX
NT
ND
NT
ND
NT
TX
ND
NT
NT
NT
TX
NT
0.
22
61
16
14
0.
ND
ND
22
ND
51
68
ND
12
0.
0.
0.
74
TX
TX
NT
NT
NT
TX
ND
ND
TX
ND
NT
NT
ND
NT
NT
NT
TX
NT
TOX
0.0 TX ND ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
54
— NUMCODE=451 CHEM=PAH-L TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
CONC EFFECT RATIO SITE SAMPLE C
11 TB-l-RE
8 CF-1-06
6 UM-1-01
8 CF-1-04
7 MR-1-25
0.8 8 CF-1-01
0.7 7 MR-1-07
6 UM-l-RE
6 UM-1-02
1.0 7 MR-1-17
10 MB-1-03
8 CF-1-02
1.3 8 CF-1-03
10 MB-l-RE
8 CF-l-CO
1.2 7 MR-1-11
8 CF-1-05
1.7 11 TB-1-03
5 WH-l-RE
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
TEL-SR(ERL*NERM)
7 MR-l-CO
1.0 3 SR-1-10
ERL-15% EFFECT
6 UM-1-03
11 TB-1-04
5 WH-l-CO
6 UM-l-CO
1.5 7 MR-1-01
10 MB-1-02
2.2 7 MR-1-19
2.3 7 MR-1-02
9 TR-1-01
2.3 5 WH-1-02
GL-ERL-15% EFFECT
3.0 3 SR-1-03
9 TR-1-02
6.8 11 TB-1-02
GL-TEL-SR (ERL*NERM)
5.2 3 SR-1-06
ERM-50% EFFECT
10 MB-1-04
1.4 2 BR-1-09
2 BR-1-08
PEL-SR(ERM*NERH)
GL-NERM-50% NO EFFECT
4 SR-3-08
4 SR-3-16
4 SR-3-24
3.0 2 BR-1-07
14.9 5 WH-1-01
GL-ERM-50% EFFECT
9 TR-1-03
NERH-85% NO EFFECT
36.1 11 TB-1-01
GL-PEL-SR(ERM*NERH)
4 SR-3-05
9 TR-1-04
4 SR-3-02
GL-NERH-85% NO EFFECT
7.1 2 BR-1-03
32.9 1 IH-1-04
4 SR-3-01
50.6 1 IH-1-03
51.9 1 IH-1-06
10 MB-1-01
14.5 2 BR-1-01
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
8.0
895.5
1209.3
2129.0
2625.0
2782.6
3125.0
3428.6
4055.6
4210.5
4233.3
4294.1
4500.0
4750.0
5000.0
5074.1
5333.3
5454.5
5617.6
6000.0
6000.0
6000.0
6000.0
6000.0
6000.0
6049.8
6090.9
6100.0
6100.0
6136.4
6363.6
6600.0
6600.0
6600.0
8000.0
9769.2
10000.0
12000.0
14228.1
14228.1
17866.7
20000.0
21818.2
28790.2
31095.2
31095.2
32150.0
37181.8
46235.3
54731.2
58256.5
70277.8
74482.8
76000.0
79176.5
91054.1
91054.1
96333.3
96333.3
115000.0
129112.0
151428.6
174000.0
183076.9
183076.9
186000.0
197142.9
276000.0
303896.1
311206.9
326444.4
377528.1
640000.0
640000.0
640000.0
NE
NE
NE
NE
NE
NC
NC
NE
NE
NC
NE
NE
SG
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
SG
NE
*
*
NE
*
*
NE
**
**
NE
SG
NE
NE
NE
NE
*
**
NE
* *
NE
NE
NE
**
**
NE
**
* *
NE
* *
NE
nment
?OXIC
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX-
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
- tote
SURV
100.0
120.3
119.3
128.4
109.3
64.9
91.9
86.5
117.9
115.1
95.5
102.7
123.0
100.0
100.0
90.7
114.9
52.3
109.5
100.0
100.0
100.0
100.0
100.0
100.0
100.0
114.9
93.2
100.0
100.0
108.1
97.0
114.0
109.3
81.4
36.5
96.2
100.0
11.4
10.3
95.5
88.2
97.4
88.3
96.1
102.6
80.3
71.7
98.6
0.0
96.1
82.9
103.8
79.0
0.0
97.4
1.4
1.4
75.8
89.5
100.0
ij. urjj
TOXS
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
TX
TX
NT
TX
TX
NT
TX
NT
L T&=HC
GROW
10
10
ND
10
95
73
91
ND
ND
92
ND
94
82
ND
10
58
98
97
11
ND
10
10
10
10
10
97
ND
10
10
ND
79
ND
89
92
ND
74
91
ND
72
60
ND
92
10
92
10
10
85
91
ND
ND
94
ND
10
85
ND
94
96
68
ND
96
92
j/g -•
TOXG
NT
NT
ND
NT
NT
TX
TX
ND
ND
TX
ND
NT
TX
ND
NT
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
TX
ND
NT
NT
ND
TX
ND
TX
TX
ND
TX
TX
ND
TX
TX
ND
NT
NT
NT
NT
NT
TX
NT
ND
ND
NT
ND
NT
TX
ND
NT
NT
NT
ND
NT
NT
MATURE
ND
90
ND
80
12
25
31
ND
ND
65
ND
48
93
ND
10
24
77
ND
ND
ND
10
10
10
10
10
10
ND
ND
ND
ND
68
ND
63
95
ND
ND
10
ND
ND
37
ND
10
10
95
95
10
10
ND
ND
ND
11
ND
10
10
ND
11
0.
0.
ND
10
96
TOXM
ND
NT
ND
NT
NT
TX
TX
ND
ND
NT
ND
NT
NT
ND
NT
TX
NT
ND
ND
ND
NT
NT
NT
NT
NT
NT
ND
ND
ND
ND
NT
ND
NT
NT
ND
ND
NT
ND
ND
TX
ND
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
ND
NT
NT
ND
NT
NT
NT
ND
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 55
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=451 CHEM=PAH-L TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
3204897.7 ** 534.1 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=452 CHEM=PAH-H TEST=CR14 SAMPTYP=bottom sediment - total UNITS=ng/g
8 CF-1-06
7 MR-1-25
8 CF-1-04
7 MR-1-07
7 MR-1-17
8 CF-1-03
8 CF-l-CO
8 CF-1-05
0.7 5 WH-1-02
7 MR-l-CO
0.6 7 MR-1-11
4 SR-3-CO
3 SR-l-CO
7 MR-1-01
1 IH-l-CO
2 BR-l-CO
5 WH-l-CO
NERM-50% NO EFFECT
8 CF-1-02
8 CF-1-01
5 WH-l-RE
3 SR-1-10
7 MR-1-02
TEL-SR(ERL*NERM)
7 MR-1-19
3 SR-1-03
4 SR-3-16
GL-NERM-50% NO EFFECT
4 SR-3-08
GL-TEL-SR(ERL*NERM)
3.6 3 SR-1-06
10.7 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-24
0.8 2 BR-1-08
2 BR-1-09
NERH-85% NO EFFECT
4 SR-3-02
4 SR-3-05
4 SR-3-01
GL-NERH-85% NO EFFECT
1.3 2 BR-1-07
PEL-SR(ERM*NERH)
GL-PEL-SR (ERM*NERH)
1.8 2 BR-1-03
2 BR-1-01
GL-ERM-50% EFFECT
ERM-50% EFFECT
4 SR-3-06
NEC-MAX NO EFFECT
GL-NEC-MAX NO EFFECT
85.9 1 IH-1-04
110.6 1 IH-1-03
187.9 1 IH-1-06
279.5 1 IH-1-07
56
CONC I
1671.6
4718.8
6354.8
6375.0
7368.4
7714.3
8333.3
8333.3
8526.3
9090.9
9333.3
10000.0
10000.0
10000.0
10000.0
10000.0
10500.0
11073.5
11647.1
12666.7
15294.1
16400.0
21375.0
39179.5
52307.7
87333.3
97931.0
97931.0
106944.4
116513.3
138095.2
138621.6
138621.6
138621.6
155000.0
211117.6
213636.4
213636.4
227692.3
235714.3
243000.0
243000.0
332352.9
376058.0
401070.2
465000.0
573033.7
661964.3
661964.3
720000.0
720000.0
720000.0
858928.6
1106493.5
1879310.3
2795454.5
.\JLJCt-
SFFEC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
* *
NE
NC
NE
NE
NE
NE
SG
SG
NE
NE
* *
* *
**
* *
nment - toca
'OXIC SURV
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
107
138
109
116
122
84
100
96
51
100
70
100
100
117
100
100
100
79
95
85
90
113
111
104
102
95
18
8
102
38
105
100
104
96
47
62
67
103
2
2
0
0
.4
.8
.9
.4
.4
.0
.0
.3
.4
.0
.2
.0
.0
.9
.0
.0
.0
.0
.1
.7
.3
.4
.9
.5
.7
.1
.7
.6
.2
.0
.0
.6
.9
.7
.9
.8
.8
.3
.0
.7
.0
.0
J. U1MJ
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
TX
TX
.TS-nc
GROW
11
11
11
11
12
10
10
11
ND
10
75
10
10
11
10
10
ND
11
13
ND
10
11
10
10
12
11
52
ND
11
97
10
12
11
10
10
87
10
11
ND
ND
ND
ND
l/g —
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
ND
ND
ND
ND
MATURE
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
TOXM
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (Al ATA) NORMALIZED TO TOTAI ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>«,
NUMCODE=452 CHEM=PAH-H TEST=HA14 SAMPTYP=bottom sediment - total UNITS=
57
CONC I
8526.3
10000.0
10000.0
10000.0
10000.0
10000.0
10500.0
15294.1
16400.0
16400.0
35600.0
35966.7
36333.3
47680.1
70609.9
87333.3
97931.0
106944.4
138095.2
138621.6
138621.6
138621.6
155000.0
211117.6
213636.4
227692.3
227692.3
235714.3
243000.0
301289.8
332352.9
398676.5
398676.5
410172.5
422000.0
465000.0
573033.7
601000.0
720000.0
720000.0
838750.0
838750.0
858928.6
1106493.5
1879310.3
,uua=
2FFEC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
**
NE
**
**
NE
SG
NE
**
* *
**
NE
NE
NE
* *
**
* *
RATIO SITE SAMPLE
CEN
2795454.5
0.7 5 WH-1-02
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
5 WH-l-CO
5 WH-l-RE
3 SR-1-10
GL-NERM-50% NO EFFECT
9 TR-1-01
NERM-50% NO EFFECT
9 TR-1-02
GL-TEL-SR (ERL*NERM)
TEL-SR(ERL*NERM)
3 SR-1-03
4 SR-3-16
4 SR-3-08
3.6 3 SR-1-06
10.7 5 WH-1-01
GL-ERL-15% EFFECT
ERL-15% EFFECT
4 SR-3-24
21.1 2 BR-1-08
21.4 2 BR-1-09
4 SR-3-02
GL-NERH-85% NO EFFECT
1.1 4 SR-3-05
4 SR-3-01
GL-PEL-SR (ERM*NERH)
33.2 2 BR-1-07
GL-ERM-50% EFFECT
ERM-50% EFFECT
PEL-SR(ERM*NERH)
NERH-85% NO EFFECT
46.5 2 BR-1-03
57.3 2 BR-1-01
9 TR-1-03
4 SR-3-06
GL-NEC-MAX NO EFFECT
9 TR-1-04
NEC-MAX NO EFFECT
85.9 1 IH-1-04
110.6 1 IH-1-03
187.9 1 IH-1-06
279.5 1 IH-1-07
to. merit i_ — uu ua
:"OXIC SURV
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
40.
100.
100.
100.
100.
100.
100.
100.
101.
100.
100.
115.
111.
110.
12.
35.
113.
113.
83.
105.
104.
116.
0
0
0
0
0
0
0
0
6
0
0
6
8
4
5
0
3
7
4
9
5
2
-L U1 NT 85 TX
87.5 NT ND ND
111.8 NT 94 NT
93.4 NT ND ND
0.0
1.4
1.4
0.0
TX
TX
TX
TX
ND
96
68
ND
ND
NT
NT
ND
0.
68
0.
ND
74
ND
ND
0.
0.
ND
TX
NT
TX
ND
NT
ND
ND
NT
NT
ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 | **>4
58
nun^
CONC I
1671.6
4014.0
4718.8
6354.8
6375.0
7368.4
7714.3
8333.3
8333.3
8526.3
9090.9
9255.8
9333.3
9928.6
10000.0
10000.0
10000.0
10000.0
10000.0
10000.0
10000.0
10500.0
10500.0
11647.1
12666.7
13622.1
15294.1
15454.5
16363.6
16400.0
18556.1
21375.0
21818.2
31237.5
34222.2
35600.0
36333.3
37409.1
40000.0
46933.3
52307.7
87333.3
87333 .3
92480.5
96166.7
97931.0
97931.0
105000.0
106944.4
138095.2
138621.6
147800.0
149272.0
155000.0
211117.6
213636.4
227692.3
231703.3
235714.3
235714.3
243000.0
306551.4
332352.9
364888.9
398676.5
465000.0
573033.7
601000.0
720000.0
720000.0
838750.0
838750.0
858928.6
1106493.5
1879310.3
SFFEC
NE
NE
NE
NE
NC
SG
SG
NE
NE
NC
NE
NE
SG
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
SG
NE
SG
SG
SG
it
NE
NE
NE
NE
NE
NE
NE
NE
* *
* *
NE
**
NE
* *
* *
NE
NE
NE
SG
NE
NE
NE
*
NE
**
* *
NE
NE
NE
* *
* *
* *
RATIO SITE SAMPLE i
8 CF-1-06
11 TB-l-RE
7 MR-1-25
8 CF-1-04
0.9 7 MR-1-07
1.1 7 MR-1-17
1.1 8 CF-1-03
8 CF-l-CO
8 CF-1-05
0.7 5 WH-1-02
7 MR-l-CO
6 DM-1-01
1.4 7 MR-1-11
6 UM-l-RE
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1.4 7 MR-1-01
1 IH-l-CO
2 BR-l-CO
ERL-15% EFFECT
5 WH-l-CO
6 UM-l-CO
8 CF-1-02
1.7 8 CF-1-01
TEL-SR(ERL*NERM)
5 WH-l-RE
1.2 11 TB-1-02
1.3 11 TB-1-03
1.6 3 SR-1-10
NERM-50% NO EFFECT
3.1 7 MR-1-02
11 TB-1-04
10 MB-l-RE
6 UM-1-02
9 TR-1-01
9 TR-1-02
6 UM-1-03
10 MB-1-02
10 MB-1-03
7.6 7 MR-1-19
8.7 3 SR-1-03
GL-ERL-15% EFFECT
GL-TEL-SR(ERL*NERM)
ERM-50% EFFECT
4 SR-3-16
GL-NERM-50% NO EFFECT
8.1 11 TB-1-01
4 SR-3-08
13.8 3 SR-1-06
10.7 5 WH-1-01
10 MB-1-04
PEL-SR(ERM*NERH)
4 SR-3-24
2 BR-1-08
1.9 2 BR-1-09
4 SR-3-02
NERH-85% NO EFFECT
4 SR-3-05
GL-NERH-85% NO EFFECT
4 SR-3-01
GL-PEL-SR(ERM*NERH)
3.0 2 BR-1-07
10 MB-1-01
GL-ERM-50% EFFECT
4.2 2 BR-1-03
5.2 2 BR-1-01
9 TR-1-03
4 SR-3-06
GL-NEC-MAX NO EFFECT
9 TR-1-04
NEC-MAX NO EFFECT
85.9 1 IH-1-04
110.6 1 IH-1-03
187.9 1 IH-1-06
nmenc
'OXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
. - coca
SURV '
120.3
100.0
109.3
128.4
91.9
115.1
123.0
100.0
114.9
36.5
100.0
119.3
90.7
86.5
100.0
100.0
100.0
108.1
100.0
100.0
100.0
100.0
102.7
64.9
109.5
11.4
52.3
100.0
109.3
93.2
100.0
117.9
81.4
100.0
114.9
97.0
95.5
114.0
96.2
96.1
0.0
88.3
10.3
71.7
95.5
102.6
97.4
88.2
103.8
96.1
97.4
80.3
75.8
79.0
89.5
98.6
100.0
82.9
0.0
1.4
1.4
1 U1M1
TOXS
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT ,
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
TX
TX
TX
.is=nc
GROW
10
10
95
10
91
92
82
10
98
74
10
ND
58
ND
ND
10
10
79
10
10
10
ND
94
73
11
72
97
97
92
10
ND
ND
ND
ND
ND
ND
ND
89
91
10
ND
92
60
91
ND
10
10
92
10
94
94
85
ND
85
96
ND
92
ND
ND
96
68
r/g —
TOXG !
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
NT
ND
TX
ND
ND
NT
NT
TX
NT
NT
NT
ND
NT
TX
NT
TX
NT
TX
TX
NT
ND
ND
ND
ND
ND
ND
ND
TX
TX
NT
ND
NT
TX
NT
ND
NT
NT
NT
NT
NT
NT
TX
ND
TX
NT
ND
NT
ND
ND
NT
NT
MATURE
90
ND
12
80
31
65
93
10
77
ND
10
ND
24
ND
ND
10
10
68
10
10
ND
ND
48
25
ND
ND
ND
10
95
ND
ND
ND
ND
ND
ND
ND
ND
63
10
95
ND
95
37
ND
ND
10
10
10
10
11
11
10
ND
10
10
ND
96
ND
ND
0.
0.
TOXM
NT
ND
NT
NT
TX
NT
NT
NT
NT
ND
NT
ND
TX
ND
ND
NT
NT
NT
NT
NT
ND
ND
NT
TX
ND
ND
ND
NT
NT
ND
ND
ND
ND
ND
ND
ND
ND
NT
NT
NT
ND
NT
TX
ND
ND
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
ND
NT
ND
ND
NT
NT
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON 59
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=452 CHEM=PAH-H TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
(continued)
CONC EFFECT RATIO SITE SAMPLE CEN TOXIC SURV TOXS GROW TOXG MATURE TOXM
2795454.5 ** 279.5 1 IH-1-07 TOX 0.0 TX ND ND ND ND
-------
APPENDIX 4b: ASCENDING DATA TABLES (ALL DATA) NORMALIZED TO TOTAL ORGANIC CARBON
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=508 CHEM=TOTAL PCBS TEST=HA28 SAMPTYP=bottom sediment - total UNITS=ng/g
RATIO SITE SAMPLE CEN
GL-SECs NOT REPORTED
0.3 8 CF-1-01
8 CF-1-06
7 MR-1-25
8 CF-1-04
0.9 7 MR-1-17
8 CF-1-02
1.3 8 CF-1-03
6 UM-l-RE
1.3 7 MR-1-19
ERL-15% EFFECT @
8 CF-l-CO
8 CF-1-05
TEL-SR(ERL*NERM) @
7 MR-l-CO
9 TR-l-CO
4 SR-3-CO
3 SR-l-CO
1 IH-l-CO
2 BR-l-CO
NERM-50% NO EFFECT
1.7 7 MR-1-07
5 WH-l-RE
2.0 7 MR-1-02
6 UM-1-01
5 WH-l-CO
NERH-85% NO EFFECT
6 UM-l-CO
PEL-SR(ERM*NERH)
ERM-50% EFFECT
4.5 7 MR-1-11
6 UM-1-03
6 UM-1-02
NEC-MAX NO EFFECT
7.7 5 WH-1-01
59.8 7 MR-1-01
61.1 5 WH-1-02
60
CONC EFFEC
289
298
625
645
1052
1176
1428
1500
1538
1538
1666
1666
1754
1818
2000
2000
2000
2000
2000
2000
2083
2411
2500
2604
2700
2700
3000
3297
4027
5555
5590
10777
10777
19729
73000
156140
.9
.5
.0
.2
.6
.5
.6
.0
.5
.5
.7
.7
.1
.2
.0
.0
.0
.0
.0
.0
.3
.8
.0
.7
.0
.0
.0
.7
.8
.6
.9
.8
.8
.7
.0
.4
NC
NE
NE
NE
NC
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
NE
NE
NE
* *
NE
NE
**
**
* *
seQ.j.mexit. - t.
miC SURV
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
64
120
109
128
115
102
123
86
114
100
114
100
100
100
100
100
100
91
109
109
119
100
100
90
114
117
71
108
36
.9
.3
.3
.4
.1
.7
.0
.5
.0
.0
.9
.0
.0
.0
.0
.0
.0
.9
.5
.3
.3
.0
.0
.7
.9
.9
.7
.1
.5
OC.d.L
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
U1M J. 1 *
GROW
73
10
95
10
92
94
82
ND
89
10
98
10
ND
10
10
10
10
91
11
92
ND
10
ND
58
ND
ND
91
79
74
>=uy / y
TOXG
TX
NT
NT
NT
TX
NT
TX
ND
TX
NT
NT
NT
ND
NT
NT
NT
NT
TX
NT
TX
ND
NT
ND
TX
ND
ND
NT
TX
TX
MATURE
25
90
12
80
65
48
93
ND
63
10
77
10
ND
10
10
10
10
31
ND
95
ND
ND
ND
24
ND
ND
ND
68
ND
TOXM
TX
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
ND
NT
NT
NT
NT
TX
ND
NT
ND
ND
ND
TX
ND
ND
ND
NT
ND
-------
Appendix 5 Other published toxicity data grouped by chemical, test type, sample type, toxicity
response, and sediment concentrations normalized to dry weight (in ascending order).
Study Codes: (1) MCGEE: McGee et al. (1994) and Schlekat et al. (1994); (2) DAY:
Day et al. (1995); (3) HOKE: Hoke et al. (1995); (3) JFLD: Field and Cairncross
(1994); and (4) SUPRF: M.D. Sprenger, USEPA, Edison, NJ (unpublished data). Tests:
(1) HA10 to HA28: Hyalella azteca 10- to 28-d test; (2) CR14: Chironomus riparius
14-d test; (3) TT28: Tubifex tubifex 28-d test; and (4) HS28: Hexagenia spp. 28-d test.
See Appendix 2c for a description of the chemical name for each abbreviated
CHEMCODE. The first four pages of this appendix are included on the following
pages of the report. The computer disk that accompanies the report contains the
electronic version of this entire appendix (file name: "apdxS.wp").
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NB no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
CONC
0.
0.
0.
0.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1.
1,
1.
1.
1
1.
1.
1.
1
1
1
1
1
1.
1.
1
1
1
2.
2
2
2
2,
2
2.
2.
2,
2
2,
2.
2.
2
2
2
2
2
2
2
2
2
51
71
73
91
20
20
24
24
24
.24
.24
.44
48
,66
.72
.72
.72
.72
.77
.77
.77
.77
.85
,85
.85
.85
.87
.87
.87
.87
.94
.04
.06
.06
.06
.06
.06
.08
.08
.08
.08
.08
.08
.08
.08
.20
.22
.22
.22
.22
.34
.34
.34
EFFECT
NE
NE
NC
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
RATIO STUDY
SUPRF
JFLD
0 . 3 JFLD
0 . 3 JFLD
JFLD
0 . 2 SUPRF
DAY
DAY
MCGEE
DAY
DAY
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 7 DAY
JFLD
DAY
0 . 8 DAY
DAY
DAY
DAY
SUPRF
DAY
- WUIM^UIJI
TEST
HA10
CT10
CT14
CT14
CT14
HA10
CR14
HA28
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CT14
CR14
HA28
HS28
TT28
CR14
HA10
HA28
^:=j.uj. ^nrii'i^uuci3 iuv^ uwj. ia=pcuL
SAMPLE SAMPTYPE
MAO 5
1111-02-RS15-01
1111-02-RS07-01
1111-02-AS07-01
1111-02-AS12-01
OE04
CM17
CM17
BR7
CM17
CM17
BR5
BR3
BR6
SL04
SL04
SL04
SL04
CW01
CW01
CW01
CW01
CW05
CW05
CMOS
CW05
CM15
CM15
CM15
CM15
BR2
BR1
CW21
CW21
BR4
CW21
CW21
CW06
CW12
CW06
CW12
CW06
CW12
CW12
CW06
1111-02-RS14-01
CW22
CW22
CW22
CW22
CW24
CS04
CW24
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT •
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
SURV
88
85
60
40
92
18
80
94
81
94
40
95
90
91
73
90
96
21
88
89
98
22
86
90
100
26
86
88
94
43
80
90.
84
89
85.
98.
45.
82.
89.
94.
94.
94.
80.
45.
24.
77.
88.
77.
98.
43.
76.
93.
90.
.30
.00
.00
.00
.50
.00
.00
.70
.30
.00
.00
.00
.00
.30
.30
.00
.70
.00
.00
.30
.00
.00
.70
.70
.00
.00
.70
.00
.00
.00
.00
.00
.00
.30
.00
.00
.00
.70
.30
70
.70
00
00
00
00
50
00
30
00
00
00
30
70
TOXS
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
GROW
0.18
4.59
3.76
2.73
4.17
4.73
0.46
0.49
3.82
2.03
73.00
4.09
3.99
3.88
0.50
0.59
4.41
109.00
0.38
0.72
6.87
22.00
0.33
0.42
6.17
29.00
0.50
0.54
3.30
102.00
4.12
4.12
0.58
0.74
3.96
9.97
117.00
0.36
0.52
0.53
0.70
5.35
10.12
172.00
22.00
4.34
0.55
0.71
9.11
74.00
0.51
0.50
0.66
TOXG
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
2.34
2.34
2.36
2.40
2.44
2.44
2.44
2.44
2.45
2.45
2.45
2.45
2.52
2.52
2.52
2.52
2.53
2.59
2.59
2.59
2.59
2.63
2.63
2.63
2.63
2.65
2.65
2.65
2.65
2.68
2.69
2.69
2.69
2.69
2.72
2.72
2.72
2.72
2.80
2.90
2.90
2.90
2.90
2.90
2.90
2.93
2.93
2.93
2.93
2.93
2.93
2.93
EFFECT
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NC
NE
SG
NE
NE
SG
NE
NE
NE
NE
NE
NE
SG
NE
RATIO STUDY
DAY
DAY
MCGEE
JFLD
DAY
DAY
DAY
0 . 8 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
0 . 9 DAY
DAY
DAY
DAY
0 . 9 DAY
0 . 5 SUPRF
DAY
1 . 1 JFLD
SUPRF
DAY
1 . 0 DAY
DAY
DAY
DAY
DAY
DAY
DAY
1 . 0 DAY
DAY
it \jrt\,\juci
TEST
HS28
TT28
HA28
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
CT14
HA10
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
— O.UA *_(iunv, vyi^ij— AV^
(continued)
SAMPLE
CW24
CW24
CON2
1111-02-RS13-01
CW23
CW23
CW23
CW23
CW14
CW14
CW14
CW14
CW15
CW15
CW15
CW15
BR9
CW13
CW13
CW13
CW13
CW18
CW18
CW18
CW18
CW09
CW09
CW09
CW09
BR8
SL07
SL07
SL07
SL07
CMOS
CMOS
CMOS
CMOS
OE21
VS01
1111-02-AS09-01
MAO 6
VS01
VS01
VS01
CW17
VS03
CW17
VS03
CW17
VS03
CW17
:nc
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
SURV
98.00
42.00
88.70
72.50
96.00
90.70
100.00
39.00
86.70
84.00
100.00
46.00
85.30
82.70
100.00
43.00
90.00
76.00
88.00
100.00
44.00
86.70
93.30
98.00
47.00
85.30
84.00
100.00
29.00
93.80
71.10
82.70
98.00
15.00
84.00
86.70
100.00
31.00
0.00
84.00
42.50
81.70
88.00
94.00
26.00
89.30
89.30
86.70
97.30
94.00
90.00
43.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
8.53
62.00
3.70
3.20
0.35
0.71
7.98
43.00
0.61
0.74
10.59
135.00
0.49
0.76
10.94
126.00
3.94
0.51
0.66
10.93
126.00
0.66
0.82
11.15
147.00
0.40
0.50
4.56
56.00
3.88
0.41
0.95
5.98
152.00
0.36
0.50
5.16
37.00
0.43
3.03
0.16
0.61
0.19
30.00
0.64
0.33
0.87
0.42
10.40
0.01
154.00
TOXG
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NR
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NB no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
lMurn-uurj=xu i \-ncin^*juci= HJL.
(continued)
CONC
2.
2.
3.
3.
3.
3.
3.
3.
3.
3.
3.
3.
3.
3.
3.
3 ,
3
3.
3,
3.
3
3.
3.
3
3
3.
3.
3
3.
3.
3.
3
3
3
3.
3
3.
3.
3.
3.
3.
3.
4.
4.
4.
4.
4
4
4
4
4
4
93
95
05
06
06
06
20
20
25
28
28
28
.28
.33
.33
.33
.33
.40
,40
.40
.40
.40
.40
.40
.48
.48
.48
.48
.50
.50
.50
.50
.50
.55
.63
.63
.63
.63
.81
.81
.81
.81
.30
.40
.40
.40
.40
.45
.45
.45
.45
.50
EFFECT
NC
NE
SG
NE
NE
NE
SG
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
* *
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NC
NE
NE
SG
SG
NE
NE
SG
NE
SG
SG
NE
SG
NE
NE
SG
SG
SG
NE
NE
NE
NE
NC
RATIO STUDY
1 . 0 DAY
JFLD
1 . 1 JFLD
DAY
DAY
DAY
1 . 2 JFLD
SOPRF
JFLD
DAY
DAY
1 . 2 DAY
DAY
DAY
DAY
1 . 2 DAY
DAY
DAY
4 . 8 JFLD
SOPRF
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
1 . 1 DAY
DAY
0 . 6 SUPRF
DAY
DAY
1 . 2 DAY
1 . 3 JFLD
DAY
DAY
1 . 3 DAY
DAY
1 . 3 DAY
1 . 3 DAY
DAY
1 . 3 DAY
JFLD
DAY
1 . 5 DAY
1 . 6 DAY
1 . 5 DAY
DAY
DAY
DAY
DAY
0 . 8 SUPRF
TEST
TT28
CT14
CT14
CR14
HA28
HS28
CT14
HA10
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
CT10
HA10
HA10
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA10
HA28
HS28
TT28
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
SAMPLE
VS03
1111-
1111-
CW16
CW16
CW16
1111-
MA09
1111-
CM09
CMC 9
CM09
CM09
CM11
CM11
CM11
CM11
CM22
1111-
MA07
MA13
CM22
CM22
CM22
CW03
CW03
CW03
CW03
SL02
OE10
SL02
SL02
SL02
1111-
CM07
CM07
CM07
CM07
SL06
SL06
SL06
SL06
1111-
VS07
VS07
VS07
VS07
CMOS
CMOS
CMOS
CMOS
OE02
02-RS11-01
02-RS12-01
02-AS08-01
02-AS06-01
02-AS03-01
02-RS01-01
02-AS05-01
TOC UNITS=pcnt
-iiu — -
1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
SURV
21.00
90.00
52.50
90.70
89.30
100.00
17.50
78.30
82.50
75.30
93.30
90.00
44.00
72.00
96.00
100.00
45.00
82.70
82.50
88.30
71.70
93.30
100.00
37.00
80.00
90.00
100.00
22.00
77.80
16.00
89.30
98.00
16 .00
60.00
82.70
85.60
89.00
31.00
76.00
78 .70
98.00
19.00
75.00
78 .70
0.00
4 .00
24 .00
85.30
93.30
100.00
37.00
3 .00
TOXS
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
GROW
22.00
4.64
1.32
0.65
0.79
10.58
0.72
0.17
4.07
0.46
0.67
3.39
113.00
0.39
0.53
4.15
91.00
0.42
3.78
0.23
0.18
0.87
4.61
150.00
0.43
0.66
5.78
15.00
0.39
3.16
0.69
3.15
147.00
4.44
0.47
0.74
4.58
123.00
0.18
0.58
4.24
131.00
5.06
0.29
0.00
-0.08
7.00
0.42
0.67
5.42
102.00
3.20
TOXG
TX
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NR
NR
TX
TX
NT
NT
NT
NT
TX
-------
CONG
4.79
4.79
4.79
4.79
5.00
5.50
7.00
7.10
7.10
7.30
7.30
7.30
7.30
7.70
8.90
9.10
9.40
9.50
10.00
12.00
14 .00
EFFECT
NE
NE
NE
NE
NE
NC
SG
SG
SG
NE
NE
NE
NE
NE
SG
NE
SG
NE
NE
*
NE
RATIO STUDY
DAY
DAY
DAY
DAY
SUPRF
0 . 9 SUPRF
1 . 2 SUPRF
1 . 2 SUPRF
1 . 2 SUPRF
DAY
DAY
DAY
DAY
SUPRF
1 . 5 SUPRF
SUPRF
1 . 6 SUPRF
SUPRF
SUPRF
2 . 0 SUPRF
SUPRF
- n ijri\^\JL
TEST
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
^ni = -LU_L v_r
(c
SAMPI
CM01
CM01
CM01
CM01
OE27
MAO 4
MA01
MA03
OE23
CM06
CM06
CM06
CM06
OE16
OE24
MA08
OE12
MA11
MA10
OE25
OE14
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=101 CHEMCODE=TOC UNITS=pcnt
(continued)
:nt
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
SURV
84 .00
89.30
96.00
34.00
90.00
76.70
0.00
10.00
0.00
78.90
97.30
100.00
45.00
98.00
13 .00
86.70
10.00
90.00
78.30
0.00
96.00
TOXS
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
GROW
0.31
0.56
5.07
102.00
3.87
0.16
0.40
0.63
6.54
96.00
4.27
3.63
0.14
3.43
0.16
0.14
4.98
TOXG
NT
NT
NT
NT
NT
NT
NR
NR
NR
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NR
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
CONC
0.
5.
6.
9 (
10,
11.
12.
15.
24.
39,
.60
.50
.10
,50
.10
.40
.90
.40
.00
.40
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
- INUFJt-ULIl
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i=s.LU4 V-,
SAMP:
BR7
BR6
CON2
BR3
BR2
BR5
BR9
BR8
BR1
BR4
I/ y
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81
91
88
90.
80.
95
90
93,
90.
85.
.30
.30
.70
.00
.00
.00
.00
.80
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3
3
3
3
4
4
3
3
4
3
.82
.88
.70
.99
.12
.09
.94
.88
.12
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
19.00
20.00
21.00
25.00
28.00
30.00
34.00
34.00
36.00
36.00
37.00
39.00
41.00
41.00
43.00
43.00
45.00
46.00
46.00
48.00
48.00
51.00
53.00
53.00
54.00
54.00
56.00
62.00
66.00
68.00
69.00
EFFECT
NC
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
SG
NE
NE
NE
SG
SG
NE
SG
NE
NE
NE
NE
NE
NE
SG
SG
NE
SG
NE
RATIO STUDY
0 . 5 SUPRF
SUPRF
SUPRF
SUPRF
0 . 7 SUPRF
0 . 8 SUPRF
SUPRF
SUPRF
SUPRF
0 . 9 SUPRF
SUPRF
SUPRF
1 . 1 SUPRF
MCGEE
MCGEE
MCGEE
1 . 2 SUPRF
1 . 2 SUPRF
MCGEE
1 . 3 SUPRF
MCGEE
MCGEE
SUPRF
SUPRF
MCGEE
MCGEE
1 . 5 SUPRF
1 . 6 SUPRF
MCGEE
1 . 8 SUPRF
SUPRF
.HU1T11_VJUG= 0- t
TEST
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA28
HA28
HA28
HA10
HA10
HA28
HA10
HA28
HA28
HA10
HA10
HA28
HA28
HA10
HA10
HA28
HA10
HA10
jj ^ncii*
SAM PI
MAO 4
MA10
MAO 8
MA11
MAO 3
MA01
MAO 7
OE14
MAO 9
OE25
MAO 6
MA13
OE04
BR4
BR1
BR2
OE12
OE24
BR6
OE23
BR8
BR5
OE16
OE27
BR3
BR9
OE02
OE21
BR7
OE10
MAO 5
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=103 CHEMCODE=SOLIDS UNITS=pcnt
icnc --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BS
BT
BS
BS
BT
BT
BS
BS
BT
BT
BS
BT
BT
TOXIC
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
SURV
76.70
78.30
86 .70
90.00
10.00
0.00
88.30
96.00
78.30
0.00
81.70
71.70
18.00
85.00
90.00
80.00
10.00
13.00
91.30
0.00
93.80
95.00
98.00
90.00
90.00
90.00
3.00
0.00
81.30
16.00
88.30
TOXS
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
GROW
0.16
0.14
0.14
0.16
0.23
4.98
0.17
0.16
0.18
4.73
3.96
4.12
4.12
3.43
3.63
3.88
3.88
4.09
4.27
3.87
3.99
3.94
3.20
3.82
3.16
0.18
TOXG
NT
NT
NT
NT
NR
NR
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
TX
TX
NT
NR
NT
NT
NT
NT
NT
NT
TX
NR
NT
TX
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
2.43
3.00
3.00
3.00
3.00
3.51
3.86
4.16
4.77
4.81
6.00
7.02
8.84
10.00
10.00
10.00
10.00
12.00
12.00
12.00
12.00
12.27
13.90
13.90
13.90
13 .90
15.40
16.19
19.00
19.06
19.65
20.00
20.00
20.00
20.00
20.00
20.00
20.92
23.67
23.79
26.00
26.00
26.00
26.00
26.00
26.17
26.30
26.90
27.20
27.38
28.00
28.00
28.30
EFFECT
NC
NE
NE
NE
NE
NC
NC
NC
NC
NC
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
NE
NE
NC
NC
NE
RATIO STUDY
0 . 1 SUPRF
DAY
DAY
DAY
DAY
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 2 SUPRF
0 . 2 SUPRF
0.2 SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 3 SUPRF
DAY
DAY
DAY
0 . 3 DAY
MCGEE
0.4 SUPRF
0 . 5 SUPRF
MCGEE
MCGEE
DAY
SUPRF
SUPRF
DAY
DAY
0 . 4 DAY
MCGEE
MCGEE
MCGEE
DAY
0 . 7 SUPRF
DAY
0 . 5 DAY
DAY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
0 . 8 SUPRF
0 . 8 SUPRF
MCGEE
WUP1I_UU
TEST
HA10
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA28
HA10
HA10
HA28
HA28
CR14
HA10
HA10
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA10
HA28
HS28
TT28
HA28
HA28
HA28
HA28
HA28
HA10
HA10
HA28
E = IU« t_H
SAMP
SD07
CM17
CM17
CM17
CM17
SD05
SD12
SD04
SD14
SD03
MA01
SD02
SD08
CM15
CM15
CM15
CM15
CM22
CM22
CM22
CM22
SD01
SL02
SL02
SL02
SL02
WS2
SD09
OE12
BR8
BR3
CM05
MAO 5
MA11
CMOS
CM05
CMOS
BR5
BR2
CON2
CM07
OE10
CM07
CM07
CM07
BR7
WS1
AR4
TB1
BR1
OE02
OE23
KL2
CHEMCODE-CLAY UNITS=pcnt
Ullt,
yiPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
SURV
55.00
80.00
94.70
94.00
40.00
35.00
33.00
23.00
35.00
43.00
0.00
47.00
0.00
86.70
88.00
94.00
43.00
82.70
93.30
100.00
37.00
12.00
77.80
89.30
98.00
16.00
78.80
0.00
10.00
93.80
90.00
84 .00
88.30
90.00
86.70
100.00
31.00
95.00
80.00
88.70
82.70
16.00
85.60
89.00
31.00
81.30
86 .30
85.00
87.50
90.00
3 .00
0.00
82.50
TOXS
TX
NT
NT
NT
NT
TX
TX
TX
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
GROW
1.86
0.46
0.49
2.03
73.00
1.83
2.07
1.50
1.95
2.11
1.98
0.00
0.50
0.54
3.30
102.00
0.42
0.87
4.61
150.00
2.02
0.39
0.69
3.15
147.00
2.61
0.00
3.43
3.88
3.99
0.36
0.18
0.16
0.50
5.16
37.00
4.09
4.12
3.70
0.47
3.16
0.74
4.58
123.00
3.82
2.58
1.96
2.96
4.12
3.20
2.62
TOXG
NR
NT
NT
NT
NT
NR
NR
NR
NR
NR
NR
NR
NR
NT
NT
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NR
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NR
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG-1 I SG 1-2 I * 2-4 I **>4
CONC
28,
28.
29.
29.
29.
29.
29,
29.
29,
29.
29.
30.
30,
30
30.
30,
30.
30.
30
30.
31.
31,
31.
31.
31.
31,
32.
32.
32.
32.
32.
33.
33.
33.
33.
34.
34,
35.
35.
35.
35.
35.
35.
35.
36.
36.
36.
36,
36
36
37.
37.
.60
.60
.00
.00
00
.00
,00
.00
.00
.00
.00
.00
.30
.30
.30
.30
.40
.40
.40
.40
.00
.00
.00
.00
.00
,00
.00
.10
.67
.70
.89
.00
.00
.80
.80
.30
.30
.00
.00
.38
.50
.50
.50
.50
.20
.30
.30
.30
.30
.90
.00
.00
EFFECT
NE
SG
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NC
NE
NE
NC
NE
NC
NE
NC
NE
NE
NE
NE
NC
NC
NE
SG
SG
SG
NE
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
SG
NE
NE
RATIO STUDY
MCGEE
1 . 0 MCGEE
DAY
DAY
0 . 8 SUPRF
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
0 . 6 DAY
0 . 6 DAY
0 . 7 DAY
DAY
0 . 6 DAY
DAY
SUPRF
0 . 8 SUPRF
DAY
0 . 6 DAY
DAY
0 . 9 SUPRF
MCGEE
MCGEE
MCGEE
MCGEE
0 . 9 SUPRF
0 . 9 SUPRF
MCGEE
1 . 2 MCGEE
1 . 2 MCGEE
1 . 2 MCGEE
SUPRF
0 . 9 SUPRF
MCGEE
DAY
DAY
DAY
0 . 7 DAY
MCGEE
DAY
DAY
DAY
DAY
1 . 3 MCGEE
DAY
SUPRF
wum^uut=
TEST
HA28
HA28
CR14
CR14
HA10
HA28
HA28
HS28
HS28
TT28
TT28
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA10
HA10
HA28
HS28
TT28
HA10
HA28
HA28
HA28
HA28
HA10
HA10
HA28
HA28
HA28
HA28
HA10
HA10
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA10
= -LU1 <-H!
(•
SAMP:
AR5
AR3
CMOl
CM09
OE04
CMOl
CM09
CMOl
CM09
CMOl
CM09
OE27
SL04
SL04
SL04
SL04
SL06
SL06
SL06
SL06
CM11
OE14
MA04
CM11
CM11
CM11
OE24
TB3
BR6
KL3
BR4
OE21
OE25
KL4
AR1
KL5
PR4
OE16
MA03
BR9
CW05
CW05
CW05
CW05
AR2
CW12
CW12
CW12
CW12
KL1
CM06
MA10
CHEMCODE=CLAY UNITS=pcnt
(continued)
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NdT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
SURV
76.
53.
84.
75.
18.
89.
93.
96.
90.
34.
44.
90.
73.
90.
96.
21.
76.
78.
98.
19.
72.
96.
76.
96,
100.
45.
13.
73.
91.
78.
85.
0,
0,
72.
38
61.
25.
98.
10.
90.
86.
90.
100.
26.
77.
89.
94.
80.
45.
61.
78.
78.
30
80
00
30
00
30
.30
.00
.00
.00
.00
.00
.30
.00
,70
,00
.00
,70
.00
,00
,00
.00
.70
,00
,00
,00
.00
.80
.30
.80
.00
,00
,00
.50
.80
,50
.00
,00
.00
.00
,70
,70
00
00
,50
30
70
00
00
.30
90
30
TOXS
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
GROW
2.
2.
0.
0,
4.
0.
0.
5.
3.
102.
113.
3.
0.
0,
4.
109.
0.
0.
4,
131.
0.
4 .
0.
0.
4.
91.
3.
2.
3.
2.
3.
2
1
2,
2.
4.
3.
0.
0.
6.
29.
2.
0.
0.
10.
172.
2.
0.
0.
68
,01
,31
.46
,73
,56
.67
.07
.39
,00
,00
.87
.50
.59
.41
.00
.18
,58
.24
.00
,39
,98
.16
.53
.15
.00
.63
.39
.88
.61
.96
.45
.96
,71
.15
.27
.94
.33
.42
17
.00
.10
52
70
,12
.00
.00
40
14
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NR
NR
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
37.
37.
37.
38.
38.
43.
44.
44.
44.
44.
45.
47.
47.
47.
47.
49
50
50.
50.
50
50
53.
53.
53
53.
62.
62
62
62
66.
66.
66
66
66.
66.
66
66.
69.
69.
69
69,
70.
70.
70.
70.
70.
70
70
70
71
71
71
00
00
00
00
00
20
00
00.
.00
.00
00
.60
.60
.60
.60
.20
.00
,00
.80
.80
.80
.30
.30
.30
.30
,80
.80
.80
.80
.00
.00
.00
.00
.50
.50
.50
.50
.80
.80
.80
.80
.30
.30
.30
.30
.90
.90
.90
.90
.50
.50
.50
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
SG
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
SUPRF
SUPRF
MCGEE
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
1 . 0 DAY
SUPRF
SUPRF
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
1 . 1 DAY
DAY
DAY
DAY
1 . 3 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
1 . 5 DAY
DAY
DAY
DAY
1 . 5 DAY
DAY
DAY
DAY
l1UFl<-\JLlCi-
TEST
HA28
HS28
TT28
HA10
HA10
HA28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA10
HA10
HA10
CR14
HA28
HS28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
= ±u*i v-nj
('
SAMP;
CM06
CM06
CM06
MAO 8
MAI 3
CON1
CMOS
CMOS
CMOS
CMOS
MAO 7
CW06
CW06
CW06
CW06
CS04
MA06
MAO 9
CW16
CW16
CW16
SL07
SL07
SL07
SL07
CW03
CW03
CW03
CW03
CW09
CW09
CW09
CW09
CW15
CW15
CW15
CW15
CW24
CW24
CW24
CW24
CW23
CW23
CW23
CW23
CW01
CW01
CW01
CW01
CW17
CW17
CW17
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=CLAY UNITS=pcnt
(continued)
,111. — -
1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
SURV
97.30
100.00
45.00
86.70
71.70
87.50
85.30
93.30
100.00
37.00
88.30
82.70
94.70
94.00
24.00
93.30
81.70
78.30
90.70
89.30
100.00
71.10
82.70
98.00
15.00
80.00
90.00
100.00
22.00
85.30
84 .00
100.00
29.00
85.30
82.70
100.00
43.00
76.00
90.70
98.00
42.00
96.00
90.70
100.00
39.00
88.00
89.30
98.00
22.00
89.30
86.70
94.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
GROW
0.63
6.54
96.00
0. 14
0.18
2.41
0.42
0.67
5.42
102.00
0.23
0.36
0.53
5.35
22.00
0.50
0.16
0.17
0.65
0.79
10.58
0.41
0.95
5.98
152.00
0.43
0.66
5.78
15.00
0.40
0.50
4.56
56.00
0.49
0.76
10.94
126.00
0.51
0.66
8.53
62.00
0.35
0.71
7.98
43.00
0.38
0.72
6.87
22.00
0.64
0.87
10.40
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
-------
CONC
71.
74.
74.
74.
74.
75.
75.
75.
75
75
75
75
75
76
76
76
76
78
78
78
78
.50
.90
.90
.90
.90
.30
.30
.30
.30
.80
.80
.80
.80
.50
.50
.50
.50
.80
.80
.80
.80
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
1 . 6 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
- iivji'iv^vyud^
TEST
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
;j.u*± v~H£
(<
SAMPI
CW17
CW18
CW18
CW18
CW18
CW14
CW14
CW14
CW14
CW22
CW22
CW22
CW22
CW13
CW13
CW13
CW13
CW21
CW21
CW21
CW21
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=104 CHEMCODE=CLAY UNITS=pcnt
(continued)
:nc
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
43.
86.
93.
98.
47.
86.
84
100
46
88
77
98
43
76
88
100
44
84
89
98
45
00
.70
.30
.00
.00
.70
.00
.00
.00
.00
.30
.00
.00
.00
.00
.00
.00
.00
.30
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
154.
0.
0.
11.
147.
0.
0.
10.
135
0
0
9
74
0
0
10
126
0
0
9
117
00
66
82
15
.00
.61
.74
.59
.00
.55
.71
.11
.00
.51
.66
.93
.00
.58
.74
.97
.00
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
• NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
CONC
0.00
0.00
0.00
0.00
0.20
0.30
0.50
0.50
0.70
1.50
2.00
2.90
3.00
3.00
3.00
3.00
3.00
3.30
3.30
3.30
3.30
4.00
4 .00
4.00
4.00
4.20
4.20
4.20
4.20
4.50
4.50
4.50
4.50
S.OO
5.10
5.10
5.10
5.10
5.17
5.20
5.20
5.20
5.20
5.80
6.00
6.40
6.40
6.40
6.40
7.09
7.60
7.60
7.60
EFFECT
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
0 . 0 MCGEE
MCGEE
MCGEE
SUPRF
MCGEE
DAY
DAY
MCGEE
DAY
DAY
DAY
0 . 1 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
0 . 2 DAY
MCGEE
DAY
DAY
DAY
DAY
0 . 5 MCGEE
SUPRF
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
Hum»-uijrj=
TEST
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
HA28
HA28
HA10
HA28
CR14
HA28
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
HA28
HA10
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
= J.UD v-ni
SAMP]
CM01
CM01
CM01
CM01
KL3
WS2
AR2
AR3
AR5
WS1
MA06
TB1
CMOS
CMOS
KL2
CMOS
CMOS
CW22
CW22
CW22
CW22
CW24
CW24
CW24
CW24
CW18
CW18
CW18
CW18
CW13
CW13
CW13
CW13
MA13
CW23
CW23
CW23
CW23
CON2
CW14
CW14
CW14
CW14
PR4
MA07
CW21
CW21
CW21
CW21
BR4
CW17
CW17
CW17
CHEMCODE=SAND UNITS=pcnt
:uu
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
84
89.
96
34.
78.
78
77
53
76
86
81
87
85
93
82
100
37
68
77
98
43
76
90
98
42
86.
93
98
47,
76
88.
100.
44.
71.
96.
90.
100.
39.
88.
86.
84.
100.
46.
25.
88.
84.
89.
98.
45.
85.
89.
86.
94.
.00
.30
.00
.00
.80
.80
.50
.80
.30
.30
.70
.50
.30
.30
.50
.00
.00
.00
.30
.00
.00
.00
.70
.00
.00
.70
.30
.00
.00
.00
.00
.00
.00
.70
.00
70
.00
.00
70
.70
00
00
00
00
30
00
30
00
00
00
30
70
00
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0
0
S
102
2
2
2
2
2
2
0
2
0
0
2
5
102
0
0
9
74
0
0
8
62
0
0
11
147
0
0
10
126
0
0
0
7
43
3.
0
0
10.
135.
2.
0.
0.
0.
9.
117.
3.
0.
0.
10.
.31
.56
.07
.00
.61
.61
.10
.01
.68
.58
.16
.96
.42
.57
.62
.42
.00
.55
.71
.11
.00
.51
.66
.53
.00
.66
.82
.15
.00
.51
.66
.93
.00
.18
.35
.71
.98
.00
.70
.61
.74
.59
.00
.15
23
,58
.74
,97
,00
,96
,64
.87
.40
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
7.60
7.90
8. 10
8.10
8.10
8. 10
8.50
8.50
8.50
8.50
11.10
11.33
11.40
11.40
11.40
11.40
12.55
12.80
12.90
13.90
14.00
14.00
14.00
14.00
14.00
16.60
18.00
19.38
21.00
21.00
21.30
22.50
22.50
22.50
22.50
22.50
22.50
22.50
22.50
22.80
22.80
22.80
22.80
24.00
24.00
25.38
27.00
27.00
27.00
27.00
28.21
28.90
EFFECT
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NC
NE
SG
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NC
NC
NE
NE
NE
NC
NE
NE
NE
RATIO STUDY
DAY
MCGEE
DAY
DAY
DAY
0 . 3 DAY
DAY
DAY
DAY
DAY
0 . 9 MCGEE
MCGEE
DAY
DAY
DAY
DAY
MCGEE
1 . 0 MCGEE
MCGEE
1 . 1 MCGEE
DAY
DAY
MCGEE
DAY
DAY
MCGEE
0 . 6 SUPRF
MCGEE
SUPRF
SUPRF
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
0 . 9 DAY
0 . 9 DAY
DAY
DAY
DAY
0 . 9 DAY
0 . 9 SUPRF
0 . 9 SUPRF
MCGEE
DAY
DAY
1 . 0 DAY
DAY
MCGEE
DAY
TEST
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
CR14
HA28
HA28
HS28
TT28
HA28
HA10
HA28
HA10
HA10
HA28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
HA28
HS28
TT28
HA10
HA10
HA28
CR14
HA28
HS28
TT28
HA28
CR14
(c
SAMPL
CW17
CON1
CW01
CW01
CW01
CW01
CW15
CW15
CW15
CW15
KL5
BR1
CW09
CW09
CW09
CW09
BR9
KL1
KL4
AR1
CM06
CM06
AR4
CM06
CM06
BR2
OE25
BR8
MA10
OE16
TB3
CW03
CW06
CW03
CW06
CW03
CW06
CW03
CW06
SL07
SL07
SL07
SL07
MA03
OE21
BR6
CM11
CM11
CM11
CM11
BR7
CW16
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=105 CHEMCODE=SAND UNITS=pcnt
(continued)
:nu
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
SURV
43.00
87.50
88.00
89.30
98.00
22.00
85.30
82.70
100.00
43.00
61.50
90.00
85.30
84.00
100.00
29.00
90.00
61.30
72.50
38.80
78.90
97.30
85.00
100.00
45.00
80.00
0.00
93.80
78.30
98.00
73.80
80.00
82.70
90.00
94.70
100.00
94.00
22.00
24.00
71.10
82.70
98.00
15.00
10.00
0.00
91.30
72.00
96.00
100.00
45.00
81.30
90.70
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
GROW
154.00
2.41
0.38
0.72
6.87
22.00
0.49
0.76
10.94
126.00
2.71
4.12
0.40
0.50
4.56
56.00
3.94
2.00
2.45
1.96
0.40
0.63
1.96
6.54
96.00
4.12
3.88
0.14
4.27
2.39
0.43
0.36
0.66
0.53
5.78
5.35
15.00
22.00
0.41
0.95
5.98
152.00
3.88
0.39
0.53
4.15
91.00
3.82
0.65
TOXG
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NR
NR
NT
NT
NT
TX
NT
NT
NT
-------
CONC
28.90
28.90
29.00
30.00
31.00
31.00
31.00
31.00
32.00
34.00
35.00
35.00
35.00
35.00
35.80
36.84
37.00
38.00
39.00
39.00
40.00
41.00
41.00
41.00
41.00
42.01
44.00
44.00
47.00
47.00
47.00
47.00
54.10
54.10
54.10
54.10
55.40
56.00
56.00
56.00
56.00
56.40
56.40
56.40
56.40
62.00
66.00
66.00
66.00
66.00
73.51
74.50
EFFECT
NE
NE
NE
SG
SG
SG
NE
SG
SG
NE
NE
NE
SG
NE
NE
NE
SG
SG
NE
NE
SG
NE
NE
SG
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
*
SG
NE
NE
NE
*
NE
NE
NE
*
NE
NE
NE
NE
NE
*
*
RATIO STUDY
DAY
DAY
SUPRF
1 . 1 SUPRF
1 . 1 DAY
1 . 0 DAY
DAY
1 . 3 DAY
1 . 1 SUPRF
SUPRF
DAY
DAY
1 . 2 DAY
DAY
SUPRF
MCGEE
1 . 3 SUPRF
1 . 3 SUPRF
SUPRF
SUPRF
1 . 4 SUPRF
DAY
DAY
1 . 5 DAY
DAY
MCGEE
SUPRF
1 . 6 SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
2 . 2 DAY
2 . 0 SUPRF
DAY
DAY
DAY
2 . 3 DAY
DAY
DAY
DAY
2 . 3 DAY
SUPRF
DAY
DAY
DAY
DAY
2 . 6 SUPRF
2 . 6 SUPRF
NUMLUL)
TEST
HA28
HS28
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA28
HA10
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
HA28
HA10
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA10
HA10
E=10b CH
(
SAMP
CW16
CW16
MAO 9
OE04
SL06
SL06
SL06
SL06
OE24
MA08
CM09
CM09
CM09
CM09
CS04
BR5
MAO 4
OE10
MA11
OE14
OE02
CM07
CM07
CM07
CM07
BR3
OE27
OE23
CW12
CW12
CW12
CW12
CW05
CW05
CW05
CW05
SD09
CMOS
CMOS
CMOS
CMOS
SL04
SL04
SL04
SL04
MAO 5
CM22
CM22
CM22
CM22
SD02
SD01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 \ * 2-4 | **>4
(continued)
i^nu — •
MPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
SURV
89.30
100.00
78.30
18.00
76.00
78.70
98.00
19.00
13.00
86.70
75.30
93.30
90.00
44.00
93.30
95.00
76 .70
16.00
90.00
96.00
3.00
82.70
85.60
89.00
31.00
90.00
90.00
0.00
89.30
94.70
80.00
45.00
86.70
90.70
100.00
26.00
0.00
84 .00
86.70
100.00
31.00
73.30
90.00
96.70
21.00
88.30
82.70
93.30
100.00
37.00
47.00
12.00
TOXS
NT
NT
NT
TX
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
GROW
0.79
10.58
0.17
4.73
0.18
0.58
4 .24
131.00
3.63
0. 14
0.46
0.67
3.39
113.00
0.50
4.09
0.16
3.16
0.16
4.98
3.20
0.47
0.74
4.58
123.00
3.99
3.87
0.52
0.70
10.12
172.00
0.33
0.42
6.17
29.00
0.00
0.36
0.50
5.16
37.00
0.50
0.59
4 .41
109.00
0.18
0.42
0.87
4.61
150.00
1.98
2.02
TOXG
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
TX
NR
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NR
NR
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
76.
79.
80.
81.
82.
86.
86.
86.
86.
88.
89.
90.
90.
90,
90,
93
93
93
93
94
95
07
00
00
33
51
10
10
10
10
.70
,10
,00
,00
.00
.00
.00
.00
.00
.00
.10
.19
EFFECT
*
*
*
*
*
NE
NE
NE
*
*
*
NE
NE
NE
NE
NE
NE
NE
NE
*
*
RATIO
2.
2.
2.
2.
2.
3.
3.
3,
3
3
7
8
8
9
,9
,5
.2
.2
.3
.4
STUDY
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
DAY
DAY
DAY
DAY
SUPRF
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
SUPRF
H \JPl\*\JUCi =
TEST
HA10
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
HA10
= J.UL> v~.ni
(<
SAMP!
SD12
OE12
MA01
SD08
SD07
SL02
SL02
SL02
SL02
SD05
SD14
CM15
CM15
CM15
CM15
CM17
CM17
CM17
CM17
SD04
SD03
NUMCODE=105 CHEMCODE=SAND UNITS=pcnt
(continued)
:nc
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
SURV
33.
10.
0.
0,
55,
77.
89
98
16
35
35
86
88
94
43
80
94
94
40
23
43
,00
,00
,00
,00
.00
.80
.30
.00
.00
.00
.00
.70
.00
.00
.00
.00
.70
.00
.00
.00
.00
TOXS
TX
TX
TX
TX
TX
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
GROW
2.
3.
0.
1.
0.
0.
3.
147.
1,
1
0
0
3
102
0
0
2
73
1
2
07
43
00
,86
,39
,69
.15
.00
.83
.95
.50
.54
.30
.00
.46
.49
.03
.00
.50
.11
TOXG
NR
TX
NR
NR
NR
NT
NT
NT
NT
NR
NR
NT
NT
NT
NT
NT
NT
NT
NT
NR
NR
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
36
77
87
97
99
114
117
120
122
128
142
152
183
242
.00
.00
.10
.70
.90
.40
.90
.80
.90
.00
.20
.90
.20
.30
EFFECT
NC
NC
NE
NE
NE
NC
NC
SG
NE
NE
SG
NE
SG
NE
RATIO
0.3
0.6
0.8
0.9
1.2
1.0
1.3
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
- NU["]l-UlJt=
TEST
CT14
CT14
CT14
CT14
CT10
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
SAMPLE
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-02-AS07-
-02-RS07-
-02-RS11-
-02-RS14-
.ibK UJNlTS=pcnt --
SAMPTYPE
01
01
01
01
-02-RS15-01
-02-RS01-
-02-RS12-
-02-AS03-
-02-AS06-
-02-AS12-
-02-AS09-
-02-RS13-
-02-AS08-
-02-AS05-
01
01
01
01
01
01
01
01
01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
SURV
40
60
90
77.
85,
60.
52.
82.
82
92.
42.
72.
17.
75.
.00
.00
.00
.50
.00
.00
.50
.50
.50
.50
.50
.50
.50
.00
TOXS
TX
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
TX
NT
GROW
2.73
3.76
4.64
4.34
4.59
4.44
1.32
3.78
4.07
4.17
3.03
3.20
0.72
5.06
TOXG
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
-------
CONC
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
1.75
2.00
6.17
7.00
7.00
7.00
7.00
7.79
9.83
10.40
10.40
10.40
10.40
13.26
13.40
13.40
13.40
13.40
14.00
14.70
14.70
14.70
14.70
14.90
14.90
14.90
14.90
15.00
15.06
16.70
16.70
16.70
16.70
17.00
17.00
17.00
17.00
18.00
19.00
19.00
19.00
19.00
19.46
19.50
EFFECT
NE
NE
NC
NE
NE
NE
NE
NE
NC
NC
NC
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NC
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
RATIO STUDY
DAY
DAY
0 . 0 SUPRF
DAY
DAY
DAY
DAY
DAY
0 . 0 DAY
0 . 1 SUPRF
0 . 1 SUPRF
0 . 2 SUPRF
DAY
DAY
DAY
DAY
0 . 2 SUPRF
0 . 3 SUPRF
DAY
DAY
DAY
0 . 4 DAY
0 . 4 SUPRF
DAY
DAY
DAY
0 . 5 DAY
0 . 4 SUPRF
DAY
DAY
DAY
0 . 5 DAY
DAY
DAY
DAY
DAY
SUPRF
0 . 4 SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 6 DAY
SUPRF
DAY
DAY
DAY
DAY
0 . 6 SUPRF
DAY
n\Jl'l4
NUMCODE=107 CHEMCODE=SILT UNITS=pcnt
nc
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
SURV
86.70
77.80
43.00
88.00
89.30
94.00
98.00
43.00
16.00
23.00
10.00
35.00
80.00
94.70
94.00
40.00
35.00
0.00
86.70
90.70
100.00
26.00
12.00
73.30
90.00
96.70
21.00
0.00
80.00
90.00
100.00
22.00
84.00
89.30
98.00
45.00
93.30
55.00
89.30
94.70
80.00
45.00
84.00
86.70
100.00
31.00
88.30
76.00
88.00
100.00
44.00
47.00
86.70
TOXS
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
GROW
0.50
0.39
2.11
0.54
0.69
3.30
3.15
102.00
147.00
1.50
3.43
1.95
0.46
0.49
2.03
73.00
1.83
0.00
0.33
0.42
6.17
29.00
2.02
0.50
0.59
4.41
109.00
0.43
0.66
5.78
15.00
0.58
0.74
9.97
117.00
0.50
1.86
0.52
0.70
10.12
172.00
0.36
0.50
5.16
37.00
0.18
0.51
0.66
10.93
126.00
1.98
0.61
TOXG
NT
NT
NR
NT
NT
NT
NT
NT
NT
NR
TX
NR
NT
NT
NT
NT
NR
NR
NT
NT
NT
TX
NR
NT
NT
NT
NT
NR
NT
NT
NT
TX
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NR
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
19.50
19.50
19.50
20.07
20.30
20.30
20.30
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
20.90
21.00
22.60
22.60
22.60
22.60
23.00
23.00
23.00
23.00
23.90
23.90
23.90
23.90
24.60
24.60
24.60
24.60
25.10
25.10
25.10
25.10
26.00
26.10
26.10
26.10
26.10
26.20
S~ 26.20
26.20
EFFECT
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
^0.6 SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 9 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 8 DAY
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 9 DAY
DAY
DAY
DAY
0 . 9 DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
i1UI*lV-Ut^Ci =
TEST
HA28
HS28
TT28
HA10
CR14
HA28
HS28
CR14
CR14
CR14
CR14
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
CR14
HA28
HS28
:.LU / *_m
((
SAMP]
CW14
CW14
CW14
SD12
CW16
CW16
CW16
CW01
CW17
CW18
CW22
CW01
CW17
CW18
CW22
CW01
CW17
CW18
CW22
CW17
CW18
CW22
CW01
MAO 9
CW09
CW09
CW09
CW09
CM22
CM22
CM22
CM22
SL07
SL07
SL07
SL07
CW23
CW23
CW23
CW23
CW15
CW15
CW15
CW15
OE27
CW24
CW24
CW24
CW24
CW06
CW06
CW06
107 CHEMCODE=SILT UNITS=pcnt
(continued)
:uu
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
84.
100.
46.
33.
90.
89.
100.
88.
89.
86.
88.
89.
86.
93.
77.
98.
94
98
98.
43
47
43.
22.
78
85
84.
100
29
82
93
100
37.
71
82
98
15
96
90.
100
39.
85.
82
100.
43.
90.
76.
90.
98.
42.
82.
94.
94.
00
.00
00
00
,70
.30
.00
.00
.30
.70
.00
.30
.70
.30
.30
.00
.00
.00
.00
.00
.00
.00
.00
.30
.30
.00
.00
.00
.70
.30
.00
.00
.10
.70
.00
.00
.00
.70
.00
.00
.30
.70
.00
.00
.00
.00
.70
.00
.00
.70
.70
.00
TOXS
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0.
10.
135.
2.
0.
0.
10.
0.
0.
0.
0
0,
0.
0.
0.
6.
10
11
9.
154
147
74.
22.
0
0
0.
4
56
0,
0
4
150.
0
0,
5.
152
0.
0.
7.
43.
0.
0.
10.
126.
3.
0.
0.
8.
62.
0.
0,
5.
74
.59
,00
,07
,65
.79
,58
.38
.64
.66
.55
.72
.87
.82
.71
.87
.40
.15
.11
.00
.00
.00
.00
.17
.40
.50
.56
.00
.42
.87
.61
,00
.41
.95
.98
.00
.35
.71
.98
.00
.49
.76
.94
00
.87
51
66
,53
,00
,36
,53
,35
TOXG
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
26.
28.
28.
28.
30.
31.
31.
31.
31.
32.
32.
32.
32,
32.
32.
36.
36.
38.
38.
38.
38.
38.
41,
41,
41.
41.
42.
42.
42,
42.
42,
42,
43,
44,
45.
46.
48.
48.
49,
49,
49.
49.
49.
49.
50.
52.
53.
53.
53,
53,
53.
54,
20
00
00
,43
00
00
00
00
,00
00
00
.00
,00
.00
,00
,00
.00
.34
.60
,60
.60
.60
.00
.00
,00
,95
.00
.00
.00
.00
,00
.24
.00
.00
.62
.60
.00
.90
.00
.00
00
00
.00
.00
.30
07
00
.00
.00
.00
.40
,30
EFFECT
NC
NE
NC
NC
NE
NE
NE
SG
NE
NE
NC
NC
NE
SG
NE
SG
SG
NE
SG
SG
NE
SG
NE
SG
SG
NE
NE
NE
NE
SG
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
RATIO STUDY
1 . 0 DAY
SUPRF
0 . 8 SUPRF
0 . 8 SUPRF
SUPRF
DAY
DAY
1 . 4 DAY
DAY
DAY
0 . 9 SUPRF
0 . 9 SUPRF
DAY
1 . 4 DAY
DAY
1 . 0 SUPRF
1 . 0 SUPRF
MCGEE
1 . 6 DAY
1 . 6 DAY
DAY
1 . 4 DAY
SUPRF
1 . 2 SUPRF
1 . 2 SUPRF
MCGEE
DAY
SUPRF
DAY
1 . 8 DAY
DAY
MCGEE
1 . 2 SUPRF
SUPRF
MCGEE
MCGEE
SUPRF
MCGEE
DAY
SUPRF
1 . 4 SUPRF
DAY
DAY
DAY
0 . 9 MCGEE
MCGEE
DAY
DAY
DAY
DAY
0 . 9 MCGEE
MCGEE
NUM(_UUh =
TEST
TT28
HA10
HA10
HA10
HA10
CR14
HA28
HS28
TT28
CR14
HA10
HA10
HA28
HS28
TT28
HA10
HA10
HA28
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA28
CR14
HA10
HA28
HS28
TT28
HA28
HA10
HA10
HA28
HA28
HA10
HA28
CR14
HA10
HA10
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
= 107 CHI
0
SAMPi
CW06
MA08
OE23
SD09
OE14
CM07
CM07
CM07
CM07
CM09
MA04
OE02
CM09
CM09
CM09
OE10
OE24
BR3
SL06
SL06
SL06
SL06
MA11
MAO 3
OE04
BR6
CM11
MA10
CM11
CM11
CM11
BR5
OE21
OE16
BR7
TB3
MA06
CON1
CM06
MAO 7
OE25
CM06
CM06
CM06
KL1
BR9
CMOS
CMOS
CMOS
CMOS
AR1
KL4
107 CHEMCODE=SILT UNITS=pcnt
(continued)
;IIL,
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
SURV
24.
86
0
0
96.
82.
85
89
31
75,
76
3
93
90
44
16
13
90
76
78
98
19
90
10
18
91
72
78
96
100
45
95
0
98
81
73
81
87
78
88
0
97
100
45,
61
90.
85.
93,
100
37
38,
72,
.00
.70
.00
.00
.00
.70
.60
.00
.00
.30
.70
.00
.30
.00
.00
.00
.00
.00
.00
.70
.00
.00
.00
.00
.00
.30
.00
.30
.00
.00
.00
.00
.00
.00
.30
.80
.70
.50
.90
.30
.00
.30
.00
.00
.30
.00
.30
.30
.00
.00
.80
.50
TOXS
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
GROW
22
0
0
4
0
0
4
123
0
0
3
0
3
113
3
3
3
0
0
4
131
0
4
3
0
0
0
4
91
4
4
3
2
0
2
0
0
0
6
96
2
3
0
0
5
102
1
2
.00
.14
.00
.98
.47
.74
.58
.00
.46
.16
.20
.67
.39
.00
.16
.63
.99
.18
.58
.24
.00
.16
.73
.88
.39
.14
.53
.15
.00
.09
.27
.82
.39
.16
.41
.40
.23
.63
.54
.00
.00
.94
.42
.67
.42
.00
.96
.45
TOXG
TX
NT
NR
NR
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
TX
TX
NT
TX
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
TX
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC«1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
54.
57.
59,
59.
60.
60.
61.
61.
63.
67.
68.
69.
70.
71.
71.
71.
71.
71.
71.
72.
84.
.60
.00
.20
.73
,00
,02
.11
.29
.20
,10
.80
,90
.90
.00
,00
,00
.00
04
40
,20
20
EFFECT
NC
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
0 . 9 MCGEE
SUPRF
MCGEE
MCGEE
1 . 0 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1 . 2 MCGEE
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
MCGEE
NUMLUUE:
TEST
HA28
HA10
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
=1UV CH
(
SAMP
KL5
MA13
AR4
BR2
PR4
BR4
BR8
BR1
AR2
KL3
KL2
TB1
AR3
CM01
CM01
CM01
CM01
CON2
AR5
WS1
WS2
107 CHEMCODE=SILT UNITS=pcnt
(continued)
,11U
1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
61
71
85
80
25
85
93
90
77
78
82
87
53,
84
89.
96.
34 .
88.
76.
86.
78.
.50
.70
.00
.00
.00
.00
.80
.00
.50
.80
.50
.50
.80
.00
,30
.00
.00
.70
,30
,30
80
TOXS
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
GROW
2
0
1
4
2
3.
3.
4
2.
2,
2.
2.
2,
0.
0.
5.
102.
3.
2.
2.
2.
.71
.18
.96
.12
.15
.96
.88
.12
.10
.61
,62
,96
,01
,31
,56
,07
00
70
68
58
61
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
5.
5.
5.
6.
11.
12.
13.
18.
18.
25.
26
26
27
30
34
50
50
60
40
10
90
.40
.30
.80
.10
.50
.50
.40
.60
.20
EFFECT
NE
NE
NC
NE
NC
NE
NE
NE
NE
SG
NE
SG
SG
NE
NE
RATIO STUDY
MCGEE
MCGEE
0 . 3 MCGEE
MCGEE
0 . 6 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1 . 5 MCGEE
MCGEE
1 . 5 MCGEE
1 . 6 MCGEE
MCGEE
MCGEE
11 ur»\- v-'L/ii -
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
-J.J.U V^l
SAM]
TB3
WS2
KL5
WS1
KL1
TB1
KL2
KL3
AR5
AR1
KL4
AR3
PR4
AR2
AR4
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=110 CHEMCODE=NH3P UNITS=mg/l
I/J. —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
SURV
73 .
78.
61.
86.
61.
87.
82 .
78.
76.
38
72
53
25
77
85
80
80
50
.30
.30
.50
.50
.80
.30
.80
.50
.80
.00
.50
.00
TOXS
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
GROW
2.
2.
2,
2.
2.
2
2
2
2
1
2
2
2
2
1
.39
.61
.71
.58
.00
.96
.62
.61
.68
.96
.45
.01
.15
.10
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
CONC
412,
412.
1540.
1540.
2390,
2390.
3530.
3530.
7920.
9880,
10700,
10700,
11400,
11400.
13100.
13400.
14300.
14300.
14900.
15600.
15900.
16600.
17000.
19000.
19000.
20400.
20700.
20700.
23600.
25600.
25800.
32500.
32600.
50700.
.00
.00
.00
.00
,00
.00
.00
,00
.00
.00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
00
00
00
00
00
00
00
00
EFFECT
NE
NE
NC
NC
NE
NE
NC
NC
NC
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
SG
NE
NE
NE
*
1N
RATIO STUDY
JFLD
JFLD
0 . 3 JFLD
0 . 3 JFLD
JFLD
JFLD
0 . 6 JFLD
0 . 6 JFLD
0 . 4 JFLD
0 . 5 JFLD
MCGEE
MCGEE
JFLD
MCGEE
0 . 6 JFLD
MCGEE
JFLD
JFLD
JFLD
MCGEE
MCGEE
JFLD
0 . 5 JFLD
MCGEE
MCGEE
1 . 0 JFLD
MCGEE
MCGEE
JFLD
1 . 2 JFLD
JFLD
JFLD
JFLD
2 . 4 JFLD
TEST
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
HA28
HA28
CT14
HA28
CT14
HA28
CT15
HA28
CT14
HA28
HA28
CT14
CT10
HA28
HA28
CT14
HA28
HA28
CT14
CT14
CT14
CT14
CT10
CT14
ju LHtiv]i_uuiii=rtijUpaiiMun uwiTb-ug/g -
SAMPLE SAMPTYPE
1117-01-SED-12-01
1117-01-SED-12-01
1117-01-SED-2-01
1117-01-SED-2-01
1117-01-SED-9-01
1117-01-SED-9-01
1117-01-SED-3-01
1117-01-SED-3-01
1111-02-AS07-01
1111-02-AS08-01
BR5
BR7
1111-02-AS06-01
BR3
1111-02-AS09-01
BR6
1117-01-SED-16-01
1117-01-SED-16-01
1111-02-AS12-01
BR2
BR1
1111-02-RS13-01
1111-02-AS03-01
BR4
BR9
1111-02-RS01-01
BR8
CON2
1111-02-AS05-01
1111-02-RS07-01
1111-02-RS14-01
1111-02-RS11-01
1111-02-RS15-01
1111-02-RS12-01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BS
BT
BS
BT
BT
BT
BS
BS
BT
BT
BS
BS
BT
BS
BS
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
SURV
79
94
28
0
64
74
14
0
40
17
95
81
82
90
42
91
84.
80.
92.
80.
90.
72.
82.
85.
90.
60.
93.
88.
75.
60.
77.
90.
85.
52.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.50
.00
.30 •
.50
.00
.50
.30
.00
.00
.50
.00
.00
.50
.50
.00
00
00
80
70
00
00
50
00
00
50
TOXS
NT
NT
TX
TX
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
GROW
2.16
0.18
0.25
2.59
0.10
0.19
2.73
0.72
4.09
3.82
4.07
3.99
3.03
3.88
2.55
0.11
4.17
4.12
4.12
3.20
3.78
3.96
3.94
4.44
3.88
3.70
5.06
3.76
4.34
4.64
4.59
1.32
TOXG
NT
NT
TX
ND
NT
NT
TX
ND
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
1.
1,
1
1,
1.
1.
1.
1.
1,
1,
1.
1.
1,
1,
1,
1,
1.
2,
2
2,
2.
2.
2.
2.
2,
2.
2.
2.
2.
2.
2.
3.
3.
8.
9.
.00
.00
.00
.00
.00
.00
,00
,00
.00
.00
.50
.60
.70
.80
.80
.80
.80
.00
.00
.00
.10
.50
.50
.50
,50
50
.50
.50
,50
,50
,50
00
70
00
30
EFFECT
NC
NC
NC
NC
NC
NC
NC
NC
NC
NC
NE
NE
NE
NE
NC
NC
NC
NE
NE
SG
SG
NE
NE
NE
NG
NG
NG
NG
NG
NG
NG
NE
*
*
**
RATIO
0.
0.
0.
0.
0.
0.
0.
0.
0.
0,
0,
0.
0.
1,
1.
1.
1.
1.
1.
1.
1.
1.
2.
3.
4.
,4
.4
,4
.4
.4
4
4
.4
.4
.4
.9
.9
.9
.0
1
.0
0
0
0
0
0
0
1
2
7
STUDY
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
SUPRF
JFLD
TEST
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
CT14
CT10
HA10
CT14
SAMPLE
SD01
SD02
SD03
SD04
SD05
SD07
SD08
SD09
SD12
SD14
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
OE14
OE16
OE27
OE02
OE04
OE10
OE12
OE21
OE23
OE24
1111
1111
OE25
1111
-02-RS14
-02-AS12
-02-RS11
-02-RS15
-02-AS09
-02-RS01
-02-RS12
-02-AS06
-02-RS13
-02-AS08
LVEK UNITS-ug/g --
SAMPTYPE
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
-02-RS07-01
-02-AS05
-02-AS03
-02-AS07
-01
-01
-01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
SURV
12.
47.
43.
23.
35,
55.
0.
0.
33.
35,
77,
92.
90,
85
42
60,
52,
82
72
17
60,
96.
98,
90.
3
18,
16.
10.
0.
0.
13.
75.
82.
0.
40.
.00
.00
,00
.00
,00
.00
,00
,00
,00
.00
.50
.50
.00
.00
.50
.00
.50
.50
.50
.50
.00
.00
.00
,00
.00
.00
,00
,00
.00
,00
00
00
50
00
00
TOXS
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
TX
NT
NT
NT
TX
TX
TX
TX
TX
TX
TX
NT
NT
TX
TX
GROW
2.
1.
2.
1.
1.
1.
0.
0.
2.
1,
4.
4.
4,
4
3
4.
1.
4
3,
0,
3 .
4.
4.
3,
3,
4.
3.
3.
3.
5.
3.
2.
02
98
11
.50
,83
86
,00
,00
.07
.95
.34
.17
.64
.59
.03
.44
.32
,07
.20
.72
.76
.98
.27
,87
.20
73
,16
.43
63
06
78
,73
TOXG
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
TX
NR
NR
TX
NT
TX
NR
TX
-------
CONC
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.50
0.50
0.50
0.50
0.50
0.50
0.50
0.60
0.60
0.60
0.60
1.00
1.00
1.00
1.00
1.10
1.10
1.10
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NC
NC
NE
NC
NC
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 0 DAY
DAY
DAY
DAY
DAY
DAY
0 . 0 SUPRF
DAY
MCGEE
MCGEE
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
SUPRF
0 . 0 SUPRF
0 . 0 SUPRF
0 . 0 SUPRF
DAY
0 . 1 DAY
0 . 1 DAY
L1\JPl**.WCi = 3'
TEST
CR14
CR14
CR14
CR14
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
CR14
CR14
CR14
HA28
HA28
HA28
HS28
HS28
HS28
TT28
TT28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
HA10
HA28
HA28
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
HA10
HA10
HA10
CR14
HA28
HS28
j£. ^n&r
SAMPI
CW12
CW13
CW15
CW16
CW12
CW13
CW15
CW16
CW12
CW13
CW15
CW16
CW12
CW13
CW15
CW14
CW18
CW24
CW14
CW18
CW24
CW14
CW18
CW24
CW14
CW18
CW24
CW21
CW22
CW21
CW22
CW21
CW22
CW21
CW22
CW17
SD03
CW17
BR7
BR7
CW17
CW17
CW23
CW23
CW23
CW23
OE27
OE02
OE10
SD05
VS07
VS07
VS07
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
:=302 CHEMCODE=ARSENIC UNITS=ug/g
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NQT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
TOX
SURV
89.
76.
85.
90.
94.
88.
82,
89.
80
100.
100.
100
45
44
43
86
86
76
84
93
90
100
98
98
46
47
42
84
88
89
77
98
98
45
43
89
43
86
81
81
94
43
96
90
100
39
90
3
16
35
78
0
4
,30
,00
.30
,70
,70
.00
,70
.30
.00
.00
.00
.00
.00
.00
.00
.70
.70
.00
.00
.30
.70
.00
.00
.00
.00
.00
.00
.00
.00
.30
.30
.00
.00
.00
.00
.30
.00
.70
.30
.30
.00
.00
.00
.70
.00
.00
.00
.00
.00
.00
.70
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
TX
TX
GROW
0.
0.
0.
0.
0.
0,
0,
0,
10
10
10,
10
172
126
126
0
0
0
0
0
0
10
11
8
135
147
62
0
0
0
0
9
9
117
74
0
2
0
3
3
10
154,
0
0,
7.
43
3.
3.
3,
1,
0,
0
-0.
,52
51
,49
65
.70
,66
.76
,79
.12
.93
.94
.58
.00
.00
.00
.61
.66
.51
.74
.82
.66
.59
.15
.53
.00
.00
.00
.58
.55
.74
.71
.97
.11
.00
.00
.64
.11
.87
.82
.82
.40
.00
.35
.71
.98
.00
.87
.20
.16
,83
.29
.00
.08
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NR
NR
NR
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
1.10
2.00
2.00
2.00
2.40
2.40
2.40
2.40
2.40
2.40
2.40
2.40
2.60
2.60
2.60
2.60
2.70
2.70
2.70
2.70
3.00
3.00
3.00
3.00
3.00
3.30
3.30
3.30
3.30
3.60
4.00
4.00
4.00
4.00
4.90
4.90
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
EFFECT
NC
NE
NC
NC
NE
NE
NE
NE
NC
NC
NE
NC
NE
NE
NC
NC
NE
NE
NC
NE
NE
NC
NC
NC
NC
NE
NC
NC
NC
NC
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
0 . 3 DAY
SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
DAY
DAY
DAY
DAY
0 . 2 DAY
0 . 2 DAY
DAY
0 . 7 DAY
DAY
DAY
0 . 2 DAY
0 . 8 DAY
DAY
DAY
0 . 2 DAY
DAY
SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
DAY
0 . 3 DAY
0 . 3 DAY
1 . 0 DAY
0 . 2 HOKE
JFLD
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
JFLD
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
JFLD
DAY
DAY
DAY
11UI*J<— u^ v-ncji*n->^i_'G=rtK.or*ivj
(continued)
SAMPLE
VS07
OE16
OE25
SD04
VS03
VS04
VS03
VS04
VS03
VS04
VS04
VS03
VS05
VS05
VS05
VS05
VS01
VS01
VS01
VS01
OE14
OE12
OE23
SD01
SD14
VS06
VS06
VS06
VS06
1101
1118-01-4-01
OE04
OE21
OE24
1111-02-AS06-01
1111-02-RS13-01
CM01
CMOS
CM06
CM07
CM11
CM22
CW01
CW03
CW09
SL02
SL04
SL07
1111-02-AS12-01
CM01
CMOS
CM06
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
24.00
98.00
0.00
23.00
89.30
96.70
97.30
85.30
90.00
92.00
28.00
21.00
89.30
80.00
90.00
25.00
84.00
88.00
94.00
26 .00
96.00
10.00
0.00
12.00
35.00
89.30
58.70
78.00
27.00
10.00
75.70
18.00
0.00
13.00
82.50
72.50
84.00
84.00
78.90
82.70
72.00
82.70
88.00
80.00
85.30
77.80
73.30
71.10
92.50
89.30
86.70
97.30
TOXS
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
NT
TX
TX
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
7.00
4.27
1.50
0.33
0.32
0.42
0.62
0.01
0.46
33.00
22.00
0.32
0.60
0.15
25.00
0.43
0.61
0.19
30.00
4.98
3.43
2.02
1.95
0.32
0.54
0.01
26.00
4.73
3.63
4 .07
3.20
0.31
0.36
0.40
0.47
0.39
0.42
0.38
0.43
0.40
0.39
0.50
0.41
4 .17
0.56
0.50
0.63
TOXG
TX
NT
NR
NR
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
NT
TX
NR
NR
NR
NT
NT
TX
TX
ND
ND
NT
NR
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 \ * 2-4 | **>4
CONC
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.00
5.10
5.10
5.14
5.40
6.00
6.00
6.00
6.00
6.00
6.00
6.20
7.00
7.00
7.00
7.00
7.00
7.00
7.45
7.50
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
SG
SG
SG
SG
SG
SG
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NC
NC
NC
NC
NE
*
NE
NE
— — — i
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 5 DAY
0 . 5 DAY
DAY
DAY
DAY
DAY
DAY
DAY
1 . 5 DAY
1 . 5 DAY
1 . 5 DAY
1 . 5 DAY
1 . 5 DAY
1 . 5 DAY
HOKE
MCGEE
MCGEE
JFLD
DAY
0 . 2 JFLD
0 . 2 SUPRF
DAY
DAY
DAY
0 . 2 JFLD
0 . 8 DAY
0 . 3 SUPRF
0 . 3 SUPRF
0 . 7 DAY
DAY
2 . 1 DAY
MCGEE
MCGEE
i.wri\*\sLJCj — ~
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
HA14
HA28
HA28
CT14
CR14
CT14
HA10
HA28
HS28
TT28
CT14
CR14
HA10
HA10
HA28
HS28
TT28
HA28
HA28
i v £, i,ntti'ii~v<'iyu — rtrvoi^ii-
(continued)
SAMPLE
CM07
CM11
CM22
CW01
CW03
CW09
SL02
SL04
SL07
CM01
CMOS
CM06
CM22
CW01
CW03
CW09
SL02
SL04
SL07
CMC 7
CM11
CM01
CM06
CM07
CM11
CM22
CW09
CMOS
CW01
CW03
SL02
SL04
SL07
1104
BR5
BR5
1111-02-RS14-01
CMOS
1111-02-RS07-01
SD07
CMOS
CMOS
CMOS
1111-02-RS01-01
SL06
SD09
SD12
SL06
SL06
SL06
BR3
BR3
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
SURV
85.
96.
93.
89.
90.
84.
89.
90.
82.
96.
100
100
100
98
100
100
98
96
98
89
100
34
45
31
45
37
29
31
22
22
16
21
15
81
95
95
77
85
60
55
93
100
37
60
76
0
33
78
98
19
90
90
60
.00
.30
.30
.00
.00
.30
.00
.70
.00
.00
.00
.00
.00
.00
.00
.00
.70
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.00
.00
.50
.30
.00
.00
.30
.00
.00
.00
.00
.00
.00
.70
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
TX
TX
TX
NT
TX
NT
NT
GROW
0.
0.
0.
0.
0.
0.
0.
0.
0.
5.
5
6
4.
6
5
4.
3
4
5,
4
4
102
96
123
91
150
56
37
22
15
147
109
152
4
4
4
0.
3
1
0.
5.
102.
4.
0.
0.
2.
0,
4.
131.
3.
3.
74
53
87
72
.66
.50
69
.59
.95
.07
.16
.54
.61
.87
.78
.56
.15
.41
.98
.58
.15
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.09
.09
.34
.42
.76
.86
.67
.42
.00
.44
.18
.00
.07
.58
.24
.00
.99
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
ND
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
TX
NR
NR
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
— — -. — - — - HU1¥IV-VJL*CJ= 3 \i *. ^nEilFlVJWlyd=^\I\OCjl'< A
(continued)
CONC
7.60
8.00
8.00
8.00
8.00
8.60
8.60
8.66
8.70
9.00
9.00
9.00
9.00
10.00
10.00
10.00
10.00
10.00
10.00
10.00
10.00
10.50
11.00
11.10
11.10
12.00
12.00
12.00
12.00
13.00
13.10
13.50
13.50
13.50
14 .40
15.00
15.20
16.00
16.60
18.80
19.00
20.00
20.00
25.00
26.00
32.00
34.00
36.00
42.00
43.00
52.00
54.70
EFFECT
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
NC
NE
NC
SG
NE
NE
SG
NE
*
SG
RATIO STUDY
MCGEE
DAY
DAY
0 . 7 DAY
DAY
MCGEE
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
MCGEE
DAY
DAY
0 . 4 JFLD
0 . 5 HOKE
MCGEE
MCGEE
0 . 4 SUPRF
HOKE
HOKE
HOKE
0 . 6 HOKE
HOKE
JFLD
MCGEE
MCGEE
HOKE
JFLD
HOKE
HOKE
HOKE
JFLD
0 . 7 SUPRF
1 . 1 JFLD
0 . 8 JFLD
HOKE
0 . 9 JFLD
1 . 4 HOKE
HOKE
JFLD
1 . 7 JFLD
JFLD
2 . 3 HOKE
2 . 0 JFLD
TEST
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HA28
HA28
HA28
HA28
HS28
TT28
CT14
HA14
HA28
HA28
HA10
HA14
HA14
HA14
HA14
HA14
CT14
HA28
HA28
HA14
HA10
HA14
HA14
HA14
CT10
HA10
CT10
HA10
HA14
CT14
HA14
HA14
HA10
HA10
HA10
HA14
CT14
SAMPLE
CON2
CM09
CM09
CM09
CM09
BR6
BR6
BR4
BR4
CM17
CM17
CM17
CM17
CM15
CM15
BR8
BR8
BR9
BR9
CM15
CM15
1111-02-AS09-01
1096
BR2
BR2
SD08
1094
1095
1109
1090
1099
1111-02-AS05-
BR1
BR1
1111
1118-01-5-01
1107
355
1108
1111-02-RS15-
SD02
1111-02-AS03-
1118-01-1-01
1106
1111-02-AS08-
1082
1088
1118-01-9-01
1118-01-11-01
1118-01-10-01
1084
1111-02-RS12-
01
01
01
01
01
ug/g -•
IPTYPE
BS
BT
BT
BT
BT
BS
BS
BS
BS
BT
BT
BT
BT
BT
BT
BS
BS
BS
BS
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
SURV
88.70
75.30
93.30
90.00
44.00
91.30
91.30
85.00
85.00
80.00
94.70
94.00
40.00
86.70
88.00
93.80
93.80
90.00
90.00
94.00
43.00
42.50
68.80
80.00
80.00
0.00
71.30
93.80
93.80
63.80
92.50
75.00
90.00
90.00
96.10
88.70
95.00
70.00
88.80
85.00
47.00
82.50
20.00
90.00
17.50
0.00
82.50
89.00
24.30
62.30
1.30
52.50
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
NT
NT
TX
NT
TX
TX
GROW
3.70
0.46
0.67
3.39
113.00
3.88
3.88
3.96
3.96
0.46
0.49
2.03
73.00
0.50
0.54
3.88
3.88
3.94
3.94
3.30
102.00
3.03
4.12
4.12
0.00
5.06
4.12
4.12
4.59
1.98
3.78
0.72
1.32
TOXG
NT
NT
NT '
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NR
ND
ND
ND
ND
ND
NT
NT
NT
ND
ND
ND
ND
ND
NT
NR
TX
ND
ND
TX
ND
ND
ND
ND
ND
ND
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
60.00
69.80
70.00
70.00
70.00
70.
71.
92.
93.
105.
110.
120.
120.
131
137.
137.
137
137
520
00
00
90
00
00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
*
*
NE
NE
NE
**
*
NE
* *
NE
**
**
**
NE
NE
NE
NE
**
**
RATIO
2.7
2.5
20.
2.
4.
4.
4.
4.
40
21
7
9
2
.5
.9
,9
.6
.2
STUDY
HOKE
JFLD
DAY
DAY
DAY
DAY
JFLD
HOKE
HOKE
SOPRF
JFLD
JFLD
JFLD
JFLD
DAY
DAY
DAY
DAY
JFLD
tf vi'jv-vyr/d— ~
TEST
HA14
CT14
CR14
HA28
HS28
TT28
HA10
HA14
HA14
HA10
HA10
HA10
HA10
CT14
CR14
HA28
HS28
TT28
HA10
> \i £, ^,riK*i"i^-wjL/Ki — /ii\0£ij.i.
(continued)
SAMPLE
1081
1111-02-AS07-01
CW06
CW06
CW06
CW06
1118-
1110
1085
CS04
1118-
1118-
1118-
1111-
CW05
CW05
CW05
CW05
1118-
01
01
01
01
02
01
-6-01
-8-01
-2-01
-7-01
-RS11-01
-3-01
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
SURV
1.
40.
82.
94.
94.
24.
58.
95.
0.
93.
60.
33.
0.
90
86
90
100
26
42
30
00
70
70
00
00
00
.00
.00
.30
.30
.30
.00
.00
.70
.70
.00
. 00
.30
TOXS
TX
TX
NT
NT
NT
TX
TX
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
GROW
2.
0.
0.
5.
22.
0.
4
0
0
6
29
,73
.36
.53
,35
.00
.50
.64
.33
.42
.17
.00
TOXG
ND
TX
NT
NT
NT
TX
ND
ND
ND
NT
ND
ND
ND
NT
NT
NT
NT
TX
ND
-------
CONC
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.20
0.29
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.30
0.36
0.38
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
HOKE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
0 . 2 DAY
DAY
DAY
DAY
DAY
DAY
0 . 4 DAY
0 . 4 DAY
0 . 4 DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
nui'iv.iyL/u— j
TEST
CR14
CR14
CR14
CR14
CR14
CR14
CR14
CR14
HA14
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
TT28
HA28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA28
HA28
CR14
CR14
CR14
CR14
CR14
HA28
HA28
HA28
HA28
1 U_t V^IIUI'I
SAMPL
CMOS
CM09
CM15
CM17
CW13
CW23
SL02
VS01
1104
CMOS
CM09
CM15
CM17
CW13
CW23
SL02
VS01
CMOS
CM15
CM17
CW13
CW23
SL02
CM09
VS01
CM09
CM15
CM17
CW13
VS01
CMOS
CW23
SL02
BR3
CW14
CW17
CW14
CW17
CW14
CW17
CW14
CW17
BR2
BR5
CW09
CW12
CW16
CW22
CW24
CW09
CW12
CW16
CW24
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=303 CHEMCODE=CADMIUM UNITS=ug/g
•uy/y -
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
84.00
75.30
86.70
80.00
76.00
96.00
77.80
84.00
81.30
86 .70
93.30
88.00
94.70
88.00
90.70
89.30
88.00
100.00
94 .00
94.00
100.00
100.00
98.00
90.00
94.00
44.00
43.00
40.00
44.00
26.00
31.00
39.00
16.00
90.00
86.70
89.30
84.00
86.70
100.00
94.00
46.00
43.00
80.00
95.00
85.30
89.30
90.70
88.00
76.00
84.00
94.70
89.30
90.70
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0.36
0.46
0.50
0.46
0.51
0.35
0.39
0.43
0.50
0.67
0.54
0.49
0.66
0.71
0.69
0.61
5.16
3.30
2.03
10.93
7.98
3.15
3.39
0.19
113.00
102.00
73.00
126.00
30.00
37.00
43.00
147.00
3.99
0.61
0.64
0.74
0.87
10.59
10.40
135.00
154.00
4.12
4.09
0.40
0.52
0.65
0.55
0.51
0.50
0.70
0.79
0.66
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.40
0.41
0.43
0.44
0.50
0.50
0.50
0.50
0.50
0.50
0.50
0.50
0.50
0.50
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.67
0.70
0.70
EFFECT
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
SG
SG
NE
NE
NC
RATIO STUDY
0 . 5 DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
DAY
DAY
HOKE
HOKE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 3 DAY
DAY
DAY
DAY
DAY
DAY
0 . 7 DAY
0 . 5 MCGEE
DAY
DAY
DAY
DAY
0 . 7 DAY
0 . 7 DAY
DAY
DAY
DAY
DAY
1 . 2 DAY
1 . 2 DAY
MCGEE
HOKE
0 . 5 HOKE
wun\_uun*— J i
TEST
HA28
HA28
HS28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
HA28
HA28
HA28
CR14
CR14
HA14
HA14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
CR14
CR14
CR14
CR14
CR14
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
TT28
TT28
HA28
HA14
HA14
JJ i-nc*r
(t
SAMPI
CW22
BR7
CW09
CW12
CW16
CW22
CW24
CW09
CW12
CW22
CW24
CON2
BR4
BR1
CM22
CW18
1106
1107
CM22
CW18
CM22
CW18
CM22
CW18
CM01
CM07
CM11
CW01
CW15
SL06
CM01
CM07
CM11
CW01
CW15
SL06
PR4
CM01
CW01
CW15
SL06
CM07
CM11
CM01
CM07
CM11
CW15
CW01
SL06
BR6
1095
1096
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=303 CHEMCODE=CADMIUM UNITS=ug/g
(continued)
SAMPTYPE
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
TOXIC
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
SURV
77.
81.
100.
80.
100,
98.
98.
29,
45.
43.
42
88
85
90
82
86
90
95
93
93
100
98
37
47
84
82
72
88
85
76
89
85
96
89
82
78
25
96
98
100.
98.
89
100.
34 .
31.
45.
43 .
22
19.
91,
93
68
30
30
00
00
.00
.00
.00
.00
.00
.00
.00
.70
.00
.00
.70
.70
.00
.00
,30
.30
.00
.00
.00
.00
.00
.70
.00
.00
.30
.00
.30
.60
.00
.30
.70
.70
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.30
.80
TOXS
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
GROW
0.
3.
4.
10.
10.
9.
8.
56.
172.
74.
62.
3.
3.
4.
0.
0.
0.
0
4.
11.
150
147
0
0.
0
0,
0.
0
0.
0.
0
0.
0.
0.
2.
5.
6
10.
4.
4.
4.
102.
123.
91.
126.
22.
131.
3.
71
82
56
12
58
11
53
.00
.00
.00
.00
.70
,96
.12
.42
.66
.87
.82
.61
.15
.00
.00
.31
.47
.39
.38
.49
.18
.56
.74
.53
.72
.76
.58
.15
.07
.87
.94
24
.58
.15
00
00
00
00
.00
.00
88
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
ND
ND
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
0.70
0.70
0.74
0.80
0.80
0.80
0.80
0.90
0.90
0.90
1.00
1.00
1.00
1.00
1.00
1.00
1.00
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.10
1.20
1.20
1.20
1.20
1.20
1.30
1.30
1.30
1.30
1.30
1.30
1.30
1.30
1.40
1.50
1.50
1.50
1.50
1.50
1.50
1.50
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
*
NE
NE
NE
NE
*
NE
NE
NE
SG
NE
SG
NE
*
SG
NE
NE
NE
NE
NE
NE
SG
RATIO STUDY
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
DAY
HOKE
HOKE
HOKE
DAY
0 . 0 SUPRF
0 . 0 SUPRF
HOKE
DAY
1 . 2 DAY
DAY
DAY
DAY
DAY
HOKE
DAY
DAY
DAY
MCGEE
DAY
DAY
1 . 3 DAY
DAY
2 . 1 DAY
2 . 1 DAY
DAY
DAY
MCGEE
DAY
2 . 3 DAY
DAY
DAY
DAY
1 . 5 DAY
DAY
1 . 5 DAY
DAY
2 . 5 DAY
1 . 1 HOKE
DAY
DAY
JFLD
DAY
DAY
MCGEE
1 . 3 MCGEE
."HJl'l^WL/J^— J
TEST
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA14
HA14
HA14
CR14
HA10
HA10
HA14
HA28
HS28
TT28
CR14
CR14
CR14
HA14
HA28
HA28
HA28
HA28
HS28
HS28
HS28
TT28
TT28
TT28
CR14
HA28
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA14
CR14
CR14
CT14
HA28
HA28
HA28
HA28
iuj v-ndi'iv-wivii — v^/^uri j. vj
(continued)
SAMPLE
BR9
TB3
BR8
CW21
CW21
CW21
CW21
1094
1099
1108
VS04
SD03
SD14
355
VS04
VS04
VS04
CM06
SL04
VS03
1111
CM06
SL04
VS03
WS2
CM06
SL04
VS03
CM06
SL04
VS03
CW03
CW03
WS1
CW03
CW03
CMOS
VS06
CMOS
VS06
CMOS
VS06
CMOS
VS06
1090
SL07
VS05
1111-02-RS13-01
SL07
VS05
AR5
KL1
SAMPTYPE
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
SURV
90.00
73.80
93.80
84.00
89.30
98.00
45.00
71.30
92.50
88.80
96.70
43.00
35.00
70.00
85.30
92.00
28.00
78.90
73.30
89.30
96.10
97.30
90.00
97.30
78.80
100.00
96.70
90.00
45.00
21.00
21.00
80.00
90.00
86.30
100.00
22.00
85.30
89.30
93.30
58.70
100.00
78.00
37.00
27.00
63.80
71 .10
89.30
72.50
82.70
80.00
76.30
61.30
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
TX
GROW
3.94
2.39
3.88
0.58
0.74
9.97
117.00
0.32
2.11
1.95
0.62
0.46
33.00
0.40
0.50
0.33
0.63
0.59
0.42
2.61
6.54
4.41
0.01
96.00
109.00
22.00
0.43
0.66
2.58
5.78
15.00
0.42
0.32
0.67
0.54
5.42
0.01
102.00
26.00
0.41
0.32
3.20
0.95
0.60
2.68
2.00
TOXG
NT
NT
NT
NT
NT
NT
NT
ND
ND
ND
NT
NR
NR
ND
NT
TX
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
1.50
1.50
1.50
1.50
1.70
1.70
1.90
1.90
1.90
2.00
2.00
2.00
2.00
2.00
2.00
2.00
2.20
2.20
2.50
2.50
2.50
2.90
3.00
3.00
3.00
3.20
3.50
3.90
4.00
4.20
4.20
4.20
4.20
4.50
4.90
4.90
4.90
4.90
5.00
5.20
6.90
7.00
8.50
9.00
9.10
10.00
11.70
12.00
12.00
24.20
28.10
36.00
EFFECT
NE
SG
*
*
NE
SG
NC
NE
NE
NC
NC
NC
NC
NE
SG
SG
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NE
NE
NE
NE
**
NC
NE
NE
NE
**
NE
**
NE
NC
NE
NE
**
**
**
NC
NC
* *
NC
NC
RATIO
1.7
2.9
2.9
1.5
0.0
0.0
0.0
0.0
0.0
1.8
1.8
0.0
0.0
0.0
8.2
0.1
9.5
4.0
0.1
7.0
7.7
9.0
0.0
0.0
18.6
0.4
0.0
STUDY
DAY
DAY
DAY
DAY
MCGEE
MCGEE
JFLD
MCGEE
MCGEE
SUPRF
SUPRF
SUPRF
SUPRF
HOKE
MCGEE
MCGEE
MCGEE
MCGEE
JFLD
SUPRF
SUPRF
HOKE
SUPRF
SUPRF
SUPRF
MCGEE
JFLD
SUPRF
HOKE
DAY
DAY
DAY
DAY
JFLD
DAY
DAY
DAY
DAY
SUPRF
HOKE
JFLD
JFLD
JFLD
SUPRF
HOKE
HOKE
HOKE
SUPRF
SUPRF
HOKE
JFLD
SUPRF
lIUl'IV-WLJCi^-
TEST
HS28
HS28
TT28
TT28
HA28
HA28
CT14
HA28
HA28
HA10
HA10
HA10
HA10
HA14
HA28
HA28
HA28
HA28
CT14
HA10
HA10
HA14
HA10
HA10
HA10
HA28
CT10
HA10
HA14
CR14
HA28
HS28
TT28
CT14
CR14
HA28
HS28
TT28
HA10
HA14
CT14
CT14
CT14
HA10
HA14
HA14
HA14
HA10
HA10
HA14
CT14
HA10
(continued)
SAMPLE
SL07
VS05
SL07
VS05
TB1
AR1
1111-
AR2
KL4
SD04
SD05
SD07
SD08
1109
AR3
KL5
KL2
KL3
1111-
OE16
OE27
1110
SD01
SD09
SD12
AR4
1111-
CS04
1088
CW06
CW06
CW06
CW06
1111-
CW05
CW05
CW05
CW05
MA13
1082
02-RS01-01
02-RS14-01
02-RS15-01
02-RS07-01
1111-02-AS12-01
1111-
1111-
OE14
1081
1101
1084
OE10
SD02
1085
1111-
OE04
02-AS09-01
02-AS06-01
02-AS08-01
SAMPTYPE
BT
BT
BT
BT
BS
BS
BT
BS
BS
BT
BT
BT
BT
BT
BS
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
SURV
98.
90.
15.
25.
87.
38.
60.
77.
72.
23,
35
55.
0.
93
53
61
82
78
77
98
90
95
12
0
33
85
85
93
82
82
94
94
24
60
86
90
100
26
71
0
92,
42
82
96.
1
10
1.
16
47
0
17
18
00
00
00
00
.50
80
00
.50
.50
.00
.00
.00
.00
.80
.80
.50
.50
.80
.50
.00
.00
.00
.00
.00
.00
.00
.00
.30
.50
.70
.70
.00
.00
.00
.70
.70
.00
.00
.70
.00
.50
.50
.50
.00
.30
.00
.30
.00
.00
.00
.50
.00
TOXS
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
TX
TX
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
TX
TX
TX
TX
TX
GROW
5.
0.
152.
25.
2,
1.
4.
2
2
1
1
1
0
2
2
2
2
4
4
3
2
0
2
1
4
0
0
0
5
22
3
0
0
6
29
0
4.
3
4.
4.
3
1
0
4
98
.15
.00
.00
,96
.96
.44
.10
.45
.50
.83
.86
.00
.01
.71
.62
.61
.34
.27
.87
.02
.00
.07
.96
.59
.50
.36
.53
.35
.00
.76
.33
.42
.17
.00
.18
.17
.03
.07
.98
.16
.98
.72
.73
TOXG
NT
TX
NT
TX
NT
NT
NT
NT
NT
NR
NR
NR
NR
ND
NT
NT
NT
NT
NT
NT
NT
ND
NR
NR
NR
NT
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
ND
NT
TX
NT
NT
ND
ND
ND
TX
NR
ND
TX
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
41.
41.
41.
41.
46.
49.
49.
52.
52.
110
120.
180.
180.
200.
210.
367
1020.
1100.
1200.
1600.
2000.
2300
3400.
4600.
180000.
.00
,00
.00
.00
.40
.00
.50
.00
.60
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
,00
.00
.00
EFFECT
NE
* *
**
**
NE
NE
**
NC
NC
NC
NC
NE
NC
NC
NE
NE
**
NC
NC
NE
NC
NC
NE
NE
NE
RATIO
47.
47.
79.
14.
0.
0.
0.
0.
0.
0.
14.
0.
0.
0.
0.
7
.5
.7
.1
.0
, 7
.0
.0
.0
.0
1
.1
. 1
.1
.1
STUDY
DAY
DAY
DAY
DAY
JFLD
SUPRF
JFLD
SUPRF
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
WUMLOUt;=.
TEST
CR14
HA28
HS28
TT28
CT14
HA10
CT10
HA10
CT14
HA10
HA10
HA10
HA10
HA10
HA10
CT14
CT14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
JUJ UHEMCOUE=CADM1I
(continued)
SAMPLE
VS07
VS07
VS07
VS07
1111-
MA08
1111-
OE24
1111-
OE21
OE12
MAO 5
OE23
OE02
MAO 7
1111-
1111-
MA03
MA01
MA06
MAO 4
OE25
MA11
MA10
MAO 9
02-AS05-01
02-AS03-01
02-AS07-01
02-RS11-01
02-RS12-01
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
SURV
78.
0.
4.
24 ,
75.
86,
82.
13,
40.
0
10.
88.
0,
3
88
90
52
10.
0
81.
76.
0.
90.
78,
78,
.70
.00
,00
.00
,00
.70
.50
.00
.00
.00
,00
.30
.00
.00
.30
.00
.50
.00
.00
.70
.70
.00
,00
,30
.30
TOXS
NT
TX
TX
TX
NT
NT
NT
TX
TX
TX
TX
NT
TX
TX
NT
NT
TX
TX
TX
NT
TX
TX
NT
NT
NT
GROW
0.
0.
-0
7,
5.
0
3
3
2
3
0
3
0
4
1
0
0
0
0
0
.29
.00
.08
.00
.06
.14
.78
.63
.73
.43
.18
.20
.23
.64
.32
.16
.16
.16
.14
.17
TOXG
NR
NR
TX
TX
NT
NT
TX
TX
TX
NR
TX
NT
NR
TX
NT
NT
TX
NR
NR
NT
NT
NR
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
2.40
2.40
10.00
10.00
12.10
12.10
20.60
20.60
21.00
23.00
24.70
27.00
29.20
29.50
30.00
34.00
34.80
35.00
37.40
40.00
43.90
45.90
46.00
46.40
46.40
48.70
50.10
52.70
53.00
53.00
54.40
55.00
56.00
57.60
58.00
59.00
59.00
61.50
67.00
68.00
69.00
70.00
72.40
76.00
80.00
84.00
90.00
91.00
92.00
94.00
95.00
97.00
100.00
EFFECT
NE
NE
NC
NE
NE
NE
*
*
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NC
NE
NE
NC
NE
NE
NC
NC
NE
NE
NC
NE
NE
SG
SG
NC
NE
NE
NE
SG
NE
NE
NE
NE
NE
NE
NE
SG
H
RATIO STUDY
JFLD
JFLD
0 . 2 SUPRF
HOKE
JFLD
JFLD
2 . 8 JFLD
2 . 8 JFLD
JFLD
SUPRF
HOKE
JFLD
MCGEE
MCGEE
MCGEE
HOKE
HOKE
SUPRF
MCGEE
HOKE
JFLD
0 . 3 JFLD
0 . 8 JFLD
0 . 3 JFLD
MCGEE
0 . 3 JFLD
MCGEE
JFLD
0 . 3 JFLD
MCGEE
MCGEE
0 . 8 SUPRF
0 . 7 HOKE
MCGEE
HOKE
1 . 0 JFLD
HOKE
MCGEE
1 . 1 JFLD
1 . 1 JFLD
0 . 9 MCGEE
HOKE
JFLD
MCGEE
1 . 3 JFLD
JFLD
HOKE
MCGEE
HOKE
MCGEE
HOKE
MCGEE
1 . 7 JFLD
IUMCODE=3
TEST
CT15
HA28
HA10
HA14
CT15
HA28
CT15
HA28
HA10
HA10
HA14
HA10
HA28
HA28
HA28
HA14
HA14
HA10
HA28
HA14
CT14
CT14
HA10
CT14
HA28
CT10
HA28
CT14
CT14
HA28
HA28
HA10
HA14
HA28
HA14
HA10
HA14
HA28
HA10
HA10
HA28
HA14
CT14
HA28
HA10
HA10
HA14
HA28
HA14
HA28
HA14
HA28
HA10
04 CHEMCODE-CHROMIUM
SAMPLE
1117-01-SED-9-01
1117-01-SED-9-01
SD03
355
1117-01-SED-16-01
1117-01-SED-16-01
1117-01-SED-2-01
1117-01-SED-2-01
1118-01-4-01
OE27
1106
1118-01-5-01
BR7
BR3
BR5
1108
1107
OE16
BR6
1104
1111-02-RS13-01
1111-02-RS07-01
1118-01-6-01
1111-02-RS01-01
BR2
1111-02-AS03-01
BR4
1111-02-RS14-01
1111-02-AS09-01
BR1
COM2
OE10
1096
BR9
1110
1118-01-8-01
1111
BR8
1118-01-2-01
1118-01-7-01
PR4
1095
1111-02-AS05-01
TB3
1118-01-11-01
1118-01-9-01
1099
WS2
1094
WS1
1109
TB1
1118-01-1-01
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BS
BT
BT
BT
BT
BT
BS
BT
BS
BT
BT
BS
BS
BT
BT
BS
BT
BT
BT
BS
BT
BT
BS
BT
BT
BS
BT
BT
BT
BS
BT
BS
BT
BS
BT
TOXIC
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
SURV
64.00
74.00
43.00
70.00
84.00
80.00
28.00
0.00
75.70
90.00
90.00
88.70
81.30
90.00
95.00
88.80
95.00
98.00
91.30
81.30
72.50
60.00
58 .00
60.00
80.00
82.50
85.00
77.50
42.50
90.00
88.70
16.00
68.80
90.00
95.00
60.30
96.10
93 .80
33 .30
0.00
25.00
93.80
75.00
73.80
24.30
89.00
92.50
78.80
71.30
86.30
93.80
87.50
20.00
TOXS
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
NT
NT
TX
NT
NT
TX
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
GROW
2.59
0.10
2.11
2.55
0.11
0.25
3.87
3.82
3.99
4.09
4.27
3.88
3.20
3.76
4.44
4.12
3.78
3.96
4.34
3.03
4.12
3.70
3.16
3.94
3.88
2.15
5.06
2.39
2.61
2.58
2.96
TOXG
NT
NT
NR
ND
NT
NT
TX
ND
ND
NT
ND
ND
NT
NT
NT
ND
ND
NT
NT
ND
NT
NT
ND
NT
NT
TX
NT
NT
TX
NT
NT
TX
ND
NT
ND
ND
ND
NT
ND
ND
NT
ND
NT
NT
ND
ND
ND
NT
ND
NT
ND
NT
ND
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE= 3 1
CONC
103,
106,
106,
107,
108,
110.
113.
115
118
118,
120,
124
130
134
140.
141.
150.
156
185
185.
260,
285,
312.
319,
362.
397.
407,
410.
427,
488.
540.
572.
760,
1132.
2100.
2100.
2610.
2700.
2800.
4600.
5200.
7400.
14000.
29000.
40000.
.00
.00
.00
.00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
,00
00
,00
,00
.00
00
00
00
00
00
00
EFFECT
SG
NE
SG
SG
NE
NE
SG
NE
NE
NE
SG
SG
*
NE
NE
NE
*
NE
**
* *
*
NE
NE
**
*
*
**
**
*
NE
* *
**
**
**
**
**
**
**
**
* *
**
**
**
**
**
RATIO
1
1
1
1
1
1
2
2
25
25
3
4,
2.
2.
5.
6,
2,
8.
7,
11,
14.
31.
31.
34.
40.
42.
69.
78.
112.
212.
439.
606.
.3
.4
.4
.5
.8
.6
.1
.3
.5
.5
.9
.2
.1
,3
.3
.2
.4
. 2
,5
.5
.8
,8
.8
.1
.9
.4
,7
,8
1
1
4
.1
STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
JFLD
HOKE
JFLD
MCGEE
MCGEE
SUPRF
MCGEE
JFLD
MCGEE
SUPRF
JFLD
SUPRF
MCGEE
JFLD
JFLD
SUPRF
JFLD
HOKE
HOKE
JFLD
JFLD
HOKE
SUPRF
JFLD
JFLD
SUPRF
HOKE
SUPRF
HOKE
SUPRF
SUPRF
HOKE
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
TEST
HA28
HA28
HA28
HA28
HA28
HA10
HA14
CT14
HA28
HA28
HA10
HA28
HA10
HA28
HA10
CT10
HA10
HA28
CT15
HA28
HA10
CT14
HA14
HA14
CT14
CT14
HA14
HA10
CT14
CT14
HA10
HA14
HA10
HA14
HA10
HA10
HA14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
J4 CHEMCODE=CHROMIUI
(continued)
SAMPLE
AR1
KL4
KL1
KL5
AR5
1118-
1090
1111-
AR2
KL3
OE24
AR3
1118-
KL2
OE14
1111-
OE04
AR4
1117-
1117-
OE21
1111-
1088
1101
1111-
1111-
1082
OE23
1111-
1111-
OE02
1081
OE12
1084
SD04
SD05
1085
SD14
SD07
SD08
OE25
SD12
SD09
SD01
SD02
01-10-01
02-AS12-01
01-3-01
02-RS15-01
Ol-SED-3-01
Ol-SED-3-01
02-AS06-01
02-AS07-01
02-AS08-01
02-RS12-01
02-RS11-01
SAMPTYPE
BS
BS
BS
BS
BS
BT
BT
BT
BS
BS
BT
BS
BT
BS
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
SURV
38,
72,
61
61,
76,
62
63
92
77,
78
13
53
42
82
96
85
18
85
14
0
0
82
82
10
40,
17
0
0
52
90
3,
1,
10
1
23.
35.
0.
35,
55,
0.
0.
33.
0.
12.
47.
.80
.50
.30
.50
.30
.30
.80
.50
.50
.80
.00
.80
.30
.50
.00
.00
.00
.00
.00
.00
.00
.50
.50
.00
.00
.50
.00
.00
.50
.00
.00
.30
.00
.30
.00
.00
.00
.00
.00
,00
,00
,00
,00
,00
00
TOXS
TX
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
TX
TX
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
TX
TX
TX
TX
TX
TX
NT
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
GROW
1,
2,
2
2.
2.
4
2
2
3
2
2
4
4
4
1
0
4
2.
0
1
4.
3
3
1.
1
1,
1,
0.
2.
0.
2.
1.
.96
.45
.00
.71
.68
.17
.10
.61
.63
.01
.62
.98
.59
.73
.96
.19
. 07
.73
.72
.32
.64
.20
.43
.50
.83
.95
.86
,00
,07
,00
02
98
TOXG
NT
NT
NT
NT
NT
ND
ND
NT
NT
NT
TX
NT
ND
NT
NT
NT
NT
NT
TX
ND
NR
NT
ND
ND
TX
TX
ND
NR
TX
NT
TX
ND
TX
ND
NR
NR
ND
NR
NR
NR
NR
NR
NR
NR
NR
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
nuri^vL/ct= o us t-nc.i"iuui-/ci=t~wrrcin. unx io=uy / y
CONC
2.50
5.70
5.70
6.00
6.00
6.80
6.80
8.00
8.00
10.00
10.00
10.00
10.00
10.00
11.00
11.00
13.10
16.00
16.00
18.00
18.00
18.30
19.00
19.00
19.00
19.00
21.00
21.00
21.00
21.00
21.00
21.00
21.00
21.00
21.60
22.00
22.40
23.20
24.00
24.00
27.10
28.00
28.00
28.00
28.00
29.00
29.00
29.00
29.00
29.60
29.80
30.00
30.00
EFFECT
NC
NE
NE
NC
NC
NE
NE
NC
NC
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
RATIO STUDY
0 . 0 SUPRF
JFLD
JFLD
0 . 0 SUPRF
0 . 0 SUPRF
JFLD
JFLD
0 . 0 SUPRF
0 . 0 SUPRF
DAY
HOKE
DAY
DAY
DAY
0 . 0 SUPRF
0 . 0 SUPRF
0 . 1 JFLD
JFLD
HOKE
SUPRF
0 . 1 SUPRF
HOKE
DAY
DAY
DAY
0 . 4 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 4 DAY
MCGEE
SUPRF
0 . 1 JFLD
MCGEE
SUPRF
HOKE
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
0 . 1 DAY
DAY
JFLD
MCGEE
DAY
DAY
TEST
HA10
CT15
HA28
HA10
HA10
CT15
HA28
HA10
HA10
CR14
HA14
HA28
HS28
TT28
HA10
HA10
CT14
HA10
HA14
HA10
HA10
HA14
CR14
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA28
HA10
CT14
HA28
HA10
HA14
CT14
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CT14
HA28
CR14
CR14
SAMPLE
SD03
1117-01-SED-16-01
1117-01-SED-16-01
SD04
SD05
1117-01-SED- 12-01
1117-01-SED-12-01
SD07
SD14
CM17
355
CM17
CM17
CM17
SD08
SD12
1111-02-RS01-01
1118-01-4-01
1104
OE27
SD09
1107
SL04
SL04
SL04
SL04
CM22
SL02
CM22
SL02
CM22
SL02
CM22
SL02
CON2
OE16
1111-02-RS07-01
BR7
MA13
1106
1111-02-RS13-01
CM01
CM01
CM01
CM01
CM07
CM07
CM07
CM07
1111-02-RS14-01
BR6
CM11
CM15
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
TOXIC
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
SURV
43.
84.
80.
23.
35.
79.
94.
55.
35.
80.
70.
94
94.
40.
0
33
60
75
81
90
0
95
73
90
96
21.
82
77
93
89
100
98
37.
16
88,
98
60
81.
71.
90.
72.
84.
89.
96.
34.
82.
85.
89.
31.
77.
91.
72.
86,
00
00
,00
,00
00
00
,00
,00
.00
.00
.00
.70
.00
.00
.00
.00
.00
.70
.30
.00
.00
.00
.30
.00
.70
.00
.70
.80
.30
.30
.00
.00
.00
.00
.70
.00
.00
.30
,70
.00
.50
.00
.30
.00
00
.70
,60
,00
.00
.50
.30
.00
,70
TOXS
TX
NT
NT
TX
TX
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
2.
2.
0.
1.
1.
2.
0.
1.
1
0,
0
2
73.
0
2
4
3
0
0
0
4
109
0
0
0
0
4
3
150
147
3.
4.
3
3 .
0.
3.
0.
0.
5.
102.
0.
0.
4.
123,
4.
3.
0.
0.
11
55
.11
.50
,83
,16
.18
.86
.95
.46
.49
.03
.00
.00
.07
.44
.87
.00
.50
.59
.41
.00
.42
.39
.87
.69
.61
.15
.00
.00
.70
.27
.76
.82
.18
.20
.31
.56
.07
00
.47
.74
,58
,00
34
88
.39
.50
TOXG
NR
NT
NT
NR
NR
NT
NT
NR
NR
NT
ND
NT
NT
NT
NR
NR
NT
ND
ND
NT
NR
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
30
30.
30.
30
30.
30.
32
32
32
32
33
33
33
33
33
34
34
34
34
35
35
35
35
35
35
35.
35
35
35
35
35
36
36
36
36
36
36
36
36
37
37.
37
37
37
37
38.
38
38
38
39
39
39
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.10
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.60
.80
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NC
NE
NC
NE
RATIO STUDY
DAY
DAY
DAY
0 . 1 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 6 DAY
HOKE
DAY
DAY
DAY
DAY
DAY
DAY
0 . 1 DAY
DAY
DAY
0 . 1 DAY
DAY
DAY
DAY
DAY
DAY
0 . 7 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 7 DAY
MCGEE
0 . 5 MCGEE
DAY
DAY
DAY
0 . 7 DAY
DAY
0 . 2 DAY
DAY
NUMl_UUt; = .
TEST
HA28
HA28
HS28
HS28
TT28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA14
CR14
HA28
HS28
TT28
CR14
CR14
CR14
HA28
HA28
HA28
HS28
HS28
HS28
TT28
TT28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
SUb LHttl
(c
SAMP:
CMll
CM15
CM15
CMll
CMll
CM15
CW15
CW15
CW15
CW15
CMOS
CM05
CMOS
CMOS
1108
CW18
CW18
CW18
CW18
CW14
CW17
SL06
CW14
CW17
SL06
CW14
CW17
SL06
CW14
CW17
SL06
CW13
CW21
CW13
CW21
CW13
CW21
CW13
CW21
CW01
CW01
CW01
CW01
BR9
PR4
SL07
SL07
SL07
SL07
CW22
CW22
CW22
305 CHEMCODE=COPPER UNITS=ug/g
(continued)
iy/a --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
SURV
96.
88.
94,
100.
45.
43.
85
82
100
43
84
86
100
31
88
86
93
98
47
86
89
76
84
86
78
100
94
98
46
43
19
76
84
88
89
100
98
44
45
88
89
98
22
90
25
71
82
98
15
88
77
98
.00
.00
.00
.00
.00
.00
.30
.70
.00
.00
.00
.70
.00
.00
.80
.70
.30
.00
.00
.70
.30
.00
.00
.70
.70
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.00
.00
.00
.00
.00
.30
.00
.00
.00
.00
.10
.70
.00
.00
.00
.30
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
TX
NT
GROW
0.
0.
3
4
91.
102
0
0
10
126
0
0
5
37
0
0
11
147
0
0
0
0
0
0
10
10
4
135
154
131
0
0
0
0
10
9
126
117
0
0
6
22
3
2
0.
0
5
152
0
0
9
.53
.54
.30
.15
.00
.00
.49
.76
.94
.00
.36
.50
.16
.00
.66
.82
.15
.00
.61
.64
.18
.74
.87
.58
.59
.40
.24
. 00
.00
.00
.51
.58
.66
.74
.93
.97
.00
.00
.38
.72
.87
.00
.94
.15
.41
.95
.98
.00
.55
.71
. 11
TOXG
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
39.00
39.50
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.00
41.80
44.00
44.00
44.50
45.00
46.00
47.40
49.00
49.00
49.00
49.00
49.00
49.00
49.80
51.90
54.80
59.00
63.20
63.20
63.80
65.00
65.00
65.00
65.00
67.00
68.00
68.00
69.30
73.00
74.00
75.00
75.60
76.10
EFFECT
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NC
NE
NE
SG
NE
NE
NE
NE
NC
NC
NC
NC
RATIO STUDY
DAY
MCGEE
DAY
DAY
DAY
DAY
0 . 9 HOKE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
DAY
DAY
DAY
0 . 8 DAY
MCGEE
0 . 1 SUPRF
0 . 1 SUPRF
MCGEE
SUPRF
HOKE
JFLD
DAY
HOKE
HOKE
DAY
DAY
DAY
HOKE
HOKE
HOKE
0 . 2 SUPRF
JFLD
JFLD
0 . 8 MCGEE
DAY
0 . 2 SUPRF
DAY
DAY
1 . 5 HOKE
SUPRF
SUPRF
MCGEE
SUPRF
0 . 2 SUPRF
0 . 2 SUPRF
1 . 0 MCGEE
1 . 0 MCGEE
WUMLOUK^
TEST
TT28
HA28
CR14
CR14
CR14
CR14
HA14
HA28
HA28
HA28
HA28
HS28
HS28
HS28
HS28
TT28
TT28
TT28
TT28
HA28
HA10
HA10
HA28
HA10
HA14
CT10
CR14
HA14
HA14
HA28
HS28
TT28
HA14
HA14
HA14
HA10
CT15
HA28
HA28
CR14
HA10
HA28
HS28
HA14
HA10
HA10
HA28
HA10
HA10
HA10
HA28
HA28
JOb CHEMCODE=COPPER
(continued)
SAMPLE
CW22
BR8
CMOS
CM09
CW23
CW24
1096
CMOS
CM09
CW23
CW24
CMOS
CW23
CW24
CM09
CMOS
CM09
CW24
CW23
BR5
OE10
OE24
TB3
OE14
1095
1111-02-RS15-01
CW12
1094
1099
CW12
CW12
CW12
1111
1110
1109
SD01
1117-01-SED-9-01
1117-01-SED-9-01
KL1
CW16
SD02
CW16
CW16
1090
MAO 5
MA08
BR3
MAO 6
MAO 4
MAO 3
AR1
KL5
uy/y --
1PTYPE
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
SURV
43.00
93.80
85.30
75.30
96.00
76.00
68.80
93.30
93.30
90.70
90.70
100.00
100.00
98.00
90.00
37.00
44.00
42.00
39.00
95.00
16.00
13.00
73.80
96.00
93.80
85.00
89.30
71.30
92.50
94.70
80.00
45.00
96.10
95.00
93.80
12.00
64 .00
74 .00
61.30
90.70
47.00
89.30
100.00
63.80
88.30
86.70
90.00
81.70
76.70
10.00
38.80
61.50
TOXS
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
TX
TX
TX
GROW
74.00
3.88
0.42
0.46
0.35
0.51
0.67
0.67
0.71
0.66
5.42
7.98
8.53
3.39
102.00
113.00
62.00
43.00
4.09
3.16
3.63
2.39
4.98
4.59
0.52
0.70
10. 12
172.00
2.02
2.59
0.10
2.00
0.65
1.98
0.79
10.58
0.18
0.14
3.99
0.16
0.16
1.96
2.71
TOXG
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
ND
NT
NT
ND
ND
NT
NT
NT
ND
ND
ND
NR
NT
NT
NT
NT
NR
NT
NT
ND
NT
NT
NT
NT
NT
NR
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
rguncuuK= j ub UHKMUOUKZLOPPKK
(continued)
CONC
77
78
80
90
91
92
92
93
96
96
100
100
100
100
100
101
101
101
101
102
103
109
109
109
109
120
120
120
121
126
130
135
135
135
135
140
142
142
142
142
147
148
149
149
150
152
152
152
152
167
182
187
.70
.00
.00
.20
.90
.30
.60
.00
.00
.60
.00
.00
.00
.00
.10
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.10
.00
.90
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NC
*
NC
NE
NE
NC
NE
NC
NE
**
**
NE
NE
NC
NC
*
NE
*
**
RATIO STUDY
MCGEE
SUPRF
0 . 3 SUPRF
MCGEE
MCGEE
MCGEE
MCGEE
SUPRF
SUPRF
MCGEE
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
1 . 9 DAY
1 . 3 MCGEE
MCGEE
DAY
DAY
DAY
DAY
0 . 4 SUPRF
0 . 4 SUPRF
MCGEE
MCGEE
MCGEE
JFLD
DAY
DAY
0 . 5 DAY
2 . 5 DAY
0 . 3 JFLD
DAY
DAY
0 . 5 DAY
DAY
0 . 8 JFLD
HOKE
5 . 9 JFLD
5 . 9 JFLD
JFLD
DAY
0 . 6 DAY
0 . 6 DAY
2 . 9 DAY
MCGEE
4 . 0 HOKE
4 . 1 HOKE
TEST
HA28
HA10
HA10
HA28
HA28
HA28
HA28
HA10
HA10
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
HA10
HA10
HA28
HA28
HA28
CT14
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
CT14
HA14
CT15
HA28
HA10
CR14
HA28
HS28
TT28
HA28
HA14
HA14
SAMPLE
BR4
MAO 7
MA01
AR5
AR2
KL2
WS2
MA11
MA10
KL4
CM06
CM06
CM06
CM06
KL3
CW03
CW03
CW03
CW03
AR3
WS1
CW09
CW09
CW09
CW09
OE04
OE21
TB1
BR2
AR4
1111-
VS05
VS05
VS05
VS05
1118-
VS04
VS04
VS04
VS04
1111-
1088
1117-
1117-
1118-
VS06
VS06
VS06
VS06
BR1
1082
1101
02-RS11-01
01-1-01
02-RS12-01
Ol-SED-2-01
Ol-SED-2-01
01-5-01
iy/a --
IPTYPE
BS
BT
BT
BS
BS
BS
BS
BT
BT
BS
BT
BT
BT
BT
BS
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
TOXIC
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
SURV
85.
88.
0,
76
77 .
82.
78.
90.
78.
72.
78,
97.
100
45
78.
80
90
100
22
53
86
85
84
100
29
18
0
87
80
85
90
89
80
90
25
20
96
85
92
28
52
82.
28
0
88
89.
58.
78
27
90
0
10.
.00
.30
.00
.30
.50
,50
.80
.00
.30
.50
.90
.30
.00
.00
.80
.00
.00
.00
.00
.80
.30
.30
.00
.00
.00
.00
.00
.50
.00
.00
.00
.30
.00
.00
.00
.00
.70
.30
.00
.00
.50
.50
.00
.00
.70
.30
.70
.00
.00
.00
.00
.00
TOXS
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
TX
TX
NT
NT
TX
TX
GROW
3.
0.
2.
2.
2.
2.
0.
0.
2.
0,
0.
6
96.
2,
0.
0.
5
15
2.
2
0
0
4
56
4
2
4
1.
4.
0
0
0
25
0,
0.
0
33.
1.
0.
0.
0.
0.
26.
4.
.96
.23
.68
.10
.62
.61
.16
.14
.45
.40
.63
.54
.00
,61
.43
.66
.78
.00
.01
.58
.40
.50
.56
.00
.73
.96
.12
.96
.64
.32
.60
.15
.00
.32
.62
.46
.00
.32
.25
,32
,54
,01
.00
.12
TOXG
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
TX
TX
ND
NT
NT
TX
NT
TX
ND
TX
ND
ND
NT
NT
TX
TX
NT
ND
ND
-------
SAMPLE COLLECTIONS SORXED BY CONCENXRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
CONC
190.00
201.00
201.00
201.00
201.00
207.00
207.00
207.00
207.00
207.00
207.00
207.00
207.00
226.00
230.00
230.00
231.00
270
281
287
340
360
379.
452
530.
533,
570,
605,
605,
780,
810.
830.
920.
1000.
1190.
2121.
2121.
2121.
2121.
2400.
2835.
2920.
4170.
4170.
4170.
4170.
.00
.00
.00
.00
.00
.00
.00
.00
,00
,00
.00
,00
.00
.00
.00
.00
00
00
00
00
00
00
00
00
00
00
00
00
00
EFFECT
NE
NE
NE
NC
NE
NE
NE
NE
NC
NC
NC
*
*
* *
NC
NC
SG
NE
NE
**
SG
NC
* *
NE
SG
*
SG
**
**
NE
SG
SG
NE
*
**
NE
NE
NE
**
**
NE
**
NE
NE
NE
* *
RATIO
0.7
0.8
0.8
0.8
3.9
3.9
4.9
0.7
0.7
1.2
6
1
0
8
1
2
1
24
24
1
1
2
25,
39,
7.
15.
78.
.3
.1
.8
.3
.1
.9
.2
.0
.0
.7
.8
.1
.1
.8
.8
.8
3
STUDY
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
HOKE
SUPRF
SUPRF
JFLD
SUPRF
JFLD
HOKE
SUPRF
JFLD
HOKE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
DAY
DAY
DAY
DAY
SUPRF
SUPRF
JFLD
DAY
DAY
DAY
DAY
nuni_uuii=.
TEST
CT14
CR14
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA14
HA10
HA10
CT14
HA10
CT14
HA14
HA10
HA10
HA14
CT14
HA10
CT14
HA10
CT15
HA28
HA10
HA10
HA10
HA10
HA10
CT10
CR14
HA28
HS28
TT28
HA10
HA10
CT14
CR14
HA28
HS28
TT28
JUb <_HC;i»HJUUl!;=l.UFFEK
(continued)
SAMPLE
1111-02-AS12-01
VS01
VS01
VS01
VS01
VS03
VS07
VS03
VS07
VS03
VS07
VS03
VS07
1081
OE12
OE23
1111-02-AS09-01
MAO 9
1111
1085
OE02
1118
1084
1111
1118
1111
1118
1117
1117
1118
1118
1118
1118
1118
1111
CW06
CW06
CW06
CW06
OE25
CS04
1111
CW05
CW05
CW05
CW05
-02
-01
-AS05-
-6-01
-02-AS06-
-01
-02
-01
-01
-01
-01
-01
-01
-01
-01
-02
-02
-7-01
-AS08-
-2-01
-SED-3
-SED-3
-9-01
-8-01
-11-01
-10-01
-3-01
-AS03-
-AS07-
01
01
01
-01
-01
01
01
ay/y
"1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
SURV
92.50
84.00
88.00
94.00
25.00
89.30
78.70
97.30
0.00
90.00
4.00
21.00
24.00
1.30
10.00
0.00
42.50
78.30
75.00
0.00
3.00
58 .00
1.30
82 .50
0.00
17.50
33 .30
14 .00
0.00
89.00
60.30
24 .30
62.30
42.30
82.50
82.70
94.70
94 .00
24 .00
0.00
93 .30
40.00
86.70
90.70
100.00
26.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
TX
TX
TX
NT
NT
XX
TX
TX
TX
NT
TX
TX
TX
TX
TX
NT
TX
TX
NT
TX
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
GROW
4.17
0.43
0.61
0.19
30.00
0.33
0.29
0.42
0.00
0.01
-0.08
22.00
7.00
3.43
3.03
0.17
5.06
3.20
4.07
0.72
0.19
3.78
0.36
0.53
5.35
22.00
0.50
2.73
0.33
0.42
6.17
29.00
TOXG
NT
NT
NT
TX
NT
NT
NR
NT
NR
TX
TX
TX
XX
ND
XX
NR
TX
NT
NT
ND
TX
ND
ND
NT
ND
XX
ND
XX
ND
ND
ND
ND
ND
ND
XX
NT
NX
NT
XX
NR
NX
TX
NX
NX
NX
XX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
1
1
1
1
1
1
1
1
1
1
2
2
2
2
2
2
2
2
2
2
2
2
3
3
3
3
3
3
.03
.03
.13
.13
.17
.27
.28
.31
.31
.36
.36
.40
.48
.48
.48
.51
.60
.66
.67
.76
.80
.80
.83
.98
.00
.10
.10
.20
.20
.20
.20
.20
.60
.63
.90
.02
.03
.03
.14
.21
.30
.36
.41
.57
.80
.82
.90
.00
.14
.24
.40
.40
.51
EFFECT
NE
NE
NE
NE
NE
NC
NC
NC
NC
SG
SG
NE
NE
SG
SG
NE
NC
NC
NC
NC
NE
NE
NC
NC
NC
NE
NE
NE
NC
NC
NC
NC
NE
NE
NC
NC
NE
NC
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
SG
NE
RATIO
0
0
0
0
1
1
1
1
0
0
0
0
0
0
0
0
0
0
0
0
0.
0.
0.
0.
1.
1,
.1
.1
.1
.1
.1
.1
.5
.5
.2
.2
.2
.3
.3
.3
.3
.4
.4
.4
.4
.6
.6
.6
.7
.7
.0
,2
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
SUPRF
JFLD
JFLD
JFLD
MCGEE
MCGEE
MCGEE
JFLD
JFLD
JFLD
SUPRF
MCGEE
SUPRF
SUPRF
JFLD
MCGEE
SUPRF
SUPRF
MCGEE
NUMCOUli!
TEST
CT15
HA28
CT15
HA28
CT10
HA10
HA10
HA10
HA10
CT15
HA28
CT10
CT10
CT15
HA28
CT10
HA10
HA10
HA10
HA10
CT15
HA28
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
CT14
HA10
CT14
CT14
CT14
HA28
HA28
HA28
CT14
CT14
CT14
HA10
HA28
HA10
HA10
CT14
HA28
HA10
HA10
HA28
= JU6 CHt;MCOUE=IRON UNITS=pcnt
SAMPLE SAMPTYPE
1117-
1117-
1117-
1117-
1123-
SD03
SD04
SD05
SD14
1117-
1117-
1123-
1123-
1117-
1117-
1123-
SD07
SD09
SD02
SD08
1117-
1117-
OE12
SD12
OE10
MAO 9
OE27
OE14
OE02
OE21
OE23
SD01
MAO 5
1111-
OE24
1111-
1111-
1111-
BR7
BR3
BR5
1111-
1111-
1111-
MA13
BR6
OE25
OE16
1111-
BR2
MAO 8
OE04
BR1
Ol-SED-12-01
Ol-SED-12-01
Ol-SED-9-01
Ol-SED-9-01
Ol-GW-1-01
Ol-SED-2-01
Ol-SED-2-01
Ol-CK-1-01
Ol-IS-3-01
Ol-SED-3-01
Ol-SED-3-01
Ol-GW-4-01
Ol-SED-16-01
Ol-SED-16-01
02-AS06-01
02-AS08-01
02-AS12-01
02-AS09-01
02-RS01-01
02-AS07-01
02-RS13-01
02-RS14-01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BS
BT
BT
BT
BS
BT
BT
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
SURV
79.
94.
64 .
74 .
81.
43.
23 .
35.
35.
28.
0.
83.
88.
14 .
0.
82.
55.
0.
47 .
0.
84 .
80.
10.
33 .
16.
78.
90.
96.
3 .
0.
0.
12.
88.
82.
13.
17.
92.
42.
81.
90.
95.
60.
40.
72.
71.
91.
0.
98.
77.
80.
86.
18.
90.
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
30
00
00
00
00
00
00
30
50
00
50
50
50
30
00
00
00
00
50
70
30
00
00
50
00
70
00
00
TOXS
NT
NT
NT
NT
NT
TX
TX
TX
TX
TX
TX
NT
NT
TX
TX
NT
TX
TX
TX
TX
NT
NT
TX
TX
TX
NT
NT
NT
TX
TX
TX
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
GROW
2.16
0.18
2.59
0.10
3.06
2.11
1.50
1.83
1.95
0.25
3.18
2.95
0.19
2.75
1.86
0.00
1.98
0.00
2.55
0.11
3.43
2.07
3.16
0.17
3.87
4.98
3.20
2.02
0.18
4 .07
3.63
0.72
4.17
3.03
3.82
3.99
4.09
4.44
2.73
3.20
0.18
3.88
4.27
4.34
4.12
0.14
4.73
4.12
TOXG
NT
NT
NT
NT
NT
NR
NR
NR
NR
TX
ND
NT
NT
TX
ND
NT
NR
NR
NR
NR
NT
NT
TX
NR
TX
NT
NT
NT
TX
NR
NR
NR
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
CONC
3
3
3
3
3
3
3
3
3
3
3
4
4
4
4
4
4
4
4
4
4
4
4
4
4
5
5.
5,
5.
5.
5.
6.
.60
.60
.63
.66
.79
.80
.81
.88
.89
.91
.95
.00
.06
.07
.19
.19
.23
.30
.31
.38
.56
.73
.82
.87
.89
.00
.04
.06
.20
.23
.24
.45
EFFECT
NE
SG
NE
NE
*
SG
NE
NE
NE
NC
NE
SG
SG
SG
NE
NE
NE
NE
SG
SG
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
SUPRF
1 . 2 SUPRF
MCGEE
MCGEE
3 . 5 JFLD
1 . 3 SUPRF
JFLD
JFLD
MCGEE
1 . 0 MCGEE
MCGEE
1 . 4 SUPRF
1 . 0 MCGEE
1 . 0 MCGEE
MCGEE
MCGEE
MCGEE
SUPRF
1 . 3 JFLD
1 . 1 MCGEE
MCGEE
MCGEE
1 . 2 MCGEE
1 . 5 JFLD
MCGEE
SUPRF
MCGEE
MCGEE
SUPRF
MCGEE
MCGEE
JFLD
numjjlJK'
TEST
HA10
HA10
HA28
HA28
CT10
HA10
CT10
CT14
HA28
HA28
HA28
HA10
HA28
HA28
HA28
HA28
HA28
HA10
CT14
HA28
HA28
HA28
HA28
CT14
HA28
HA10
HA28
HA28
HA10
HA28
HA28
CT14
=J06 CHEMCODE=IRON
(continued)
SAMPLE
MAO 7
MAO 4
CON2
BR4
1111
MA03
1111
1111
TB3
AR1
BR9
MA01
PR4
KL1
AR4
KL4
BR8
MA10
1111
KL5
AR2
KL3
AR3
1111
TB1
MAO 6
KL2
WS1
MA11
AR5
WS2
1111
-02-AS03-01
-02-RS15-01
-02-RS11-01
-02-RS12-01
-02-RS07-01
-02-AS05-01
JJ1L.
1PTYPE
BT
BT
BS
BS
BT
BT
BT
BT
BS
BS
BS
BT
BS
BS
BS
BS
BS
BT
BT
BS
BS
BS
BS
BT
BS
BT
BS
BS
BT
BS
BS
BT
TOXIC
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
88.30
76.70
88.70
85.00
82.50
10.00
85.00
90.00
73.80
38.80
90.00
0.00
25.00
61.30
85.00
72.50
93 .80
78.30
52.50
61.50
77.50
78.80
53.80
60.00
87.50
81.70
82.50
86.30
90.00
76.30
78.80
75.00
TOXS
NT
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0.23
0.16
3.70
3.96
3.78
4.59
4.64
2.39
1.96
3.94
2.15
2.00
1.96
2.45
3.88
0. 14
1.32
2.71
2.10
2.61
2.01
3.76
2.96
0.16
2.62
2.58
0.16
2.68
2.61
5.06
TOXG
NT
NT
NT
NT
TX
NR
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC«;1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.04
0.04
0.05
0.06
0.06
0.06
0.10
0.11
0. 11
0.13
0.13
0.15
0.16
0.18
0.18
0.18
0.19
0.19
0.20
0.20
0.20
0.20
0.21
0.21
0.22
0.22
0.24
0.24
0.25
0.27
0.28
0.28
0.29
0.29
0.29
0.29
0.30
0.30
0.30
0.33
0.34
0.35
0.36
0.37
0.38
0.39
0.39
0.40
0.43
0.45
0.45
0.46
0.46
EFFECT
NC
NC
NC
NE
NE
NC
NE
NC
NE
NE
NE
NC
NC
NE
SG
NE
SG
NE
NE
NE
NC
NC
NE
NE
SG
NE
SG
NE
NE
SG
NC
NC
NC
NE
SG
NE
NE
NE
SG
NC
NC
SG
NE
SG
NE
NC
NE
*
NE
NC
NE
NC
NE
RATIO
0.2
0.2
0.3
0.3
0.6
0.4
0.9
1.0
1.1
0.4
0.4
1.2
1.4
1.5
0.6
0.8
0.6
1.6
1.7
0.7
1.0
1.0
1.1
0.8
2.3
1.0
1.0
STUDY
SUPRF
SUPRF
SUPRF
JFLD
SUPRF
SUPRF
MCGEE
SUPRF
MCGEE
MCGEE
MCGEE
MCGEE
SUPRF
SUPRF
SUPRF
MCGEE
SUPRF
MCGEE
JFLD
JFLD
JFLD
JFLD
JFLD
MCGEE
SUPRF
MCGEE
SUPRF
MCGEE
MCGEE
SUPRF
JFLD
MCGEE
JFLD
SUPRF
SUPRF
MCGEE
JFLD
JFLD
SUPRF
JFLD
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
JFLD
MCGEE
SUPRF
MCGEE
JFLD
MCGEE
JFLD
MCGEE
WUML.UUt;=:
TEST
HA10
HA10
HA10
HA10
HA10
HA10
HA28
HA10
HA28
HA28
HA28
HA28
HA10
HA10
HA10
HA28
HA10
HA28
CT14
CT14
CT14
CT14
HA10
HA28
HA10
HA28
HA10
HA28
HA28
HA10
HA10
HA28
HA10
HA10
HA10
HA28
CT14
HA10
HA10
HA10
HA28
HA28
HA28
HA28
HA28
HA10
HA28
HA10
HA28
HA10
HA28
HA10
HA28
iU/ LHlSnUUUlisMKKCUKK
SAMPLE
OE10
OE23
SD03
1118-01-4-01
OE27
OE21
CON2
OE04
BR3
BR5
BR7
PR4
OE12
OE14
OE02
BR2
SD14
BR6
1111-02-RS13-01
1111-02-RS14-01
1111-02-RS01-01
1111-02-RS07-01
1118-01-5-01
BR1
OE24
BR4
SD04
TB3
BR9
SD05
1118-01-11-01
KL1
1118-01-6-01
OE16
OE25
AR2
1111-02-AS12-01
1118-01-9-01
SD07
1118-01-2-01
AR1
KL5
AR5
AR3
BR8
1118-01-8-01
KL3
SD12
KL2
1118-01-7-01
TB1
1118-01-1-01
KL4
UNITH=ug/g --
SAMPTYPE
BT
BT
BT
BT
BT
BT
BS
BT
BS
BS
BS
BS
BT
BT
BT
BS
BT
BS
BT
BT
BT
BT
BT
BS
BT
BS
BT
BS
BS
BT
BT
BS
BT
BT
BT
BS
BT
BT
BT
BT
BS
BS
BS
BS
BS
BT
BS
BT
BS
BT
BS
BT
BS
TOXIC
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
SURV
16 .00
0.00
43 .00
75.70
90.00
0.00
88.70
18.00
90.00
95.00
81.30
25.00
10.00
96.00
3 .00
80.00
35.00
91.30
72.50
77.50
60.00
60.00
88.70
90.00
13.00
85.00
23.00
73.80
90.00
35.00
24.30
61.30
58.00
98.00
0.00
77.50
92.50
89.00
55.00
33.30
38.80
61.50
76.30
53.80
93.80
60.30
78.80
33.00
82.50
0.00
87.50
20.00
72.50
TOXS
TX
TX
TX
NT
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
TX
NT
TX
NT
NT
NT
TX
TX
TX
TX
NT
TX
NT
TX
NT
TX
NT
TX
NT
TX
NT
GROW
3.16
2.11
3.87
3.70
4.73
3.99
4.09
3.82
2.15
3.43
4.98
3.20
4.12
1.95
3.88
3.20
4.34
4 .44
3.76
4.12
3.63
3.96
1.50
2.39
3.94
1.83
2.00
4.27
2.10
4.17
1.86
1.96
2.71
2.68
2.01
3.88
2.61
2 .07
2.62
2.96
2.45
TOXG
TX
NR
NR
ND
NT
NR
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NR
NT
NT
NT
NT
NT
ND
NT
TX
NT
NR
NT
NT
NR
ND
NT
ND
NT
NR
NT
NT
ND
NR
ND
NT
NT
NT
NT
NT
ND
NT
NR
NT
ND
NT
ND
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
NUMCODE=307 CHEMCODE=MERCU
(continued)
CONC
0
0
0
0
0
0
0
0
0
1
1.
1.
1.
1.
1,
2.
4.
8.
.50
.52
.56
.60
.60
.65
.70
.74
.80
.04
.10
.26
.28
,30
.50
29
90
60
EFFECT
NC
NE
*
NE
NE
*
SG
NE
NE
NE
SG
**
NE
NE
*
* *
**
* *
RATIO
0
3
3.
1.
1.
7.
2.
13.
10.
15.
.9
.2
.7
.2
.9
.1
6
0
6
2
STUDY
JFLD
MCGEE
SUPRF
JFLD
JFLD
SUPRF
JFLD
MCGEE
JFLD
MCGEE
JFLD
SUPRF
JFLD
JFLD
JFLD
SUPRF
JFLD
JFLD
TEST
CT14
HA28
HA10
CT10
CT14
HA10
CT10
HA28
CT14
HA28
CT14
HA10
HA10
CT14
CT14
HA10
HA10
CT14
SAMPLE
1111
WS2
SD08
1111
1111
SD09
1111
WS1
1111
AR4
1111
SD01
1118
1111
1111
SD02
1118
1111
-02-RS12-
-02-RS15-
-02-AS05-
-02-AS03-
-02-AS06-
-02-AS09-
-01-10-01
-02-RS11-
-02-AS08-
-01-3-01
-02-AS07-
01
01
01
01
01
01
01
01
01
SAMPTYPE
BT
BS
BT
BT
BT
BT
BT
BS
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
SURV
52
78
0
85.
75.
0.
82.
86.
82.
85.
42.
12.
62.
90.
17.
47.
42.
40.
.50
.80
.00
.00
.00
.00
.50
.30
.50
.00
.50
.00
30
00
50
00
30
00
TOXS
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
TX
TX
TX
TX
GROW
1
2
0
4
5
0
3
2
4
1.
3.
2.
4.
0.
1.
2.
.32
.61
.00
.59
.06
.00
.78
.58
.07
.96
.03
.02
.64
.72
98
73
TOXG
TX
NT
NR
NT
NT
NR
TX
NT
NT
NT
TX
NR
ND
NT
TX
NR
ND
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
CONG
1.70
1.70
6.00
6.00
7.20
11.00
15.80
16.20
16.20
17.00
23.10
23.10
27.00
33.00
37.00
48.00
49.30
49.30
59.00
60.00
65.00
73.00
86.00
92.00
99.00
110.00
110.00
120.00
130.00
150.00
170.00
190.00
220.00
221.00
260.00
260.00
298.00
330.00
370.00
397.00
421.00
430.00
432.00
451.00
460.00
465.00
490.00
500.00
510.00
530.00
549.00
652.00
670.00
EFFECT
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
SG
SG
NC
NC
NC
NC
NE
NE
NC
NC
NC
NE
NC
NC
NC
NC
NC
NE
NC
NC
NC
NC
NC
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
SG
NE
NE
NE
NE
NE
NC
NE
NE
RATIO
0.9
0.9
1.2
1.2
0.1
0.1
0.1
0.1
0.1
0.1
0.1
0.2
0.2
0.2
0.2
0.2
0.3
0.3
0.4
0.4
0.5
0.7
0.9
1.0
0.9
1\1
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
SOPRF
SUPRF
SUPRF
SUPRF
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
JFLD
SUPRF
SUPRF
MCGEE
SUPRF
MCGEE
JFLD
MCGEE
SUPRF
MCGEE
JFLD
SUPRF
JFLD
MCGEE
SUPRF
SUPRF
SUPRF
JFLD
JFLD
SUPRF
Ul'H— \JLJCi= J \J
TEST
CT15
HA28
CT15
HA28
CT10
CT10
CT10
CT15
HA28
CT10
CT15
HA28
HA10
HA10
HA10
HA10
CT15
HA28
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
CT14
HA10
HA10
HA28
HA10
HA28
CT14
HA28
HA10
HA28
CT14
HA10
CT14
HA28
HA10
HA10
HA10
CT14
CT14
HA10
>o v^ncji"n_ wci=rinn\3niiCii3i
SAMPLE
1117-01-SED-12-01
1117-01-SED-12-01
1117-01-SED-9-01
1117-01-SED-9-01
1123-01-IS-3-01
1123-01-GW-1-01
1123-01-CK-1-01
1117-01-SED-2-01
1117-01-SED-2-01
1123-01-GW-4-01
1117-01-SED-3-01
1117-01-SED-3-01
SD03
SD04
SD05
SD14
1117-01-SED-16-01
1117-01-SED-16-01
OE02
SD07
SD02
OE27
EDO 8
SD12
OE12
OE21
SD09
OE14
OE10
OE24
OE25
SD01
OE23
1111-02-AS12-01
MAO 5
MA13
BR3
MAO 9
BR2
1111-02-RS01-01
BR1
OE04
BR4
1111-02-RS13-01
MA04
1111-02-AS06-01
BR5
MA10
MAO 6
MA11
1111-02-AS09-01
1111-02-RS14-01
OE16
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BS
BT
BS
BT
BS
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
SURV
79.00
94 .00
64 .00
74.00
88.00
81.00
83 .00
28.00
0.00
82.00
14 .00
0.00
43.00
23.00
35.00
35.00
84.00
80.00
3.00
55.00
47.00
90.00
0.00
33.00
10.00
0.00
0.00
96.00
16.00
13.00
0.00
12.00
0.00
92.50
88.30
71.70
90.00
78.30
80.00
60.00
90.00
18.00
85.00
72.50
76.70
82.50
95.00
78.30
81.70
90.00
42.50
77.50
98.00
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
TX
TX
NT
NT
TX
TX
TX
NT
TX
TX
TX
TX
TX
NT
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
NT
GROW
2.16
0.18
2.59
0.10
2.9B
3.06
3.18
0.25
2.75
0.19
2.11
1.50
1.83
1.95
2.55
0.11
3.20
1.86
1.98
3.87
0.00
2.07
3.43
0.00
4.98
3.16
3.63
2.02
4.17
0.18
0.18
3.99
0.17
4.12
4.44
4.12
4.73
3.96
3.20
0.16
4.07
4.09
0.14
0.16
0.16
3.03
4.34
4.27
TOXG
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
TX
ND
NR
NR
NR
NR
NT
NT
TX
NR
NR
NT
NR
NR
TX
NR
NR
NT
TX
TX
NR
NR
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
numi-ULir;=jUH t-nc;nuuL'ii=ro/\riKjAjN,
(continued)
CONC
720.
734,
810.
869.
870.
881,
903.
911
977
983
990
999.
1510
2400
2600.
3830.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
SG
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
**
**
**
**
RATIO STUDY
MCGEE
1 . 2 JFLD
SUPRF
MCGEE
1 . 4 JFLD
JFLD
1 . 5 JFLD
JFLD
MCGEE
JFLD
SUPRF
MCGEE
7 . 8 JFLD
5 . 2 SUPRF
5 . 7 SUPRF
6 . 3 JFLD
TEST
HA28
CT14
HA10
HA28
CT14
CT14
CT14
CT10
HA28
CT14
HA10
HA28
CT10
HA10
HA10
CT14
SAMPLE
BR7
1111-02-RS12-01
MA08
BR6
1111
1111
1111
1111
BR8
1111
MAO 7
BR9
1111
MAO 3
MA01
1111
-02-AS07
-02-RS11
-02-AS08
-02-RS15
-02-AS05
-02-AS03
-02-RS07
-01
-01
-01
-01
-01
-01
-01
SAMPTYPE
BS
BT
BT
BS
BT
BT
BT
BT
BS
BT
BT
BS
BT
BT
BT
BT
TOXIC
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
SURV
81
52
86
91
40
90
17
85
93
75
88
90
82
10
0
60
.30
.50
.70
.30
.00
.00
.50
.00
.80
.00
.30
.00
.50
.00
.00
.00
TOXS
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
TX
TX
GROW
3
1
0
3
2
4.
0
4
3.
5.
0.
3.
3
3.
.82
.32
.14
.88
.73
.64
.72
.59
.88
.06
.23
.94
.78
.76
TOXG
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
TX
NR
NR
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
5.
5.
5.
6.
7.
8.
8.
8.
9.
13.
14.
15.
15.
15.
21.
22.
23.
25.
25.
25.
26
27
27.
28
29
29
30
31
32
32
33
35
35
37
37
37
38
40
42
43
43
44
45
46
46
48
49
50
50
52
54
54
57
00
00
00
00
00
00
00
30
00
00
00
00
00
30
00
80
.00
.00
.50
.80
.50
.00
.80
.50
.30
.90
.90
.00
.60
.80
.80
.20
.20
.00
.40
.90
.90
.00
.90
.00
.10
.00
.00
.10
.20
.50
.20
.00
.00
.20
.00
.00
.00
EFFECT
NC
NC
NC
NC
NC
NC
NC
NE
NC
NC
NC
NE
NE
NE
NE
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
SG
NE
NE
NE
NE
NE
SG
NE
NE
NE
NE
SG
NE
NE
SG
SG
SG
SG
NE
NE
NC
NE
RATIO
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
1.
1
1
1
1
1
1
0
0
0
0
0
0
0
0
0
0
0
7
8
8
.0
.0
.3
.5
.4
.4
.6
.6
.0
J
STUDY
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
HOKE
SUPRF
SUPRF
SUPRF
SUPRF
HOKE
HOKE
HOKE
JFLD
SUPRF
JFLD
JFLD
MCGEE
JFLD
JFLD
MCGEE
HOKE
HOKE
MCGEE
HOKE
SUPRF
JFLD
JFLD
JFLD
JFLD
JFLD
HOKE
MCGEE
HOKE
MCGEE
HOKE
JFLD
HOKE
JFLD
HOKE
HOKE
MCGEE
MCGEE
JFLD
JFLD
HOKE
HOKE
MCGEE
SUPRF
SUPRF
HOKE
.1\jri\^\JLJd~ J
TEST
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA14
HA10
HA10
HA10
HA10
HA14
HA14
HA14
CT14
HA10
CT14
CT14
HA28
CT14
CT14
HA28
HA14
HA14
HA28
HA14
HA10
CT14
CT14
CT10
CT10
CT14
HA14
HA28
HA14
HA28
HA14
CT14
HA14
CT14
HA14
HA14
HA28
HA28
CT14
CT14
HA14
HA14
HA28
HA10
HA10
HA14
\J ^ ^*nCirl\j\sUCt = i* J-VjiYEii-
SAMPLE
SD03
SD04
SD14
SD05
SD07
SD08
SD09
1107
SD12
SD02
SD01
OE27
1104
1106
355
1111-
OE16
1111-
1111-
BR3
1111-
1111-
BR5
1108
1111
BR7
1110
MA13
1111-
1111-
1111-
1111-
1111-
1099
BR1
1109
BR2
1096
1111-
1095
1111-
1094
1090
BR4
BR6
1111-
1111-
1081
1082
BR9
OE14
OE10
1088
02-RS01-
02-AS12-
02-RS13-
02-AS09-
02-AS08-
02-RS14-
02-RS07-
02-RS15-
02-AS03-
02-RS11-
02-AS06-
02-AS05-
02-RS12-
02-AS07-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
9/9 --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BS
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BS
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BS
BT
BT
BT
TOXIC
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NO'T
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
SURV
43.00
23.00
35.00
35.00
55.00
0.00
0.00
95.00
33.00
47.00
12.00
90.00
81.30
90.00
70.00
60.00
98.00
92.50
72.50
90.00
42.50
17.50
95.00
88.80
96.10
81.30
95.00
71.70
77.50
60.00
85.00
82.50
90.00
92.50
90.00
93.80
80.00
68.80
82.50
93.80
75.00
71.30
63.80
85.00
91.30
52.50
40.00
1.30
0.00
90.00
96.00
16.00
82.50
TOXS
TX
TX
TX
TX
TX
TX
TX
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
TX
TX
TX
NT
NT
TX
NT
GROW
2.11
1.50
1.95
1.83
1.86
0.00
0.00
2.07
1.98
2.02
3.87
4 .44
4.27
4.17
3.20
3.99
3.03
0.72
4.09
3.82
0.18
4.34
3.76
4.59
3.78
4.64
4.12
4.12
4.07
5.06
3.96
3.88
1.32
2.73
3.94
4.98
3.16
TOXG
NR
NR
NR
NR
NR
NR
NR
ND
NR
NR
NR
NT
ND
ND
ND
NT
NT
NT
NT
NT
TX
TX
NT
ND
ND
NT
ND
NT
NT
NT
NT
TX
NT
ND
NT
ND
NT
ND
NT
ND
NT
ND
ND
NT
NT
TX
TX
ND
ND
NT
NT
TX
ND
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
58
65
65
103
120
150
157
160
180
440
450
690
760
800
1000
1100
1200
1800
2400
5200
90000
.00
.00
.70
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
SG
NE
NE
*
NC
NE
* *
NE
NC
NC
NC
NC
NE
NC
NC
NC
NC
NE
NE
NC
NE
RATIO
1
3
0
5
0
0
0
0
0
0
0
0
0
.9
.4
.0
.1
.0
.1
.1
.1
.1
.1
.1
.1
.6
STUDY
HOKE
SUPRF
MCGEE
HOKE
SUPRF
SUPRF
HOKE
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
«UMUULU!>.
TEST
HA14
HA10
HA28
HA14
HA10
HA10
HA14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
suy LHKI
(
SAMP
1085
MA08
BR8
1084
OE24
MAO 5
1101
MAO 7
OE04
OE12
OE21
OE23
MAO 6
OE02
MA04
MA03
MA01
MA11
MA10
OE25
MA09
309 CHEMCODE=NICKEL UNITS=ug/g
(continued)
'y/y --
1PTYPE
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
SURV
0.
86,
93.
1.
13.
88.
10,
88,
18,
10.
0.
0.
81.
3.
76.
10.
0.
90.
78.
0.
78.
.00
.70
.80
.30
.00
.30
,00
.30
.00
.00
.00
.00
.70
.00
.70
.00
00
00
30
00
30
TOXS
TX
NT
NT
TX
TX
NT
TX
NT
TX
TX
TX
TX
NT
TX
TX
TX
TX
NT
NT
TX
NT
GROW
0
3
3
0
0
4
3
0,
3
0.
0,
0,
0.
.14
.88
.63
.18
.23
.73
.43
.16
.20
.16
.16
.14
.17
TOXG
ND
NT
NT
ND
TX
NT
ND
NT
NT
TX
NR
NR
NT
TX
NT
NR
NR
NT
NT
NR
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
6.00
7.00
7.00
7.80
8.20
8.20
10.00
10.00
10.00
10.00
10.30
11.00
12.00
14,10
15.00
16.90
17.60
18.00
18.00
18.00
18.00
18.00
18.80
18.80
19.00
20.00
20.00
21.00
21.00
21.00
21.00
22.00
23.00
23.00
23.00
23.00
24.00
24.20
25.00
25.50
25.50
25.90
26.00
27.00
27.00
27.00
27.00
27.10
27.80
29.80
29.90
30.00
30.00
EFFECT
NC
NE
NC
NE
NE
NE
NC
NC
NC
NC
NE
NC
NC
NE
NC
NE
NC
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
0 . 0 SUPRF
SUPRF
0 . 0 SUPRF
JFLD
JFLD
JFLD
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
0 . 1 SUPRF
JFLD
0 . 1 SUPRF
0 . 1 SUPRF
JFLD
0.1 SUPRF
HOKE
0 . 0 JFLD
DAY
0 . 1 SUPRF
DAY
DAY
DAY
JFLD
JFLD
HOKE
SUPRF
SUPRF
DAY
DAY
DAY
0 . 3 DAY
0 . 1 SUPRF
DAY
DAY
DAY
0 . 3 DAY
HOKE
JFLD
0 . 2 SUPRF
JFLD
JFLD
MCGEE
JFLD
DAY
DAY
DAY
DAY
JFLD
MCGEE
HOKE
MCGEE
DAY
DAY
LWrt\-\JLJCi = J
TEST
HA10
HA10
HA10
CT10
CT15
HA28
HA10
HA10
HA10
HA10
CT10
HA10
HA10
CT10
HA10
HA14
CT14
CR14
HA10
HA28
HS28
TT28
CT15
HA28
HA14
HA10
HA10
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
TT28
HA14
CT10
HA10
CT15
HA28
HA28
HA10
CR14
HA28
HS28
TT28
CT14
HA28
HA14
HA28
CR14
HA28
j-U \^nciri\^\juct— i-iCit\Lj ur
SAMPLE
OE12
OE27
OE10
1123-01-CK-1-01
1117-01-SED-12-01
1117-01-SED-12-01
OE02
OE21
OE24
SD03
1123
OE04
SD05
1123
SD04
1107
1111
CM17
OE23
CM17
CM17
CM17
1117
1117
1104
MA13
OE16
SL02
SL02
SL02
SL02
SD07
SL04
SL04
SL04
SL04
355
1123
SD14
1117
1117
BR3
1118
CM22
CM22
CM22
CM22
1111
BR5
1106
BR7
SL07
SL07
-Ol-IS-3-01
-Ol-GW-1-01
-02-RS01-01
-Ol-SED-9-01
-Ol-SED-9-01
-Ol-GH-4-01
-Ol-SED-16-01
-Ol-SED-16-01
-01-4-01
-02-RS13-01
i/y —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BS
BT
BS
BT
BT
TOXIC
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
10.00
90.00
16.00
83.00
79.00
94.00
3.00
0.00
13.00
43.00
88.00
18.00
35.00
81.00
23.00
95.00
60.00
80.00
0.00
94.70
94.00
40.00
64.00
74.00
81.30
71.70
98.00
77.80
89.30
98.00
16.00
55.00
73.30
90.00
96.70
21.00
70.00
82.00
35.00
84.00
80.00
90.00
75.70
82.70
93.30
100.00
37.00
72.50
95.00
90.00
81.30
71.10
82.70
TOXS
TX
NT
TX
NT
NT
NT
TX
TX
TX
TX
NT
TX
TX
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.43
3.87
3.16
3.18
2.16
0.18
3.20
3.63
2.11
2.95
4.73
1.83
3.06
1.50
4.44
0.46
0.49
2.03
73.00
2.59
0.10
0.18
4.27
0.39
0.69
3.15
147.00
1.86
0.50
0.59
4.41
109.00
2.75
1.95
2.55
0.11
3.99
0.42
0.87
4.61
150.00
3.20
4.09
3.82
0.41
0.95
TOXG
TX
NT
TX
NT
NT
NT
TX
NR
TX
NR
NT
NT
NR
NT
NR
ND
NT
NT
NR
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NR
NT
NT
NT
NT
ND
NT
NR
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 I SG 1-2 I * 2-4 I **>4
CONC
30.00
30.00
30.20
31.00
31.00
31.00
31.00
31.00
31.00
31.00
31.00
32.00
32.00
32.00
32.00
32.00
32.00
32.00
32.00
34.00
34.20
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
37.00
38.40
38.90
39.00
39.00
42.00
42.00
42.00
42.00
44.80
46.10
46.20
49.00
51.00
52.20
55.00
55.00
55.00
55.00
EFFECT
NE
NC
NC
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NC
NE
NE
NC
NE
NE
NC
NE
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
0 . 4 DAY
0 . 0 JFLD
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
DAY
0 . 4 DAY
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
DAY
DAY
SUPRF
HOKE
DAY
DAY
0 . 3 DAY
0.2 SUPRF
DAY
DAY
0 . 3 DAY
DAY
DAY
0 . 3 DAY
DAY
DAY
0 . 5 DAY
MCGEE
MCGEE
0 . 3 SUPRF
0 . 3 MCGEE
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
0 . 8 HOKE
HOKE
MCGEE
DAY
HOKE
DAY
DAY
• KUMLUlJli:
TEST
HS28
TT28
CT14
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA10
HA14
CR14
CR14
CR14
HA10
HA28
HA28
HA28
HS28
HS28
HS28
TT28
TT28
TT28
HA28
HA28
HA10
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA14
HA14
HA28
CR14
HA14
HA28
HS28
=J1U
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
CONC
55.
57.
57.
57.
57.
58.
59.
59.
59.
59
59,
60.
65
67.
67.
68
68.
68.
68
68,
70.
70
71.
71.
71.
71.
71,
71.
71.
71.
75.
76.
76.
76.
76.
86.
88.
88.
88.
90.
91.
91.
91.
91.
92.
92.
92.
92.
92.
92.
92.
92.
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
,00
.00
.70
.00
.70
.00
.00
.00
.00
,70
.00
.20
,00
.00
.00
.00
,00
.00
.00
.00
.00
00
,00
00
00
00
00
,00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
EFFECT
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
NE
NC
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
HOKE
DAY
0 . 4 SUPRF
DAY
DAY
DAY
0 . 4 SUPRF
MCGEE
SUPRF
HOKE
DAY
DAY
DAY
DAY
HOKE
HOKE
JFLD
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
1 . 0 DAY
1 . 3 HOKE
DAY
DAY
DAY
JFLD
DAY
DAY
DAY
1 . 2 DAY
DAY
DAY
DAY
0 . 7 DAY
DAY
DAY
DAY
DAY
NUNL.UUC;=
TEST
TT28
CR14
HA28
HS28
TT28
HA14
CR14
HA10
HA28
HS28
TT28
HA10
HA28
HA10
HA14
CR14
HA28
HS28
TT28
HA14
HA14
CT10
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA10
CR14
HA28
HS28
TT28
HA14
CR14
HA28
HS28
HA10
CR14
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
-JJ.U UHEMLULIlS-bhAlJ
(continued)
SAMPLE
CW17
CW15
CW15
CW15
CW15
1110
CW18
SD09
CW18
CW18
CW18
OE25
BR8
MAO 8
1111
CW21
CW21
CW21
CW21
1109
1094
1111-02-RS15-01
CW13
CW14
CW13
CW1 4
CW13
CW14
CW13
CW14
MAO 7
CW01
CW01
CW01
CW01
1101
CW16
CW16
CW16
1118-01-5-01
CW23
CW23
CW23
CW23
CW22
CW24
CW24
CW22
CW22
CW24
CW22
CW24
i/a —
1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
SURV
43.
85.
82
100.
43,
95,
86,
0,
93
98,
47
0
93
86
96
84
89
98
45
93
71
85
76
86
88
84
100
100
44
46
88
88,
89,
98
22.
10,
90,
89.
100.
88.
96.
90.
100.
39.
88.
76.
90.
77.
98.
98.
43.
42.
.00
.30
.70
.00
,00
.00
,70
.00
.30
.00
.00
.00
.80
.70
.10
.00
.30
.00
.00
.80
.30
.00
.00
.70
.00
.00
.00
.00
.00
.00
.30
.00
.30
.00
.00
.00
.70
,30
,00
.70
,00
70
,00
,00
00
,00
.70
30
.00
,00
00
,00
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
GROW
154.
0.
0,
10.
126.
0.
0,
0
11.
147,
3,
0
0
0
9
117
4
0
0
0
0
10
10
126
135
0,
0,
0,
6,
22.
0,
0.
10.
0.
0.
7.
43.
0.
0.
0.
0.
9.
8.
74.
62.
.00
.49
.76
.94
.00
.66
.00
.82
.15
.00
.88
.14
.58
.74
.97
.00
.59
.51
.61
.66
.74
.93
.59
.00
.00
.23
.38
.72
.87
.00
,65
,79
.58
35
71
98
.00
55
51
.66
71
11
,53
00
00
TOXG
NT
NT
NT
NT
NT
ND
NT
NR
NT
NT
NT
NR
NT
NT
ND
NT
NT
NT
NT
ND
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
ND
NT
NT
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
CONC
105.
105.
105.
105.
107.
110.
110.
110.
110.
110.
110.
110.
118.
118.
118
118
126.
131.
134
135.
135
135
135
139.
142.
142
142
142.
144
148.
149
149
1 <. 0
150
152
152
152
152.
152.
157
177
183
184.
199.
200
200
201
201
201
201
204
00
00
00
00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
00
.0
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
NE
NE
NE
SG
**
NE
NC
NC
NC
**
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
SG
SG
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
SG
*
SG
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
RATIO STUDY
DAY
DAY
DAY
DAY
1 . 6 HOKE
6 . 3 JFLD
SUPRF
0 . 7 SUPRF
0 . 7 SUPRF
0 . 7 SUPRF
6 . 3 JFLD
MCGEE
DAY
DAY
DAY
DAY
MCGEE
MCGEE
1 . 2 MCGEE
DAY
DAY
1 . 0 DAY
1 . 8 DAY
1 . 2 MCGEE
DAY
DAY
1 . 1 DAY
DAY
1 . 3 MCGEE
MCGEE
DAY
DAY
DAY
DAY
SUPRF
DAY
JFLD
1 . 2 DAY
1 . 2 DAY
2 . 1 DAY
1 . 4 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
SUPRF
SUPRF
DAY
DAY
1 . 5 DAY
DAY
MCGEE
WUl*ll_UUC.s
TEST
CR14
HA28
HS28
TT28
HA14
CT15
HA10
HA10
HA10
HA10
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
HA10
CR14
CT14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
HA28
HA10
HA10
CR14
HA28
HS28
TT28
HA28
= jj.u v-naiviuuun=ijcittij i
(continued)
SAMPLE
CW12
CW12
CW12
CW12
1090
1117-01-SED-2-01
MA10
MA01
MAO 3
MAO 4
1117-01-SED-2-01
TB3
CMOS
CM06
CM06
CM06
WS2
AR5
KL1
VS05
VS05
VS05
VS05
AR1
VS04
VS04
VS04
VS04
KL5
AR2
CW09
CW09
CW09
CW09
MAO 5
VS06
1111-02-RS14-01
VS06
VS06
VS06
AR3
KL3
WS1
KL2
KL4
MAO 9
MA11
VS01
VS01
VS01
VS01
TB1
i/y
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BS
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BS
BS
BT
BT
BT
BT
BT
BT
BS
TOXIC
NOT
NOT
NOT
NOT
TOX
TOX
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
SURV
89.
94.
80.
45.
63
28
78.
0.
10.
76
0
73
78
97
100
45
78
76
61
89.
80
90
25
38
96.
85
92
28
61
77.
85
84
100.
29.
88.
89
77.
58.
78.
27.
53.
78.
86.
82.
72.
78.
90.
84.
88.
94 .
26.
87.
.30
.70
.00
.00
.80
.00
.30
.00
.00
.70
.00
.80
.90
.30
.00
.00
.80
.30
.30
.30
.00
.00
.00
.80
.70
.30
.00
.00
.50
.50
.30
.00
.00
.00
.30
.30
.50
.70
.00
.00
.80
.80
.30
50
50
30
00
00
00
00
00
50
TOXS
NT
NT
NT
NT
TX
TX
NT
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0
0
10
172
0
0
0
2
0
0
6
96
2
2
2
0
0
0
25
1
0
0
0
33
2
2
0
0
4
56.
0.
0
4.
0.
0.
26.
2.
2.
2.
2.
2.
0.
0.
0.
0.
0.
30,
2.
.52
.70
.12
.00
.25
.14
.16
.39
.40
.63
.54
.00
.61
.68
.00
.32
.60
.15
.00
.96
.32
.62
.46
.00
.71
.10
.40
.50
.56
.00
.18
.32
.34
.54
,01
.00
.01
.61
58
62
45
17
16
43
61
19
00
96
TOXG
NT
NT
NT
NT
ND
TX
NT
NR
NR
I1"
NU
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
CONC
207.00
207.00
207.00
207.00
207.00
207.00
207.00
207.00
210.00
210.00
230.00
250.00
280.00
286.00
290.00
300.00
320.00
329.00
329.00
329.00
329.00
330.00
396.00
400.00
409.00
410.00
550.00
589.00
593.00
609.00
700.00
709.00
724.00
724.00
724.00
724.00
878.00
974.00
974.00
974.00
974.00
1354.00
1440.00
1730.00
1730.00
1830.00
2170.00
3680.00
5550.00
22300.00
EFFECT
NE
NE
NE
SG
SG
SG
*
*
NE
SG
SG
SG
NE
NE
SG
SG
NE
NE
NE
NE
**
*
**
*
NE
*
NE
**
NE
NE
**
NE
NE
NE
NE
**
* *
NE
NE
NE
+ *
* *
*
**
**
*
NE
* *
**
* *
RATIO
1.6
1.6
1.6
2.8
2.8
1.3
1.4
1.6
1.8
1.9
4.5
2.0
6.1
2.5
2.5
9.1
4.3
9.9
13.5
13.3
20.8
2.1
98.9
98.9
2.7
5.4
219.2
32.6
STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
JFLD
JFLD
JFLD
SUPRF
SUPRF
HOKE
JFLD
SUPRF
JFLD
DAY
DAY
DAY
DAY
JFLD
HOKE
JFLD
MCGEE
JFLD
JFLD
HOKE
JFLD
JFLD
JFLD
SUPRF
DAY
DAY
DAY
DAY
HOKE
DAY
DAY
DAY
DAY
HOKE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
nun^ui^cj3
TEST
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA10
HA10
HA10
HA10
HA10
HA14
HA10
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA14
HA10
HA28
HA10
CT14
HA14
CT14
CT14
HA10
HA10
CR14
HA28
HS28
TT28
HA14
CR14
HA28
HS28
TT28
HA14
CT14
CT15
HA28
CT14
CT14
CT14
CT10
CT14
:J-LU ^nLil'l'~WCl = LlCil\U L
(continued)
SAMPLE
VS03
VS07
VS03
VS07
VS03
VS07
VS03
VS07
1118-01-9-01
1118-01-6-01
1118-01-11-01
SD02
MAO 6
1088
1118-01-1-01
SD01
1118-01-10-01
CW03
CW03
CW03
CW03
1118-01-8-01
1082
1118-01-3-01
AR4
1118-01-2-01
1111-02-AS12-01
1081
1111-02-AS05-01
1111-02-AS06-01
1118-01-7-01
CS04
CW06
CW06
CW06
CW06
1084
CW05
CW05
CW05
CW05
1085
1111-02-RS12-01
1117-01-SED-3-01
1117-01-SED-3-01
1111-02-AS09-01
1111-02-RS11-01
1111-02-AS08-01
1111-02-AS03-01
1111-02-AS07-01
i/g —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
TOX
TOX
SURV
89.30
78.70
97.30
0.00
90.00
4.00
21.00
24.00
89.00
58.00
24.30
47.00
81.70
82.50
20.00
12.00
62.30
80.00
90.00
100.00
22.00
60.30
0.00
42.30
85.00
33.30
92.50
1.30
75.00
82.50
0.00
93.30
82.70
94.70
94.00
24.00
1.30
86.70
90.70
100.00
26.00
0.00
52.50
14.00
0.00
42.50
90.00
17.50
82.50
40.00
TOXS
NT
NT
NT
TX
NT
TX
NT
TX
NT
TX
TX
TX
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
TX
TX
NT
TX
NT
TX
NT
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
TX
TX
TX
NT
TX
NT
TX
GROW
0.33
0.29
0.42
0.00
0.01
-0.08
22.00
7.00
1.98
0.16
2.02
0.43
0.66
5.78
15.00
1.96
4.17
5.06
4.07
0.50
0.36
0.53
5.35
22.00
0.33
0.42
6.17
29.00
1.32
0.19
3.03
4.64
0.72
3.78
2.73
TOXG
NT
NR
NT
NR
TX
TX
TX
TX
ND
ND
ND
NR
NT
ND
ND
NR
ND
NT
NT
NT
TX
ND
ND
ND
NT
ND
NT
ND
NT
NT
ND
NT
NT
NT
NT
TX
ND
NT
NT
NT
TX
ND
TX
TX
ND
TX
NT
TX
TX
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.
0.
0.
0.
0.
0.
0.
1.
1.
1.
1.
1.
1.
1,
1,
1.
1.
1
1.
1.
1
1
1.
1
1
1.
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
3
12
76
77
78
88
89
92
98
00
.00
.00
.00
.00
.00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.30
.40
.80
.30
.90
.30
EFFECT
NC
NE
NE
NE
NC
NC
NE
NE
NE
NE
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NG
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
*
*
* *
RATIO
0
0
0
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
3
10
.7
.8
.8
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.2
.6
.4
.6
H
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
SUPRF
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
\Jl wl\~\JLsCt = J J
TEST
CT14
CT14
CT14
CT10
CT14
CT14
CT14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
CT14
CT14
CT14
CT14
CT10
CT14
CT14
LJ. v_n&l'l^WL^Cj = OC*UCil\J.'
SAMPLE
1111
1111
1111
1111
1111
1111
1111
OE14
OE16
OE27
OE02
OE04
OE10
OE12
OE21
OE23
OE24
OE25
SD01
SD02
SD03
SD04
SD05
SD07
SD08
SD09
SD12
SD14
BR1
BR2
BR3
BR4
BR5
BR6
BR7
BR8
BR9
1111
1111
1111
1111
1111
1111
1111
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
-02-
RS07-
RS14-
AS12-
RS15-
RS01-
RS12-
RS13-
AS06-
RS11-
AS09-
AS05-
AS03-
AS08-
AS07-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BS
BS
BS
BS
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
SURV
60.
77.
92.
85.
60.
52,
72,
96,
98.
90,
3.
18
16.
10,
0
0
13.
0
12
47,
43
23
35,
55
0
0,
33
35
90
80
90
85
95
91
81,
93
90,
82.
90.
42.
75.
82.
17.
40.
.00
,50
.50
,00
.00
.50
,50
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.30
.80
.00
,50
.00
,50
.00
50
.50
00
TOXS
TX
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
TX
GROW
3,
4.
4.
4,
4,
1
3,
4,
4
3
3
4
3
3
3
2
1
2
1
1
1
0
0
2
1
4
4
3
3
4
3
3
3
3
4.
4,
3,
5.
3.
0.
2.
.76
.34
.17
.59
.44
.32
.20
.98
.27
.87
.20
.73
.16
.43
.63
.02
.98
.11
.50
.83
.86
.00
.00
.07
.95
.12
.12
.99
.96
.09
.88
.82
.88
.94
.07
.64
.03
.06
.78
.72
73
TOXG
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
TX
TX
NR
NR
TX
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
4.
4.
10.
13.
18.
19.
21.
22.
22
24
24.
29
31
32
36
41
41
46
51
54
54
54
54
56
56
64
68
69
78
78
78
78
78
86
86
86
86
89
89
89
89
95
95
95
95
96
98
99
99
100
110
118
118
.20
.20
.00
.80
.30
.60
.00
.80
.80
.70
.70
.00
.00
.50
.00
.40
.40
.00
.00
.00
.00
.00
.00
.00
.30
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.30
.70
.00
.80
.00
.00
.00
.00
EFFECT
NE
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NC
NE
NC
*
*
NE
NC
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NC
NE
NC
NE
NC
NC
NC
NE
NE
RATIO STUDY
JFLD
JFLD
0 . 0 SUPRF
JFLD
JFLD
JFLD
0 . 0 SUPRF
JFLD
JFLD
JFLD
JFLD
SUPRF
0 . 0 SUPRF
JFLD
0 . 0 SUPRF
2 . 4 JFLD
2 . 4 JFLD
JFLD
0 . 0 SUPRF
DAY
DAY
DAY
DAY
0 . 1 SUPRF
HOKE
HOKE
0 . 1 SUPRF
SUPRF
DAY
0 . 1 SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 6 DAY
DAY
DAY
DAY
0 . 6 DAY
JFLD
0 . 0 JFLD
HOKE
0 . 0 JFLD
0 . 1 SUPRF
0 . 1 SUPRF
DAY
DAY
WUM^UUtis
TEST
CT15
HA28
HA10
CT10
CT10
CT10
HA10
CT15
HA28
CT15
HA28
HA10
HA10
CT10
HA10
CT15
HA28
HA10
HA10
CR14
HA28
HS28
TT28
HA10
HA14
HA14
HA10
HA10
CR14
HA10
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CT14
CT14
HA14
CT14
HA10
HA10
CR14
CR14
= Jl/i LHUFU.UUH'ZINU Ul
SAMPLE
1117
1117
SD03
1123
1123
1123
SD04
1117
1117
1117
1117
OE27
SD05
1123
SD14
1117
1117
1118
SD07
CM17
CM17
CM17
CM17
OE10
1107
355
SD08
MA13
CM15
SD12
CM15
CM15
CM15
CM22
CM22
CM22
CM22
SL04
SL04
SL04
SL04
CMOS
CM05
CMOS
CMOS
1111
1111
1104
1111
SD09
OE24
CM07
CM11
-Ol-SED-12-01
-Ol-SED-12-01
-Ol-CK-1-01
-Ol-GW-4-01
-Ol-GW-1-01
-Ol-SED-9-01
-Ol-SED-9-01
-Ol-SED-16-01
-01-SED- 16-01
-Ol-IS-3-01
-Ol-SED-2-01
-Ol-SED-2-01
-01-4-01
-02-RS13-01
-02-RS01-01
-02-RS07-01
/u —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
SURV
79.
94.
43.
83.
82.
81.
23.
64,
74.
84
80.
90
35
88
35
28
0
75
55
80
94
94
40
16
95
70
0
71
86
33
88
94
43
82
93
100
37
73
90
96
21
84
86
100
31
72
60
81
60
0
13
82
72
00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.70
.00
.00
.70
.00
.00
.00
.00
.00
.00
.70
.70
.00
.00
.00
.00
.70
.30
.00
.00
.30
.00
.70
.00
.00
.70
.00
.00
.50
.00
.30
.00
.00
.00
.70
.00
TOXS
NT
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
GROW
2.
0.
2.
3.
2.
3.
1.
2.
0.
2.
0.
3.
1.
2.
1
0.
1
0
0,
2
73
3
0
0
0
2
0.
3
102
0
0
4
150
0
0
4
109.
0
0
5
37
3.
4.
3
0
3
0
0
16
18
11
18
75
06
50
.59
.10
.55
.11
.87
.83
.95
.95
.25
.86
.46
.49
.03
.00
.16
.00
.18
.50
.07
.54
.30
.00
.42
.87
.61
.00
.50
.59
.41
.00
.36
.50
.16
.00
.20
.44
.76
.00
.63
.47
.39
TOXG
NT
NT
NR
NT
NT
NT
NR
NT
NT
NT
NT
NT
NR
NT
NR
TX
ND
ND
NR
NT
NT
NT
NT
TX
ND
ND
NR
NT
NT
NR
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
ND
NT
NR
TX
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
CONC
118.00
118.00
118.00
118.00
118.00
118.00
121.00
121.00
121.00
121.00
121.00
121.00
122.00
122.00
122.00
122.00
124.00
124.00
124.00
124.00
125.00
125.00
125.00
125.00
127.00
127.00
127.00
127.00
127.00
128.00
128.00
128.00
128.00
129.00
129.00
129.00
129.00
138.00
138.00
138.00
138.00
140.00
140.00
141.00
141.00
141.00
141.00
141.00
141.00
141.00
141.00
145.00
EFFECT
NE
NE
NC
NC
NE
NE
NE
**
NE
* *
NC
NE
NC
NC
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
DAY
DAY
0 . 1 DAY
0 . 1 DAY
DAY
DAY
DAY
7 . 0 JFLD
DAY
7 . 0 JFLD
0 . 1 DAY
DAY
0 . 2 DAY
0 . 1 DAY
DAY
0 . 8 DAY
DAY
DAY
DAY
0 . 8 DAY
DAY
DAY
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
0 . 2 DAY
0 . 1 DAY
0 . 8 DAY
DAY
DAY
DAY
0 . 9 DAY
DAY
DAY
DAY
DAY
SUPRF
SUPRF
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
• wunuuuh:
TEST
HA28
HA28
HS28
HS28
TT28
TT28
CR14
CT15
HA28
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA10
HA10
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
-J12 CHEMCODE=ZINC 1
(continued)
SAMPLE
CM07
CM11
CM07
CM11
CM07
CM11
CM09
1117-01-SED-3-01
CM09
1117-01-SED-3-01
CM09
CM09
SL06
SL06
SL06
SL06
SL02
SL02
SL02
SL02
CW15
CW15
CW15
CW15
CM01
CM01
BR7
CM01
CM01
VS06
VS06
VS06
VS06
CW01
CW01
CW01
CW01
CW18
CW18
CW18
CW18
MA05
OE16
CW13
CW14
CW13
CW14
CW13
CW14
CW13
CW14
CW21
_,,a
WTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
85.60
96.00
89.00
100.00
31.00
45.00
75.30
14.00
93.30
0.00
90.00
44.00
76.00
78.70
98.00
19.00
77.80
89.30
98.00
16.00
85.30
82.70
100.00
43.00
84.00
89.30
81.30
96.00
34.00
89.30
58.70
78.00
27.00
88.00
89.30
98.00
22.00
86.70
93.30
98.00
47.00
88.30
98.00
76.00
86.70
88.00
84.00
100.00
100.00
44.00
46.00
84.00
TOXS
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
0.74
0.53
4.58
4.15
123.00
91.00
0.46
0.19
0.67
3.39
113.00
0.18
0.58
4.24
131.00
0.39
0.69
3.15
147.00
0.49
0.76
10.94
126.00
0.31
0.56
3.82
5.07
102.00
0.32
0.54
0.01
26.00
0.38
0.72
6.87
22.00
0.66
0.82
11.15
147.00
0.18
4.27
0.51
0.61
0.66
0.74
10.93
10.59
126.00
135.00
0.58
TOXG
NT
NT
TX
TX
NT
NT
NT
TX
NT
ND
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
145.00
145.00
145.00
151.00
151.00
151.00
151.00
152.00
152.00
152.00
152.00
153.00
155.00
155.00
155.00
155.00
156.00
156.00
156.00
156.00
157.00
157.00
157.00
157.00
159.00
160.00
163.00
163.00
163.00
163.00
165.00
165.00
165.00
165.00
165.00
165.00
165.00
165.00
166.00
166.30
169.00
169.00
169.00
169.00
169.00
169.00
169.00
169.00
169.00
169.00
169.00
169.00
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
SG
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
SG
SG
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
NC
NE
SG
RATIO STUDY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
1 . 0 DAY
MCGEE
DAY
0 . 2 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 2 DAY
DAY
0 . 5 HOKE
MCGEE
DAY
DAY
0 . 2 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
1 . 1 DAY
1 . 1 DAY
HOKE
HOKE
DAY
DAY
DAY
JFLD
DAY
DAY
0 . 2 DAY
DAY
0 . 2 DAY
0 . 2 DAY
DAY
1 . 1 DAY
mji'i\-,\jijci—
TEST
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
HA14
HA28
CR14
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
HA14
HA14
CR14
CR14
CR14
CT14
HA28
HA28
HA28
HS28
HS28
HS28
TT28
TT28
(continued)
SAMPLE
CW21
CW21
CW21
CW17
CW17
CW17
CW17
VS05
VS05
VS05
VS05
BR5
CW22
CW22
CW22
CW22
CMOS
CMOS
CMOS
CMOS
VS01
VS01
VS01
VS01
1096
CON2
VS04
VS04
VS04
VS04
CW23
SL07
CW23
SL07
CW23
SL07
CW23
SL07
1095
1106
CW24
VS03
VS07
1111-02-RS14-01
CW24
VS03
VS07
CW24
VS03
VS07
CW24
VS03
i/g —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
SURV
89.30
98.00
45.00
89.30
86.70
94.00
43.00
89.30
80.00
90.00
25.00
95.00
88.00
77.30
98.00
43.00
85.30
93.30
100.00
37.00
84.00
88.00
94.00
26.00
68.80
88.70
96.70
85.30
92.00
28.00
96.00
71.10
90.70
82.70
100.00
98.00
39.00
15.00
93.80
90.00
76.00
89.30
78.70
77.50
90.70
97.30
0.00
98.00
90.00
4.00
42.00
21.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
GROW
0.74
9.97
117.00
0.64
0.87
10.40
154.00
0.32
0.60
0.15
25.00
4.09
0.55
0.71
9.11
74.00
0.42
0.67
5.42
102.00
0.43
0.61
0.19
30.00
3.70
0.32
0.62
0.46
33.00
0.35
0.41
0.71
0.95
7.98
5.98
43.00
152.00
0.51
0.33
0.29
4.34
0.66
0.42
0.00
8.53
0.01
-0.08
62.00
22.00
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
NT
ND
ND
NT
NT
NR
NT
NT
NT
NR
NT
TX
TX
NT
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG = 1 | SG 1-2 | * 2-4 | **>4
CONG
169.00
170.00
173.00
188.00
195.00
210.00
210.00
216.00
216.00
216.00
216.00
216.00
219.00
220.00
220.00
220.00
223.00
232.00
232.00
232.00
232.00
240.00
247.00
247.00
247.00
250.00
250.00
260.00
268.00
273.00
280.00
280.00
286.00
320.00
330.00
339.00
347.00
348.00
352.00
355.00
356.00
358.00
367.00
367.00
380.00
380.00
380.00
380.00
380.00
381.00
385.00
389.00
EFFECT
SG
NC
NE
NC
NE
NC
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
SG
NE
SG
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
RATIO STUDY
1 . 1 DAY
0 . 2 SUPRF
MCGEE
0 . 6 MCGEE
HOKE
0 . 2 SUPRF
0 . 2 SUPRF
DAY
DAY
MCGEE
DAY
DAY
HOKE
SUPRF
SUPRF
MCGEE
MCGEE
DAY
DAY
DAY
DAY
SUPRF
DAY
DAY
DAY
SUPRF
0 . 2 SUPRF
0 . 2 SUPRF
MCGEE
MCGEE
SUPRF
SUPRF
1 . 0 HOKE
0 . 3 SUPRF
MCGEE
MCGEE
HOKE
1 . 1 MCGEE
HOKE
1 . 1 MCGEE
MCGEE
JFLD
HOKE
MCGEE
DAY
SUPRF
DAY
DAY
DAY
1 . 3 HOKE
MCGEE
MCGEE
lt\Jl'l\,\SLJCi =
TEST
TT28
HA10
HA28
HA28
HA14
HA10
HA10
CR14
HA28
HA28
HS28
TT28
HA14
HA10
HA10
HA28
HA28
CR14
HA28
HS28
TT28
HA10
CR14
HA28
HS28
HA10
HA10
HA10
HA28
HA28
HA10
HA10
HA14
HA10
HA28
HA28
HA14
HA28
HA14
HA28
HA28
CT10
HA14
HA28
CR14
HA10
HA28
HS28
TT28
HA14
HA28
HA28
- J J.^ V-flE'l *i\_, VtytJ — £J J.lt^,
(continued)
SAMPLE
VS07
OE04
BR3
PR4
1094
MA04
OE12
CW12
CW12
TB3
CW12
CW12
1108
MA07
MAO 8
BR4
BR6
CM06
CM06
CM06
CM06
MAO 9
CW16
CW16
CW16
MA06
MA03
MA01
BR8
BR9
MA10
MA11
1090
OE21
BR2
WS2
1109
KL1
1099
AR1
WS1
1111-02-RS15-01
1110
AR5
CW09
OE14
CW09
CW09
CW09
1101
TB1
BR1
i/g —
IPTYPE
BT
BT
BS
BS
BT
BT
BT
BT
BT
BS
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BS
BS
BT
BT
BT
BT
BS
BS
BT
BS
BT
BS
BS
BT
BT
BS
BT
BT
BT
BT
BT
BT
BS
BS
TOXIC
TOX
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
SURV
24.
18.
90.
25.
71.
76.
10.
89.
94.
73.
80.
45.
88.
88
86
85.
91
78
97
100
45
78
90,
89
100
81
10
0
93
90
78
90
63
0
80
78
93
61
92
38
86
85
95.
76.
85
96
84.
100
29
10
87
90
00
00
00
00
30
70
00
.30
.70
80
.00
.00
.80
.30
.70
.00
.30
.90
.30
.00
.00
.30
.70
.30
.00
.70
.00
.00
.80
.00
.30
.00
.80
.00
.00
.80
.80
.30
.50
.80
.30
.00
.00
.30
.30
.00
.00
.00
.00
.00
.50
.00
TOXS
TX
TX
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
GROW
7.
4.
3.
2.
0.
3.
0.
0.
2.
10.
172.
0.
0.
3.
3
0.
0.
6.
96
0.
0.
0
10.
0.
3
3
0.
0.
4,
2
2,
1.
2.
4.
2.
0.
4.
0.
4.
56.
2.
4 ,
00
73
99
15
16
43
52
.70
39
.12
.00
.23
.14
.96
.88
.40
.63
.54
.00
.17
.65
.79
.58
.16
.88
.94
.14
.16
.12
.61
,00
,96
,58
.59
,68
,40
,98
50
,56
.00
.96
.12
TOXG
TX
NT
NT
NT
ND
NT
TX
NT
NT
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NR
NR
NT
NT
NT
NT
ND
NR
NT
NT
ND
NT
ND
NT
NT
NT
ND
NT
NT
NT
NT
NT
NT
ND
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
UNITS=ug/g
CONC
401.
406.
411.
411.
411.
411.
418.
430.
450.
460.
460.
460.
462.
466.
512.
541
550.
749.
750.
900
975
1200
1300
1500,
1600
1800,
1800
2100
2250
2260
2650
3250
3300
3830
4460
7527
7527
7527
7527
7900
7960
10500
10780
12500
12800
13943
13943
13943
13943
14000
00
00
00
00
00
00
,00
,00
,00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
SG
NE
NE
NE
*
SG
NE
NE
NC
NC
NC
NE
NE
NE
NE
NC
NE
NC
NE
NE
SG
SG
NE
SG
NE
SG
SG
**
NC
NC
**
*
NE
**
NE
NE
NE
* *
**
**
NE
NE
**
**
NE
NE
NE
**
**
RATIO
1.
2.
1.
0.
0.
0.
0,
0.
1,
1.
1,
1,
1,
7.
0,
1.
11.
3
15
49
8
27
4
144
92
5
3
7
3
4
,4
,4
.5
.8
.3
.4
.7
.9
.9
.8
.8
.0
.2
.5
.4
.8
.4
.5
.6
.7
.3
.1
STUDY
MCGEE
MCGEE
DAY
DAY
DAY
DAY
MCGEE
JFLD
MCGEE
SUPRF
SUPRF
SUPRF
MCGEE
MCGEE
MCGEE
HOKE
SUPRF
JFLD
JFLD
HOKE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
SUPRF
HOKE
JFLD
JFLD
HOKE
JFLD
JFLD
HOKE
DAY
DAY
DAY
DAY
JFLD
HOKE
JFLD
SUPRF
JFLD
JFLD
DAY
DAY
DAY
DAY
JFLD
WUI"H-U1JC| =
TEST
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA10
HA28
HA10
HA10
HA10
HA28
HA28
HA28
HA14
HA10
CT14
HA10
HA14
CT14
HA10
HA10
HA10
HA10
HA10
HA10
HA10
HA14
CT14
CT14
HA14
HA10
CT14
HA14
CR14
HA28
HS28
TT28
HA10
HA14
CT14
HA10
CT14
CT10
CR14
HA28
HS28
TT28
CT14
= jj.*i t_nd.nuvJUCi=^ii>H-
(continued)
SAMPLE
AR2
AR3
CW03
CW03
CW03
CW03
KL5
1118
KL3
OE02
SD01
SD02
KL4
KL2
AR4
1111
OE23
1111
1118
1088
1111
1118
1118
1118
1118
1118
1118
OE25
1082
1111
1111
1081
1118
1111
1084
CW06
CW06
CW06
CW06
1118
1085
1111
CS04
1111
1111
CW05
CW05
CMOS
CW05
1111
-01-5-01
-02-AS12-
-01-2-01
-02-AS06-
-01-6-01
-01-1-01
-01-9-01
-01-11-01
-01-10-01
-01-7-01
-02-AS09-
-02-AS08-
-01-8-01
-02-AS05-
-01-3-01
-02-RS11-
-02-RS12-
-02-AS03-
-02-AS07-
01
01
01
01
01
01
01
01
01
/a —
IPTYPE
BS
BS
BT
BT
BT
BT
BS
BT
BS
BT
BT
BT
BS
BS
BS
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
TOX
TOX
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
TOX
SURV
77.
53 .
80.
90.
100.
22.
61.
88.
78.
3.
12.
47.
72.
82.
85,
96.
0.
92,
33,
82,
82
58
20
89
24
62
0
0
0
42
17
1
60
75
1
82
94
94
24
42
0
90
93
52
82
86
90
100
26
40
50
80
00
00
00
00
50
70
80
00
00
,00
,50
.50
,00
.10
.00
,50
.30
.50
.50
.00
.00
.00
.30
.30
.00
.00
.00
.50
.50
.30
.30
.00
.30
.70
.70
.00
.00
.30
.00
.00
.30
.50
.50
.70
.70
.00
.00
.00
TOXS
NT
TX
NT
NT
NT
TX
TX
NT
NT
TX
TX
TX
NT
NT
NT
NT
TX
NT
TX
NT
NT
TX
TX
NT
TX
NT
TX
TX
TX
TX
TX
TX
TX
NT
TX
NT
NT
NT
TX
TX
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
GROW
2.
2.
0.
0.
5.
15.
2.
2.
3,
2
1
2
2
1
4
4
3
0
5
0
0
5
22
4
0
1
3
0
0
6
29
2
10
01
43
66
78
.00
.71
.61
.20
.02
.98
.45
.62
.96
.17
.07
.03
.72
.06
.36
.53
.35
.00
.64
.50
.32
.78
.33
.42
.17
.00
.73
TOXG
NT
NT
NT
NT
NT
TX
NT
ND
NT
TX
NR
NR
NT
NT
NT
ND
NR
NT
ND
ND
NT
ND
ND
ND
ND
ND
ND
NR
ND
TX
TX
ND
ND
NT
ND
NT
NT
NT
TX
ND
ND
NT
NT
TX
TX
NT
NT
NT
TX
TX
-------
CONC
0.
0,
0,
0,
0.
0.
0.
0.
0
0
.00
.01
.01
.01
.02
.08
.12
.13
.22
.24
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i = JJ.*4 LI
SAMP;
CON2
BR7
BR8
BR9
BR6
BR5
BR4
BR3
BR1
BR2
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=TBT UNITS=ug/g
i/a —
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
88.
81.
93,
90.
91.
95.
85.
90,
90.
80.
,70
,30
,80
,00
,30
,00
.00
,00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
3
3
3
4
3
3
4
4
.70
.82
.88
.94
.88
.09
.96
.99
.12
.12
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0,
0.
0.
0.
0.
0
0
0
0
0
.00
.00
.01
.01
.01
.02
.02
.03
.04
.06
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
- IMUPU-UlJi:
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
!i=J-LD V-J
SAMP:
BR8
CON2
BR6
BR7
BR9
BR4
BR5
BR3
BR2
BR1
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=DBT UNITS=ug/g
i/y
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
93.
88.
91.
81.
90,
85.
95,
90,
80
90
80
70
30
,30
,00
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
3
3
3
3
4
3
4
4
.88
.70
.88
.82
.94
.96
.09
.99
.12
.12
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
.00
.00
.00
.00
,00
.01
.01
.01
.01
.01
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
- wuncuui
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i=Jlb U!
SAMP:
BR4
BR7
BR8
BR9
CON2
BR1
BR2
BR3
BR5
BR6
i/a
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
85.
81.
93 .
90.
88,
90.
80,
90,
95,
91.
,00
.30
.80
.00
.70
.00
.00
.00
.00
.30
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
3.
3 ,
3,
4.
4.
3.
4.
3.
.96
.82
.88
.94
.70
.12
.12
.99
.09
.88
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0
0
0
0
0
0,
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2
.06
.06
.08
.12
.19
.20
.20
.22
.24
.25
.26
.27
.35
.42
.44
.47
.48
.57
.70
.75
.78
.82
.95
.65
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NC
SG
NE
NE
NE
NE
NE
SG
*
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
0 . 8 MCGEE
MCGEE
1 . 0 MCGEE
1 . 1 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1 . 8 MCGEE
2 . 1 MCGEE
MCGEE
NUMCOUK =
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
= J99 CHI
SAMP:
BR4
WSl
WS2
TB3
BR1
BR5
BR8
BR9
BR3
CON2
AR5
AR4
KL1
KL3
PR4
AR1
BR6
KL2
KL4
BR2
AR2
AR3
KL5
BR7
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=SEMAVS UNITS=' '
1PTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
NOT
SURV
85.
86.
78.
73 ,
90.
95.
93 .
90.
90.
88.
76.
85.
61.
78.
25.
38.
91.
82.
72,
80
77.
53.
61.
81.
00
30
.80
,80
00
00
,80
,00
.00
.70
.30
,00
.30
.80
.00
.80
.30
.50
.50
.00
,50
.80
.50
.30
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
NT
NT
NT
NT
NT
TX
TX
NT
GROW
3.
2
2
2
4.
4
3
3
3
3
2
1
2
2
2
1
3
2
2
4
2
2
2
3
.96
.58
.61
.39
.12
.09
.88
.94
.99
.70
.68
.96
.00
.61
.15
.96
.88
.62
.45
.12
.10
.01
.71
.82
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.
0.
0.
0.
0,
0.
0.
0.
0,
.08
.08
,11
,16
,18
,18
.20
.22
.22
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
H
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
J4 L.H&I
SAM:
BR5
BR7
BR6
BR2
BR3
BR4
BR9
BR1
BR8
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=12-2CLBNZ UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
95.
81.
91.
80.
90.
85.
90,
90.
93.
.00
.30
.30
.00
.00
.00
.00
.00
.80
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
4
3
3
4
3
3
3
4
3
.09
.82
.88
.12
.99
.96
.94
.12
.88
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0.
0.
0.
0.
0.
0.
0,
0,
0.
.05
.05
,08
.11
.12
.13
,15
,15
.28
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
IN
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
urn-vji/Ci = fi u
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
3 l-tllM
SAM]
BR5
BR7
BR6
BR2
BR4
BR9
BR3
BR8
BR1
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
=403 CHEMCODE=13-2CLBNZ UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
95
81
91
80
85
90
90
93
90
.00
.30
.30
.00
.00
.00
.00
.80
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
4
3
3
4
3
3
3
3
4
.09
.82
.88
.12
.96
.94
.99
.88
.12
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0
0,
0
0.
0
0
0.
0
0
.01
.01
.01
.02
.02
.02
.03
.04
.05
EFFECT RATIO STUDY TEST SAM
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
BR5
BR6
BR7
BR2
BR8
BR9
BR4
BR1
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=NAPTHALENE UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
95.
91.
81.
80.
93.
90.
85.
90.
90.
.00
.30
.30
.00
.80
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
4,
3.
3.
4.
3,
3.
3,
4.
3.
.09
.88
.82
.12
.88
.94
.96
.12
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.
0.
0.
0.
0.
0.
0.
0.
0.
02
04
,04
.05
.06
.07
.08
.08
.11
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MUFll-UUCi-1
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
UD ^1
SAM]
BR7
BR5
BR6
BR9
BR8
BR2
BR3
BR4
BR1
NUMCODE=406 CHEMCODE=ACENA UNITS=u
'a/y
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
95.
91.
90.
93
80
90
85
90
.30
.00
.30
.00
.80
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
4.
3.
3
3
4
3
3
4
.82
.09
.88
.94
.88
.12
.99
.96
.12
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.
0.
0.
0.
0.
0.
0.
0.
0.
08
12
15
16
,17
.17
.19
.19
.19
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
l»ll_UUE* = *4 U
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i cncw
SAM:
BR7
BR6
BR3
BR5
BR2
BR9
BR1
BR4
BR8
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
91.
90.
95.
80.
90.
90,
85.
93.
.30
.30
.00
.00
,00
.00
.00
.00
.80
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3.
3.
4.
4.
3.
4.
3.
3.
.82
.88
.99
.09
.12
.94
.12
.96
.88
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.
0.
0.
0.
0,
0.
0
0
0
.03
.05
.06
.07
.07
.09
.11
.11
.12
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
UIMLULT*31* V
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
jo \^ncj\
SAM:
BR7
BR6
BR5
BR8
BR9
BR4
BR1
BR3
BR2
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=408 CHEMCODE=FLUORENE UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
91
95
93
90
85
90
90
80
.30
.30
.00
.80
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
4
3
3
3
4
3
4
.82
.88
.09
.88
.94
.96
.12
.99
.12
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0
0
0
0
0
0
0
0
0
.12
.19
.19
.20
.32
.33
.33
.43
.43
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
wu
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
lMLUL)t; = 4U!
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i (JHEMi
SAM:
BR7
BR8
BR9
BR6
BR2
BR1
BR3
BR4
BR5
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
ME no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=PHENANTHRN UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81
93
90
91
80
90
90
85
95
.30
.80
.00
.30
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3
3.
3.
3
4.
4.
3.
3,
4,
.82
.88
.94
.88
.12
.12
.99
.96
,09
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.
0.
0
0,
0,
0,
0
0
0
.12
.18
.19
.19
.28
.30
.32
.36
.40
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
l'IV_l_M_'Ej=1 J. I
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
i i_ncii't»
SAM]
BR7
BR9
BR6
BR8
BR3
BR2
BR1
BR5
BR4
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG-1 | SG 1-2 I * 2-4 I **>4
NUMCODE=410 CHEMCODE=ANTHRACENE UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
90.
91.
93,
90.
80.
90.
95.
85
30
.00
.30
,80
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3,
3,
3
3
3
4
4
4
3
.82
.94
.88
.88
.99
.12
.12
.09
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0.
0.
0.
0.
0.
0.
0.
0.
0
07
12
12
14
.22
.24
.25
.29
.36
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
nu
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1'1UWUC! = 1 JLJ
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
L i.ndi*i'
SAM!
BR7
BR8
BR9
BR6
BR2
BR1
BR5
BR3
BR4
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=411 CHEMCODE=FLUORANTHN UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
93.
90
91
80.
90
95
90
85
.30
.80
.00
.30
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3.
3
3
4
4
4
3
3
.82
.88
.94
.88
.12
.12
.09
.99
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0.
0.
0.
0.
0.
0
0
0
0
.07
.12
,12
.13
.25
.27
.31
.43
.44
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1^UPJU\JUC. = ** J
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
L^ Lm
SAM]
BR7
BR8
BR9
BR6
BR2
BR1
BR5
BR4
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
412 CHEMCODE=PYRENE UNITS=ug/g
1U/U
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
93.
90.
91.
80
90
95
85
90
.30
.80
.00
.30
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3
3
3
3
4
4
4
3
3
.82
.88
.94
.88
.12
.12
.09
.96
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.
0.
0.
0.
0.
0,
0.
0,
0
.08
10
.15
.17
.29
.30
.33
.38
.43
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
JCi=f±1.3 »
SAM]
BR6
BR7
BR9
BR8
BR2
BR1
BR5
BR4
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=413 CHEMCODE=BAA UNITS=ug/g
i/y —
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
91.
81.
90.
93.
80.
90.
95.
85.
90.
30
30
.00
.80
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3.
3.
3,
4.
4
4
3
3
.88
.82
.94
.88
.12
.12
.09
.96
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0
0
0
0
0
0
0
0,
0
.04
.08
.08
.08
.09
.11
.12
.15
.19
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
N
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
UM<_OUt;-41
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
4 LHEI
SAM
BR7
BR2
BR8
BR9
BR6
BR1
BR5
BR4
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=CHRYSENE UNITS=ug/g
SAMPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
80.
93 ,
90.
91.
90.
95.
85.
90.
.30
.00
,80
.00
.30
.00
. 00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3
4
3.
3
3
4
4
3.
3
.82
.12
.88
.94
.88
.12
.09
.96
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0.
0.
0.
0.
0.
0
0
0
0
.06
.10
.10
.12
.13
.17
.17
.19
.31
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
- 11UI'I\-»JL
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
JCj = >± ±3 '
SAM:
BR7
BR8
BR9
BR6
BR2
BR1
BR4
BR5
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=415 CHEMCODE=BBF UNITS=ug/g
i/y —
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
93 .
90.
91.
80.
90.
85.
95
90
.30
.80
.00
.30
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3
3
3
3
4
4
3
4
3
.82
.88
.94
.88
.12
.12
.96
.09
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0
0
0.
0.
0.
0
0
0
0
.04
.06
.07
.08
.09
.09
.10
.10
.17
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
- wumcui
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
-lCi = 'i-Lt> '
SAM:
BR7
BR9
BR6
BR8
BR1
BR2
BR4
BR5
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CHEMCODE=BKF UNITS=ug/g
i/y —
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
90.
91.
93.
90.
80
85
95
90
.30
.00
.30
,80
,00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3,
3
3 ,
3,
4,
4
3
4
3
.82
.94
.88
.88
,12
.12
.96
.09
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.
0,
0.
0.
0
0
0
0
0
.04
,06
.07
.07
.08
.09
.09
.09
.13
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
JC* = t J. / >
SAM!
BR7
BR9
BR6
BR8
BR2
BR1
BR4
BR5
BR3
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=417 CHEMCODE=BAP UNITS=ug/g
i/y —
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
90.
91.
93.
80.
90.
85.
95.
90
.30
.00
.30
.80
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
3
3
4
4
3
4
3
.82
.94
.88
.88
.12
.12
.96
.09
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.
0.
0.
0.
0.
0.
0.
0.
0.
01
02
02
02
03
03
.03
.03
.03
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE ,
lX\JI,'l\*\SLSCt-
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
-•* j. y \*i
SAMI
BR7
BR2
BR5
BR9
BR1
BR3
BR4
BR6
BR8
NUMCODE=419 CHEMCODE=BGHIP UNITS=ug/g
iy/y
1PTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
80.
95.
90.
90.
90
85
91
93
.30
.00
.00
.00
.00
.00
.00
.30
.80
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
4.
4,
3.
4.
3
3.
3
3
.82
12
,09
.94
.12
.99
.96
.88
.88
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
0.
0.
0.
0.
0.
0.
0.
0.
0
.01
,02
.02
.02
.02
.02
.02
.03
.04
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
HUPH_Ul-'Ei = «i
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
&\> i_j
SAM]
BR7
BR1
BR2
BR5
BR6
BR8
BR9
BR4
BR3
420 CHEMCODE=BBKF UNITS=ug/g
i/u —
IPTYPE
BS
BS
BS
BS
BS
BS
BS
BS
BS
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81,
90
80
95
91
93
90
85
90
.30
.00
.00
.00
.30
.80
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
4.
4.
4,
3,
3,
3,
3
3
,82
.12
.12
.09
.88
.88
.94
.96
.99
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
1.05
1.24
1.99
2.44
2.56
2.94
3.06
3.60
3.60
3.60
3.60
3.60
3.92
3.97
4.03
4 .60
4.60
4.60
4.60
6.30
6.50
6.50
6.50
6.50
7.20
8.70
9.60
9.80
10.30
11.60
13.20
14.20
14.40
15.00
15.00
15.00
15.00
15.10
15.30
16.00
16.00
16.00
16.00
16.10
19.00
19.00
19.00
19.00
20.00
20.00
20.00
20.00
25.70
EFFECT
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
SG
NE
NE
SG
NE
SG
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
*
NE
NE
NC
NE
NE
NE
NE
NC
NE
RATIO STUDY
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
DAY
DAY
0 . 5 MCGEE
DAY
DAY
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
1 . 3 MCGEE
MCGEE
MCGEE
1 . 7 MCGEE
MCGEE
1 . 9 MCGEE
DAY
DAY
0 . 0 DAY
DAY
MCGEE
MCGEE
DAY
DAY
DAY
DAY
2 . 1 MCGEE
DAY
DAY
0 . 0 DAY
DAY
DAY
DAY
DAY
0 . 4 DAY
DAY
- NUMCODE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
CR14
HA28
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
=450 CHI
SAMP:
CON2
BR7
BR6
BR9
BR8
BR2
BR5
CM22
CM22
PR4
CM22
CM22
BR4
BR1
BR3
CM17
CM17
CM17
CM17
WS2
CM15
CM15
CM15
CM15
WS1
TB3
AR5
KL5
KL4
TB1
AR3
KL3
AR1
CM09
CM09
CM09
CM09
AR2
KL2
CM01
CM01
CM01
CM01
KL1
CM07
CM07
CM07
CM07
CM05
CMOS
CM05
CMOS
VS01
uy/y
MPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
SURV
88.70
81.30
91.30
90.00
93.80
80.00
95.00
82.70
93.30
25.00
100.00
37.00
85.00
90.00
90.00
80.00
94.70
94.00
40.00
78.80
86.70
88.00
94 .00
43 .00
86.30
73.80
76.30
61.50
72.50
87.50
53 .80
78.80
38.80
75.30
93 .30
90.00
44 .00
77.50
82.50
84.00
89.30
96.00
34.00
61.30
82.70
85.60
89.00
31.00
84.00
86.70
100.00
31.00
84 .00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.70
3.82
3.88
3.94
3.88
4.12
4.09
0.42
0.87
2.15
4.61
150.00
3.96
4.12
3.99
0.46
0.49
2.03
73.00
2.61
0.50
0.54
3.30
102.00
2.58
2.39
2.68
2.71
2.45
2.96
2.01
2.61
1.96
0.46
0.67
3.39
113.00
2.10
2.62
0.31
0.56
5.07
102.00
2.00
0.47
0.74
4.58
123.00
0.36
0.50
5.16
37.00
0.43
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
TX
NT
-------
CONC
25.70
25.70
25.70
28.30
38.30
38.30
38.30
38.30
50.00
50.00
50.00
50.00
95.00
95.00
95.00
95.00
106.00
106.00
106.00
106.00
278.00
278.00
278.00
278.00
469.00
469.00
469.00
469.00
1302.00
1302.00
1302.00
1302.00
4012.00
4012.00
4012.00
4012.00
EFFECT
NE
NC
NE
NE
NE
NE
NC
NC
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
*
NC
**
NE
NE
NE
**
**
**
NE
* *
RATIO
0.0
0.1
0.7
0.9
0.2
3.3
0.8
8.2
22.9
24.6
28.4
70.5
STUDY
DAY
DAY
DAY
MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
iiurn-wuci = '±
TEST
HA28
HS28
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
o\j v,nr
(c
SAMPI
VS01
VS01
VS01
AR4
VS03
VS03
VS03
VS03
SL02
SL02
SL02
SL02
CM11
CM11
CM11
CM11
CMOS
CMOS
CMOS
CMOS
CM06
CM06
CM06
CM06
VS07
VS07
VS07
VS07
SL07
SL07
SL07
SL07
SL06
SL06
SL06
SL06
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=450 CHEMCODE=PAH-T UNITS=u
(continued)
ly/y --
1PTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
NOT
TOX
SURV
88.
94.
26.
85.
89.
97.
90.
21.
77.
89.
98.
16.
72.
96.
100
45
85
93
100
37
78
97
100
45
78
0
4
24
71
82
98
15
76
78
98
19
00
00
00
00
30
30
00
.00
.80
.30
.00
.00
.00
.00
.00
.00
.30
.30
.00
.00
.90
.30
.00
.00
.70
.00
.00
.00
.10
.70
.00
.00
.00
.70
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
TX
NT
TX
NT
TX
GROW
0.
0.
30.
1.
0.
0.
0.
22.
0.
0.
3.
147.
0.
0.
4
91
0
0
5
102
0
0
6
96
0
0
-0
7
0
0
5
152
0
0
4
131
61
19
00
96
33
42
.01
.00
.39
.69
.15
.00
.39
.53
.15
.00
.42
.67
.42
.00
.40
.63
.54
.00
.29
.00
.08
.00
.41
.95
.98
.00
.18
.58
.24
.00
TOXG
NT
TX
NT
NT
NT
NT
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
NT
NR
NR
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
-------
CONC
0
0
0
0
0
0
0
0
1
1
.36
.44
.55
.56
.88
.89
.93
.99
.04
.68
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
NUMt,UDE=
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
=4bl LHi
SAMP:
BR7
CON2
BR5
BR6
BR9
BR2
BR4
BR8
BR3
BR1
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NCcl | NG=1 | SG 1-2 | * 2-4 | **>4
451 CHEMCODE=PAH-L UNITS=ug/g
>a/y --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
81.
88
95.
91.
90.
80
85.
93
90.
90,
.30
.70
.00
.30
.00
.00
.00
.80
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3.
4.
3.
3.
4.
3.
3.
3.
4,
.82
.70
.09
.88
.94
.12
.96
.88
.99
.12
1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONC
0.
0
1
1
1
2
2
2
2
2
.61
.88
.43
.57
.59
.05
.29
.51
.99
.99
EFFECT RATIO STUDY
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
nUl'H-WUIi*
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
= ij^ <_ni
SAMP:
CON2
BR7
BR6
BR9
BR8
BR2
BR1
BR5
BR3
BR4
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=452 CHEMCODE=PAH-H UNITS=ug/g
iy/9 --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
NOT
SURV
88.
81.
91
90
93
80
90
95
90
85
.70
.30
.30
.00
.80
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
GROW
3.
3
3.
3,
3.
4.
4
4
3
3
.70
.82
.88
.94
.88
.12
.12
.09
.99
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG = 1 | SG 1-2 | * 2-4 | **>4
NUMCODE=507 CHEMCODE=PCB 1260 UNITS=ug/g
CONC EFFECT RATIO STUDY TEST SAMPLE SAMPTYPE TOXIC SURV TOXS GROW TOXG
0.00 NE . JFLD CT15 1117-01-SED-9-01 BT NOT 64.00 NT 2.59 NT
0.00 NE . JFLD HA28 1117-01-SED-9-01 BT NOT 74.00 NT 0.10 NT
0.01 NC . JFLD CT15 1117-01-SED-2-01 BT TOX 28.00 TX 0.25 TX
0.01 NC . JFLD HA28 1117-01-SED-2-01 BT TOX 0.00 TX . ND
0.03 NC . JFLD CT15 1117-01-SED-3-01 BT TOX 14.00 TX 0.19 TX
0.03 NC . JFLD HA28 1117-01-SED-3-01 BT TOX 0.00 TX . ND
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.07
0.07
0.07
0.07
0.07
0.10
0.10
0.10
0.10
0.12
0.12
0.12
0.12
0.15
0.15
0.15
0.15
0.17
0.17
0. 17
0.17
0.17
0.17
0.17
0.17
0.20
0.20
0.20
0.20
0.25
0.30
0.39
0.45
0.47
0.47
0.47
0.47
0.49
0.50
0.51
0.53
0.53
0.53
0.53
0.53
0.61
0.65
0.66
0.71
0.77
1.88
1.88
1.88
EFFECT
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
NC
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NE
NC
NE
NE
SG
SG
SG
SG
NE
NE
NE
RATIO STUDY
DAY
DAY
0 . 1 MCGEE
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 0 DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
DAY
0 . 0 DAY
DAY
DAY
0 . 0 DAY
DAY
MCGEE
MCGEE
MCGEE
MCGEE
DAY
DAY
DAY
DAY
MCGEE
MCGEE
MCGEE
DAY
DAY
MCGEE
0 . 0 DAY
DAY
MCGEE
1 . 0 MCGEE
1 . 1 MCGEE
1 . 1 MCGEE
1 . 2 MCGEE
DAY
DAY
DAY
nuiTi\-wi-'c*=-j
TEST
CR14
HA28
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
CR14
HA28
HA28
HS28
HS28
TT28
TT28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
HA28
CR14
HA28
HS28
TT28
HA28
HA28
HA28
CR14
HA28
HA28
HS28
TT28
HA28
HA28
HA28
HA28
HA28
CR14
HA28
HS28
UO v-ni:
SAMPI
CM22
CM22
PR4
CM22
CM22
CMOS
CMOS
CMOS
CMOS
CM15
CM15
CM15
CM15
CM09
CM09
CMC 9
CM09
CMOS
CM17
CMOS
CM17
CMOS
CM17
CM17
CMOS
CM07
CM07
CM07
CM07
TB3
WS2
WS1
KL3
CM06
. CM06
CM06
CM06
AR5
AR2
KL4
CM11
CM11
KL2
CM11
CM11
TB1
KL1
KL5
AR1
AR3
CM01
CM01
CM01
508 CHEMCODE=PCB-T UNITS=ug/g
SAMPTYPE TOXIC SURV TOXS GROW TOXG
BT NOT 82.70 NT 0.42 NT
BT NOT 93.30 NT 0.87 NT
BT TOX 25.00 TX 2.15 NT
BT NOT 100.00 NT 4.61 NT
BT NOT 37.00 NT 150.00 NT
BT NOT 85.30 NT 0.42 NT
BT NOT 93.30 NT 0.67 NT
BT NOT 100.00 NT 5.42 NT
BT NOT 37.00 NT 102.00 NT
BT NOT 86.70 NT 0.50 NT
BT NOT 88.00 NT 0.54 NT
BT NOT 94.00 NT 3.30 NT
BT NOT 43.00 NT 102.00 NT
BT NOT 75.30 NT 0.46 NT
BT NOT 93.30 NT 0.67 NT
BT TOX 90.00 NT 3.39 TX
BT NOT 44.00 NT 113.00 NT
BT NOT 84.00 NT 0.36 NT
BT NOT 80.00 NT 0.46 NT
BT NOT 86.70 NT 0.50 NT
BT NOT 94.70 NT 0.49 NT
BT NOT 100.00 NT 5.16 NT
BT NOT 94.00 NT 2.03 NT
BT NOT 40.00 NT 73.00 NT
BT TOX 31.00 NT 37.00 TX
BT NOT 82.70 NT 0.47 NT
BT NOT 85.60 NT 0.74 NT
BT TOX 89.00 NT 4.58 TX
BT NOT 31.00 NT 123.00 NT
BT NOT 73.80 NT 2.39 NT
BT NOT 78.80 NT 2.61 NT
BT NOT 86.30 NT 2.58 NT
BT NOT 78.80 NT 2.61 NT
BT NOT 78.90 NT 0.40 NT
BT NOT 97.30 NT 0.63 NT
BT NOT 100.00 NT 6.54 NT
BT NOT 45.00 NT 96.00 NT
BT NOT 76.30 NT 2.68 NT
BT NOT 77.50 NT 2.10 NT
BT NOT 72.50 NT 2.45 NT
BT NOT 72.00 NT 0.39 NT
BT NOT 96.00 NT 0.53 NT
BT NOT 82.50 NT 2.62 NT
BT TOX 100.00 NT 4.15 TX
BT NOT 45.00 NT 91.00 NT
BT NOT 87.50 NT 2.96 NT
BT TOX 61.30 TX 2.00 NT
BT TOX 61.50 TX 2.71 NT
BT TOX 38.80 TX 1.96 NT
BT TOX 53.80 TX 2.01 NT
BT NOT 84.00 NT 0.31 NT
BT NOT 89.30 NT 0.56 NT
BT NOT 96.00 NT 5.07 NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect I NC<1 I NG=1 i SG 1-2 I * 2-4 I **>4
CONG
1,
2.
142.
142.
142.
142.
226.
226,
226,
226,
283,
283.
283.
283.
.88
,20
.00
.00
.00
.00
.00
,00
,00
.00
.00
.00
.00
.00
EFFECT
NE
NE
NE
NE
NE
**
NE
NE
**
**
NE
NE
* *
NE
RATIO STUDY
DAY
MCGEE
DAY
DAY
DAY
5 . 0 DAY
DAY
DAY
12.5 DAY
7 . 9 DAY
DAY
DAY
15.6 DAY
DAY
NUMCODE;
TEST
TT28
HA28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
CR14
HA28
HS28
TT28
-508 CHI
(i
SAMP!
CM01
AR4
SL04
SL04
SL04
SL04
VS03
VS03
VS03
VS03
VS01
VS01
VS01
VS01
(continued)
ly/y --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
NOT
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
SURV
34
85
73
90
96
21
89
97
90
21
84
88
94
26
.00
.00
.30
.00
.70
.00
.30
.30
.00
.00
.00
.00
.00
.00
TOXS
NT
NT
NT
NT
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
GROW
102
1
0
0
4
109
0,
0
0
22
0
0
0
30
.00
.96
.50
.59
.41
.00
.33
.42
.01
.00
.43
.61
.19
.00
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NOMCODE=703 CHEMCODE=6CL-CHX-B UNITS=ug/g
CONC EFFECT RATIO STUDY TEST SAMPLE SAMPTYPE TOXIC SURV TOXS GROW TOXG
0.00 NC . JFLD CT15 1117-01-SED-2-01 BT TOX 28.00 TX 0.25 TX
0.00 NC . JFLD CT15 1117-01-SED-3-01 BT TOX 14.00 TX 0.19 TX
0.00 NC . JFLD HA28 1117-01-SED-2-01 BT TOX 0.00 TX . ND
0.00 NC . JFLD HA28 1117-01-SED-3-01 BT TOX 0.00 TX . ND
-------
CONC
0.
0.
0.
0.
0.
0,
0.
0.
0.
0
0.
0,
0.
0
0
.01
.01
.01
.02
.03
.06
,09
.09
.10
.11
.11
.12
.14
.14
.15
EFFECT
NE
NE
NC
NE
NE
NE
NE
NE
SG
NE
SG
NE
*
*
NE
wu
RATIO STUDY
MCGEE
MCGEE
0 . 1 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1 . 4 MCGEE
MCGEE
1 . 6 MCGEE
MCGEE
2 . 0 MCGEE
2 . 0 MCGEE
MCGEE
FJl_UUC,= /Ul
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
> t-nwn
SAM:
TB3
WSl
PR4
WS2
TB1
AR5
AR2
AR4
KL1
KL2
AR3
KL3
AR1
KL5
KL4
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
706 CHEMCODE=CHLORDAN-G UNITS=ug/g
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
SURV
73,
86,
25.
78.
87.
76,
77,
85.
61,
82
53
78,
38,
61
72
.80
.30
.00
.80
.50
.30
.50
.00
.30
.50
.80
.80
.80
.50
.50
TOXS
NT
NT
TX
NT
NT
NT
NT
NT
TX
NT
TX
NT
TX
TX
NT
GROW
2,
2
2
2.
2.
2
2
1
2
2
2
2
1
2
2
,39
.58
.15
.61
.96
.68
.10
.96
.00
.62
.01
.61
.96
.71
.45
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
CONG
0.01
0.03
0.04
0.04
0.06
0.06
0.06
0.07
0.08
0.08
0.08
0.08
0.09
0.12
0.16
EFFECT
NC
NE
NE
NC
NE
NE
NE
NE
NE
SG
SG
SG
NE
NE
NE
RATIO STUDY
0 . 1 MCGEE
MCGEE
MCGEE
0 . 5 MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
MCGEE
1 . 0 MCGEE
1 . 0 MCGEE
1 . 0 MCGEE
MCGEE
MCGEE
MCGEE
TEST
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
HA28
SAM!
PR4
WS2
WS1
KL1
AR2
AR5
KL3
KL2
KL4
AR1
AR3
KL5
TB3
AR4
TB1
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
NUMCODE=710 CHEMCODE=DDT UNITS=ug/g
,/g ---
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
NOT
TOX
NOT
NOT
NOT
NOT
NOT
TOX
TOX
TOX
NOT
NOT
NOT
SORV
25.
78.
86.
61.
77.
76.
78
82
72
38
53
61
73
85
87
.00
,80
.30
.30
.50
.30
.80
.50
.50
.80
.80
.50
.80
.00
.50
TOXS
TX
NT
NT
TX
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
NT
GROW
2.
2.
2.
2.
2.
2.
2
2
2
1
2
2
2
1
2
15
.61
.58
.00
.10
.68
.61
.62
.45
.96
.01
.71
.39
.96
.96
TOXG
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
43.
48.
53,
62.
75,
76
82
86.
90
90
90
91
95
96
.00
.00
,00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NC
NE
NC
NC
NE
NE
SG
NE
NC
NE
SG
SG
NE
NE
RATIO
0.
0.
0.
1.
0,
1,
1
5
7
8
.0
.9
.1
.2
LV\JFt\~WCi= yu i. v-nc*rn-WL'Ci = r-v-.L r xi
STUDY TEST SAMPLE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT10
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-02-AS07-
-02-AS06-
-02-AS08-
-02-AS09-
-02-RS11-
-02-AS12-
-02-RS01-
-02-RS13-
-02-AS03-
-02-AS05-
-02-RS07-
-02-RS12-
-02-RS14-
-02-RS15-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
UWJ. li>=pCIlL
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
TOX
TOX
NOT
NOT
SURV
40.
82.
17,
42,
90,
92
60
72
82
75
60
52
77
85
.00
.50
,50
,50
,00
.50
.00
.50
.50
.00
.00
.50
.50
.00
TOXS
TX
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
TX
NT
NT
GROW
2.
4.
0.
3.
4.
4,
4.
3,
3
5
3
1
4
4
73
07
.72
.03
.64
.17
.44
.20
.78
.06
.76
.32
.34
.59
TOXG
TX
NT
TX
TX
NT
NT
NT
NT
TX
NT
NT
TX
NT
NT
-------
" SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
4.70
4.70
21.10
21.10
31.00
31.00
113.00
113.00
167.00
189.00
201.00
226.00
249.00
508.00
1410.00
1710.00
1770.00
1840.00
3940.00
12000.00
21900.00
25000.00
EFFECT
NE
NE
NE
NE
NC
NC
NE
NE
NC
NE
NC
NE
NE
NE
NC
NE
NC
NC
NC
NE
NE
* *
RATIO STUDY
JFLD
JFLD
JFLD
JFLD
0 . 7 JFLD
0 . 7 JFLD
JFLD
JFLD
0 . 0 JFLD
JFLD
0 . 0 JFLD
JFLD
JFLD
JFLD
0 . 2 JFLD
JFLD
0 . 3 JFLD
0 . 3 JFLD
0 . 6 JFLD
JFLD
JFLD
110.6 JFLD
11Ul"H_V_/iyE»— 3
TEST
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT10
SAMPLE
1117-01-SED-12-01
1117-01-SED-12-01
1117-01-SED-9-01
1117-01-SED-9-01
1117-01-SED-3-01
1117-01-SED-3-01
1117-01-SED-16-01
1117-01-SED-16-01
1111-02-RS01-01
1111-02-RS13-01
1111-02-RS07-01
1111-02-RS15-01
1111-02-RS14-01
1111-02-AS06-01
1111-02-AS09-01
1111-02-AS12-01
1111-02-RS12-01
1111-02-AS08-01
1111-02-AS07-01
1111-02-RS11-01
1111-02-AS05-01
1111-02-AS03-01
iy/y --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
TOX
TOX
NOT
NOT
TOX
SURV
79.
94.
64.
74.
14.
0.
84.
80.
60.
72
60
85
77
82
42
92
52
17
40
90
75
82
00
00
00
.00
.00
.00
.00
.00
.00
.50
.00
.00
.50
.50
.50
.50
.50
.50
.00
.00
.00
.50
TOXS
NT
NT
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
NT
GROW
2.
0.
2.
0.
0.
2.
0.
4
3
3
4
4
4
3
4
1
0
2
4
5
3
16
18
59
.10
.19
,55
.11
.44
.20
.76
.59
.34
.07
.03
.17
.32
.72
.73
.64
.06
.78
TOXG
NT
NT
NT
NT
TX
ND
NT
NT
NT
NT
NT
NT
NT
NT
TX
NT
TX
TX
TX
NT
NT
TX
-------
NUMCODE=903 CHEMCODE=ANTIM01
CONC
10
10
11
11
11
11
11
14
14
19
22
24
25
128
.00
.30
.30
.50
.60
.70
.70
.00
.10
.50
.50
.30
.20
.00
EFFECT
NE
NE
NE
NE
NC
NC
NC
NC
NE
NE
NE
*
SG
**
RATIO
0
0
0
1
2
1
8
.8
.8
.8
.0
.1
.7
.8
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
TEST
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
SAMPLE
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-02
-02
-02
-02
-02
-02
-02
-02
-02
-02
-02
-02
-02
-02
-RS14
-AS12
-RS11
-RS15
-AS09
-RS01
-RS12
-RS07
-RS13
-AS05
-AS06
-AS03
-AS08
-AS07
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
-01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NCd | NG=1 | SG 1-2 | * 2-4 | **>4
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
NOT
TOX
TOX
TOX
SURV
77.
92
90
85
42
60
52
60
72
75
82
82
17
40
.50
.50
.00
.00
.50
.00
.50
.00
.50
.00
.50
.50
.50
.00
TOXS
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
TX
GROW
4.
4.
4.
4.
3.
4.
1.
3.
3.
5,
4.
3.
0.
2.
.34
.17
.64
.59
.03
.44
.32
.76
,20
.06
.07
.78
.72
.73
TOXG
NT
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
TX
TX
TX
-------
CONC
25.20
25.
85.
85.
110.
110.
206.
206.
257.
257.
1050.
1310,
1550.
1810.
2010
2020
2230
2620
3110
3210
3300
4190
5310
11300
20
90
90
00
00
00
00
00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
EFFECT
NE
NE
NE
NE
NC
NC
SG
SG
NE
NE
NC
NC
NC
NC
NE
NC
NE
NE
NE
NC
NC
NE
NE
NE
RATIO
0.
0.
1.
1.
0.
0.
0.
0.
0
0
0
9
9
7
7
.2
.3
.7
.4
.4
.7
.7
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
iNui"Juwuci=r
TEST
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
CT10
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
I UH \_nC*lMV_»~'l-'E* = t-*Vl_H^ J.U1"!
SAMPLE
1117-01-SED-12-01
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
Ol-SED-12-01
Ol-SED-9
Ol-SED-9
Ol-SED-2
Ol-SED-2
Ol-SED-3
Ol-SED-3
-01
-01
-01
-01
-01
-01
Ol-SED-16-01
Ol-SED-16-01
02-AS07-
02-AS08-
02-AS03-
02-RS12-
02-RS11-
02-AS09-
02-RS15-
02-RS14-
02-RS13-
02-RS01-
02-RS07-
02-AS05-
02-AS06-
02-AS12-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CALCIUM UNITS=ug/g
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
NOT
SURV
79.
94.
64.
74.
28.
0.
14.
0.
84.
80.
40.
17,
82.
52.
90.
42.
85.
77.
72.
60,
60.
75.
82.
92.
00
00
00
00
00
00
00
00
00
.00
.00
,50
.50
.50
.00
.50
.00
.50
.50
.00
.00
.00
.50
.50
TOXS
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
TX
TX
NT
TX
NT
TX
NT
NT
NT
TX
TX
NT
NT
NT
GROW
2,
0,
2.
0.
0.
0.
2
0
2
0
3
1
4
3
4
4
3
4
3
5
4
4
,16
,18
.59
.10
.25
.19
.55
.11
.73
.72
.78
.32
.64
.03
.59
.34
.20
.44
.76
.06
.07
.17
TOXG
NT
NT
NT
NT
TX
ND
TX
ND
NT
NT
TX
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
8.
8,
9.
10.
10.
11.
12.
15.
15.
15.
18.
24.
38.
55,
.10
.20
.80
.00
.80
.30
.60
.40
.60
.60
.90
.00
.40
.60
EFFECT
NE
NC
NC
NC
NC
NE
NE
NC
NE
NC
NE
NE
NE
*
RATIO
0
0
0
0
0
0
3
.4
.5
.5
.6
.8
.9
.0
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
NUMCODE=905 CHEMCODE=COBAL'
TEST SAMPLE
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
CT10
CT14
CT14
CT14
1111-02-AS12-01
1111-02-AS07-01
1111-02-AS09-01
1111-02-AS08-01
1111-02-RS01-01
1111-02-AS06-01
1111-02-RS13-01
1111-02-AS03-01
1111-02-RS14-01
1111-02-RS07-01
1111-02-RS15-01
1111-02-AS05-01
1111-02-RS11-01
1111-02-RS12-01
iy/y --
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
SURV
92,
40.
42
17
60.
82.
72.
82
77
60.
85.
75.
90
52
.50
.00
.50
.50
.00
.50
.50
.50
.50
.00
.00
.00
.00
.50
TOXS
NT
TX
TX
TX
TX
NT
NT
NT
NT
TX
NT
NT
NT
TX
GROW
4.
2,
3,
0
4,
4,
3.
3
4
3,
4.
5.
4
1
.17
.73
.03
.72
.44
.07
.20
.78
.34
.76
.59
.06
.64
.32
TOXG
NT
TX
TX
TX
NT
NT
NT
TX
NT
NT
NT
NT
NT
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 **>4
CONC
17.30
17.30
84.80
84.80
111.00
111.00
238.00
238.00
586.00
586.00
1160.00
1430.00
3620.00
3960.00
4290.00
4780.00
6000.00
6090.00
6170.00
6240.00
6250.00
6780.00
6900.00
8250.00
EFFECT
NE
NE
NE
NE
NC
NC
SG
SG
NE
NE
NC
NC
NC
NE
NC
NE
NE
NE
SG
NE
SG
NE
NE
SG
RATIO
0.5
0.5
1.0
1.0
0.2
0.2
0.6
0.7
1.1
1.1
1.4
r
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
iunt-UUCi=y UD Lnai"i\-uijii=r'uvjwej£>.LU(u] UPJlTti=uy/g
TEST SAMPLE SAMPTYPE
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
CT10
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
1117-01-SED- 12-01
1117-01-SED-12-01
1117-01-SED-9-01
1117-01-SED-9-01
1117-01-SED-2-01
1117-01-SED-2-01
1117-01-SED-3-01
1117-01-SED-3-01
1117-01-SED-16-01
1117-01-SED-16-01
1111-02-AS07-01
1111-02-AS08-01
1111-02-AS03-01
1111-02-AS06-01
1111-02-AS09-01
1111-02-AS05-01
1111-02-RS15-01
1111-02-RS13-01
1111-02-RS07-01
1111-02-RS11-01
1111-02-RS01-01
1111-02-RS14-01
1111-02-AS12-01
1111-02-RS12-01
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
NOT
TOX
SURV
79.00
94.00
64.00
74.00
28.00
0.00
14.00
0.00
84.00
80.00
40.00
17.50
82.50
82.50
42.50
75.00
85.00
72.50
60.00
90.00
60.00
77.50
92.50
52.50
TOXS
NT
NT
NT
NT
TX
TX
TX
TX
NT
NT
TX
TX
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
TX
GROW
2.16
0.18
2.59
0.10
0.25
0.19
2.55
0.11
2.73
0.72
3.78
4.07
3.03
5.06
4.59
3.20
3.76
4.64
4 .44
4.34
4.17
1.32
TOXG
NT
NT
NT
NT
TX
ND
TX
ND
NT
NT
TX
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
-------
CONG
58.30
58.30
113.00
113.
142
142
218.
218.
254,
254.
421
598
968.
1170.
1190
1250.
1740.
2250.
2260.
2550.
3120,
3600.
3640.
4560.
.00
.00
.00
.00
,00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
,00
,00
,00
,00
EFFECT
NE
NE
NC
NC
NE
NE
SG
SG
NE
NE
NC
NC
NE
NC
NE
NC
NE
NE
NE
SG
SG
NE
NE
it
RATIO
0.7
0
1
1
0
0.
0.
0
1 ,
1.
2.
.7
.4
.4
.2
.3
.6
.3
.3
.6
.3
NUMCODE=907 CHEMCODE=POTASSIU1
STUDY TEST SAMPLE
JFLD CT15 1117-01-SED-16-01
JFLD HA28 1117-01 -SED-16-01
JFLD CT15 1117-01-SED-2-01
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
CT14
CT14
CT14
CT10
CT14 .
CT14
CT14
CT14
CT14
CT14
CT10
CT14
1117
1117
1117
1117
1117
1117
1117
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-Ol-SED-2
-01-SED-
-01-SED-
-01-SED-
-01-SED-
9
9
3
3
-01
-01
-01
-01
-01
-01-SED- 12-01
-Ol-SED-12-01
-02-AS08
-02-AS07
-02-AS06
-02-AS09
-02-AS12
-02-AS03
-02-AS05
-02-RS14
-02-RS13
-02-RS01
-02-RS07
-02-RS11
-02-RS15
-02-RS12
_
_
-
-
_
_
-
-
_
-
_
-
_
-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
TOX
NOT
NOT
TOX
SURV
84.
80.
28.
0,
64.
74.
14.
0.
79.
94.
17.
40.
82.
42.
92.
82.
75.
77.
72.
60,
60,
90.
85.
52,
.00
.00
.00
.00
.00
.00
.00
.00
.00
.00
.50
.00
.50
.50
.50
.50
.00
.50
.50
.00
.00
.00
,00
,50
TOXS
NT
NT
TX
TX
NT
NT
TX
TX
NT
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
TX
TX
NT
NT
TX
GROW
2.
0.
0.
2,
0.
0,
2,
0
0
2
4
3
4
3.
5
4
3
4.
3.
4.
4.
1.
.55
.11
.25
.59
.10
.19
.16
.18
.72
.73
.07
.03
.17
.78
.06
.34
.20
.44
.76
.64
.59
.32
TOXG
NT
NT
TX
ND
NT
NT
TX
ND
NT
NT
TX
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
:=SODIUM UNITS-ug/g
CONG
158.
172.
251.
260.
341.
435.
464.
591.
731.
1490.
1770.
1840.
1980.
2140.
00
00
00
00
00
00
00
00
00
00
.00
.00
.00
.00
EFFECT
NC
NC
NE
NC
NC
NE
NE
NE
NE
*
NE
*
NE
*
RATIO
0.
0.
0.
0.
2.
2.
2
2
1
4
5
.0
.5
.9
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
TEST
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
CT14
*uo ^nc.pi^wL'c.— OWI^.LUI
SAMPLE
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
02-AS08-
02-AS03-
02-AS05-
02-AS09-
02-AS07-
02-AS12-
02-AS06-
02-RS14-
02-RS13-
02-RS07-
02-RS15-
02-RS01-
02-RS11-
02-RS12-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
ly/y
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
NOT
TOX
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
SURV
17.
82.
75.
42.
40.
92.
82.
77.
72.
60.
85,
60,
90.
52.
.50
.50
.00
.50
.00
.50
,50
.50
,50
.00
.00
.00
.00
.50
TOXS
TX
NT
NT
TX
TX
NT
NT
NT
NT
TX
NT
TX
NT
TX
GROW
0
3
5
3
2
4
4
4
3
3
4
4
4
1
.72
.78
.06
.03
.73
.17
.07
.34
.20
.76
.59
.44
.64
.32
TOXG
TX
TX
NT
TX
TX
NT
NT
NT
NT
NT
NT
NT
NT
TX
-------
CONC
0.80
0.
4.
4.
5.
5.
8.
8.
23.
23.
39.
46.
48,
50.
50.
51.
53.
54
63.
65.
75
82
85.
103
80
40
40
30
30
20
20
.20
.20
.30
.90
.40
.60
.60
.80
.50
.60
.50
.40
.90
.10
.50
.00
EFFECT
NE
NE
NC
NC
NE
NE
NC
NC
NE
NE
NC
NE
NC
NC
NE
NC
NC
NC
NE
NE
NE
NE
NE
SG
RATIO
0.
0.
0.
0.
0.
0.
0,
0
0
0
1
.5
.5
8
.8
.6
.1
.9
.8
.8
.8
.5
i>
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
TEST
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT15
HA28
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
SAMPLE
1117-01-SED-12-01
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1117-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
1111-
Ol-SED-12-01
Ol-SED-2
Ol-SED-2
Ol-SED-9
Ol-SED-9
Ol-SED-3
Ol-SED-3
-01
-01
-01
-01
-01
-01
Ol-SED-16-01
Ol-SED-16-01
02-AS07-
02-RS13-
02-AS09-
02-AS03-
02-AS12-
02-AS08-
02-RS01-
02-RS07-
02-RS14-
02-RS15-
02-RS11-
02-AS06-
02-AS05-
02-RS12-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect j NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
ONITS=ug/g
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
NOT
TOX
TOX
NOT
NOT
TOX
TOX
NOT
NOT
TOX
NOT
TOX
TOX
NOT
TOX
TOX
TOX
NOT
NOT
NOT
NOT
NOT
TOX
SORV
79.
94.
28.
0.
64.
74.
14.
0.
84.
80.
40.
72.
42.
82.
92.
17.
60.
60
77.
85.
90
82
75
52
00
00
00
00
00
00
00
00
00
00
.00
.50
.50
.50
,50
.50
.00
.00
.50
.00
.00
.50
.00
.50
TOXS
NT
NT
TX
TX
NT
NT
TX
TX
NT
NT
TX
NT
TX
NT
NT
TX
TX
TX
NT
NT
NT
NT
NT
TX
GROW
2.
0.
0.
2.
0.
0.
2.
0.
2.
3.
3.
3.
4.
0
4.
3.
4
4
4
4
5
1
16
18
25
59
10
19
.55
11
.73
.20
.03
.78
.17
.72
.44
.76
.34
.59
.64
.07
.06
.32
TOXG
NT
NT
TX
ND
NT
NT
TX
ND
NT
NT
TX
NT
TX
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONC
0.61
0.64
0.80
0.80
0.85
0.90
0.93
1.00
1.00
1.10
1.50
1.60
1.80
1.90
2.40
3.10
EFFECT
NC
NC
NE
NE
NE
NC
NE
NC
NE
NC
NE
SG
NE
NE
NE
*
RATIO
0.4
0.5
0.6
0.5
0.8
1.1
2.2
IN
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
TEST
CT14
CT14
CT15
HA28
CT14
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT10
CT14
CT14
L3
SAMPLE
1111-02-AS08-01
1111-02-AS07-01
1117-01-SED-16-01
1117-01-SED-16-01
1111-02-AS12-01
1111-02-AS09-01
1111-02-AS06-01
1111-02-AS03-01
1111-02-RS13-01
1111-02-RS01-01
1111-02-RS14-01
1111-02-RS07-01
1111-02-AS05-01
1111-02-RS15-01
1111-02-RS11-01
1111-02-RS12-01
uwirt>=ug/g -
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
TOX
NOT
NOT
NOT
TOX
NOT
TOX
NOT
TOX
NOT
TOX
NOT
NOT
NOT
TOX
SURV
17.50
40.00
84.00
80.00
92.50
42.50
82.50
82.50
72.50
60.00
77.50
60.00
75.00
85.00
90.00
52.50
TOXS
TX
TX
NT
NT
NT
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
TX
GROW
0.72
2.73
2.55
0.11
4.17
3.03
4.07
3.78
3.20
4.44
4.34
3.76
5.06
4.59
4.64
1.32
TOXG
TX
TX
NT
NT
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
NT
TX
-------
CONG
1
1
1
1
1
1
1.
1.
1.
1.
1.
1.
2
2.
.10
.10
.20
.30
.30
.30
.40
.40
.40
.50
.50
.50
.00
.30
EFFECT
NE
NC
NE
NE
NE
NC
SG
NC
NC
NE
NE
SG
SG
NE
RATIO
0,
0.
1.
0.
0.
1.
1.
.7
.9
.1
.9
.9
.0
3
NUMCODE=920 CHEMCODE=THALLII
STUDY TEST SAMPLE
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
CT14
CT14
CT14
CT10
CT14
CT14
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-02-RS14-
-02-RS07-
-02-AS12-
-02-RS15-
-02-RS11-
-02-RS01-
-02-AS03-
-02-AS09-
-02-RS12-
-02-AS06-
-02-RS13-
-02-AS08-
-02-AS07-
-02-AS05-
01
01
01
01
01
01
01
01
01
01
01
01
01
01
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG-1 | SG 1-2 | * 2-4 | **>4
SAMPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
NOT
TOX
NOT
NOT
NOT
TOX
TOX
TOX
TOX
NOT
NOT
TOX
TOX
NOT
SURV
77.
60.
92.
85.
90.
60.
82.
42.
52.
82.
72.
17.
40.
75.
.50
.00
.50
.00
.00
.00
.50
.50
.50
.50
.50
.50
.00
.00
TOXS
NT
TX
NT
NT
NT
TX
NT
TX
TX
NT
NT
TX
TX
NT
GROW
4.
3
4.
4
4.
4.
3.
3.
1,
4.
3,
0.
2.
5.
.34
.76
.17
.59
.64
.44
.78
.03
.32
.07
.20
.72
.73
.06
TOXG
NT
NT
NT
NT
NT
NT
TX
TX
TX
NT
NT
TX
TX
NT
-------
SAMPLE COLLECTIONS SORTED BY CONCENTRATION
NE no effect | NC<1 | NG=1 | SG 1-2 | * 2-4 | **>4
CONG
6.
6.
6.
6.
6.
6.
6.
6.
7,
7
7
7
7
8
70
80
80
,80
.80
.90
.90
.90
.00
.00
.10
.40
.70
.20
EFFECT
NC
NE
NC
NC
NC
NE
NG
NE
NE
NE
NE
SG
NE
SG
RATIO
0.
1.
1.
1.
1 (
1
1
9
.0
.0
.0
.0
.0
.2
STUDY
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
JFLD
TEST
CT14
CT14
CT14
CT14
CT14
CT10
CT10
CT14
CT14
CT14
CT14
CT14
CT14
CT14
SAMPLE
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
1111
-02-AS08-
-02-AS05-
-02-AS07-
-02-RS07-
-02-RS12-
-02-RS15-
-02-AS03-
-02-RS14-
-02-RS11-
-02-RS13-
-02-AS12-
-02-RS01-
-02-AS06-
01
01
01
01
01
01
01
01
01
01
01
01
01
-02-AS09-01
IPTYPE
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
BT
TOXIC
TOX
NOT
TOX
TOX
TOX
NOT
TOX
NOT
NOT
NOT
NOT
TOX
NOT
TOX
SURV
17.
75.
40.
60.
52.
85.
82.
77.
90.
72.
92,
60.
82
42
50
00
00
00
50
00
.50
.50
.00
.50
.50
.00
.50
.50
TOXS
TX
NT
TX
TX
TX
NT
NT
NT
NT
NT
NT
TX
NT
TX
GROW
0.
5.
2,
3.
1,
4.
3
4
4
3
4
4
4
3
.72
.06
,73
.76
,32
.59
.78
.34
.64
.20
.17
.44
.07
.03
TOXG
TX
NT
TX
NT
TX
NT
TX
NT
NT
NT
NT
NT
NT
TX
------- |