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Table 35. Chemicals Detected in the Sediment in the Scarboro Community
Substance Name |
Minimum (ppm) |
Maximum (ppm) |
Average (ppm) |
Number of Times Detected |
Sample Total |
Comparison Value |
Source |
Maximum Above CV? |
---|---|---|---|---|---|---|---|---|
Inorganics |
||||||||
Aluminum |
5,830 |
21,000 |
10,000 |
4 |
5 |
100,000 |
IEMEG |
No |
Antimony |
0.0507 |
0.0949 |
0.073 |
2 |
5 |
20 |
RMEG |
No |
Arsenic |
1.62 |
5.17 |
3.7 |
4 |
5 |
0.5 |
CREG |
Yes |
Barium |
76.4 |
91.4 |
81 |
4 |
5 |
4,000 |
RMEG |
No |
Beryllium |
0.576 |
0.977 |
0.75 |
4 |
5 |
100 |
CEMEG |
No |
Cadmium |
0.124 |
0.29 |
0.22 |
4 |
5 |
10 |
CEMEG |
No |
Chromium |
14.3 |
26.6 |
20.6 |
4 |
5 |
200 |
RMEG (CrVI) |
No |
Cobalt |
7.91 |
15 |
9.8 |
4 |
5 |
500 |
IEMEG |
No |
Copper |
7.29 |
17.4 |
10 |
4 |
5 |
2,000 |
IEMEG |
No |
Iron |
12,500 |
23,900 |
20,700 |
4 |
5 |
23,000 |
Residential RBC |
Yes |
Lead |
9 |
101 |
32.5 |
4 |
5 |
400 |
Soil Screening Level |
No |
Manganese |
542 |
680 |
590 |
4 |
5 |
3,000 |
RMEG |
No |
Nickel |
9.3 |
16.1 |
11 |
4 |
5 |
1,000 |
IEMEG |
No |
Selenium |
0.936 |
1.13 |
1.03 |
2 |
5 |
300 |
CEMEG |
No |
Thallium |
0.23 |
0.31 |
0.27 |
2 |
5 |
5.5 |
Residential RBC |
No |
Vanadium |
15.7 |
33 |
23 |
4 |
5 |
200 |
IEMEG |
No |
Zinc |
51.7 |
94 |
74 |
4 |
5 |
20,000 |
CEMEG |
No |
Organics |
||||||||
Benzoic acid |
0.206 |
0.206 |
0.206 |
1 |
8 |
200,000 |
RMEG |
No |
Bromoform |
0.0022 |
0.0022 |
0.0022 |
1 |
5 |
90 |
CREG |
No |
cis-Chlordane |
0.0005 |
0.002 |
0.0015 |
3 |
5 |
2 |
CREG (chlordane) |
No |
Di-n-butyl phthalate |
0.54 |
0.54 |
0.54 |
1 |
5 |
5,000 |
RMEG |
No |
gamma-Chlordane |
0.00075 |
0.0017 |
0.0014 |
3 |
5 |
2 |
CREG (chlordane) |
No |
Essential nutrients (calcium, magnesium, potassium, and sodium) are not included in the table.
CEMEG = chronic environmental media evaluation guide
IEMEG = intermediate environmental media evaluation guide
CREG = cancer risk evaluation guide
ppm = parts per million
CrVI = chromium VI
RBC = risk-based concentration
CV = comparison value
RMEG = reference dose media evaluation guide
Table 36. Chemicals Detected in the Surface Water in the Scarboro Community
Substance Name |
Minimum (ppb) |
Maximum (ppb) |
Average (ppb) |
Number of Times Detected |
Sample Total |
Comparison Value |
Source |
Maximum Above CV? |
---|---|---|---|---|---|---|---|---|
Inorganics |
||||||||
Aluminum |
261 |
1,640 |
798 |
4 |
5 |
20,000 |
IEMEG |
No |
Antimony |
0.21 |
0.21 |
0.21 |
1 |
5 |
4 |
RMEG |
No |
Arsenic |
0.83 |
0.88 |
0.86 |
2 |
5 |
0.023 |
CREG |
Yes |
Barium |
17.6 |
106 |
68 |
4 |
5 |
700 |
RMEG |
No |
Beryllium |
0.06 |
0.06 |
0.06 |
2 |
5 |
20 |
CEMEG |
No |
Chromium |
2.36 |
2.56 |
2.46 |
2 |
5 |
100 |
LTHA |
No |
Cobalt |
0.36 |
0.96 |
0.8 |
4 |
5 |
100 |
IEMEG |
No |
Copper |
1.83 |
3.16 |
2.5 |
2 |
5 |
300 |
IEMEG |
No |
Iron |
565 |
1,160 |
765 |
4 |
5 |
10,950 |
RBC |
No |
Lead |
0.48 |
1.06 |
0.77 |
2 |
5 |
0 |
MCLG |
Yes |
Manganese |
39.4 |
292 |
170 |
4 |
5 |
500 |
RMEG |
No |
Nickel |
1.87 |
2.73 |
2.3 |
2 |
5 |
100 |
LTHA |
No |
Selenium |
2.04 |
2.04 |
2.04 |
1 |
5 |
50 |
CEMEG |
No |
Silver |
0.105 |
0.14 |
0.12 |
2 |
5 |
50 |
RMEG |
No |
Vanadium |
1.87 |
2.48 |
2.2 |
2 |
5 |
30 |
IEMEG |
No |
Zinc |
3.93 |
12.4 |
8.2 |
2 |
5 |
3,000 |
CEMEG |
No |
Organics |
||||||||
Butyl benzyl phthalate |
15.8 |
15.8 |
15.8 |
1 |
5 |
2,000 |
RMEG |
No |
Di-n-butyl phthalate |
11.7 |
31.4 |
21.5 |
2 |
9 |
1,000 |
RMEG |
No |
Toluene |
5 |
5 |
5 |
1 |
5 |
200 |
IEMEG |
No |
Essential nutrients (calcium, magnesium, potassium, and sodium) are not included in the table.
CEMEG = chronic environmental media evaluation guide for drinking water
MCLG = maximum contaminant level goal for drinking water
CREG = cancer risk evaluation guide for drinking water
ppb = parts per billion
CV = comparison value
RBC = risk-based concentration for tap water
IEMEG = intermediate environmental media evaluation guide for drinking water
RMEG = reference dose media evaluation guide
LTHA = lifetime health advisory for drinking water
Table 37. Estimated Exposure Doses for Chemicals in Scarboro Compared to Noncancer Screening Guidelines
Substance Name |
Maximum Concentration (ppm) |
2nd Tier Screening Conc. |
Estimated Exposure Dose (mg/kg/day) |
Acute Screening Guideline (mg/kg/day) |
Source |
Chronic Screening Guideline (mg/k/day) |
Source |
Does the Estimated Exposure Dose Exceed the Noncancer Screening Guideline? |
||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Pica |
Child |
Adult |
Pica |
Child |
Adult |
|||||||
Surface Soil |
||||||||||||
Arsenic |
6.39 |
6.03 |
4.6E-04 |
7.4E-05 |
3.4E-06 |
0.005 |
AMRL |
0.0003 |
CMRL |
No |
No |
No |
gamma-Chlordane |
2.8 |
3.01 |
2.0E-04 |
3.7E-05 |
1.7E-06 |
0.001 |
Acute MRL (chlordane) |
0.0006 |
CMRL |
No |
No |
No |
Heptachlor epoxide |
0.97 |
1.20 |
6.9E-05 |
1.5E-05 |
6.9E-07 |
0.008 |
Tox profile* |
0.000013 |
RfD |
No |
Yes |
No |
Iron |
29,700 |
25,600 |
149 mg/day |
3.1E-01 |
1.5E-02 |
10 mg/day |
DRI |
0.3 |
RfD |
Yes |
Yes |
No |
Sediment |
||||||||||||
Arsenic |
5.17 |
5.25 |
NA |
1.3E-06 |
2.5E-07 |
NA |
NA |
0.0003 |
CMRL |
NA |
No |
No |
Iron |
23,900 |
26,200 |
NA |
6.6E-03 |
1.2E-03 |
NA |
NA |
0.3 |
RfD |
NA |
No |
No |
Surface Water |
||||||||||||
Arsenic |
0.88 |
0.0009 |
NA |
1.1E-06 |
2.1E-07 |
NA |
NA |
0.0003 |
CMRL |
NA |
No |
No |
Lead |
1,160 |
0.0012 |
NA |
1.5E-06 |
2.8E-07 |
NA |
NA |
0.02 |
Acute LOAEL |
NA |
No |
No |
Soil doses were calculated using the following formulas:
pica dose = (maximum concentration×0.005 kg/day×52 days/year×3 years)/(10 kg×(365 days/year×3 years))
child dose = (second-tier screening concentration×0.0002 kg/day×291.2 days/year×6 years)/(13 kg×(365 days/year×6 years))
adult dose = (second-tier screening concentration×0.00005 kg/day×291.2 days/year×30 years)/(70 kg×(365 days/year×30 years))
Sediment doses were calculated using the following formulas:
child dose = (second-tier screening concentration×0.0001 kg/day×12 days/year×6 years)/(13 kg×(365 days/year×6 years))
adult dose = (second-tier screening concentration×0.0001 kg/day×12 days/year×30 years)/(70 kg×(365 days/year×30 years))
Surface water doses were calculated using the following formulas:
child dose = (second-tier screening concentration×0.5 L/day×12 days/year×6 years)/(13 kg×(365 days/year×6 years))
adult dose = (second-tier screening concentration×0.5 L/day×12 days/year×30 years)/(70 kg×(365 days/year×30 years))
* The acute screening guideline was derived from limited acute toxicological data available in ATSDR's toxicological profile. A safety factor of 1,000 was applied. These acute screening guidelines should be considered unofficial and are for use in this health assessment only.
AMRL = acute minimal risk level mg/kg/day = milligram per kilogram per day
CMRL = chronic minimal risk level NA = not applicable
conc. = concentration ppm = parts per million
DRI = dietary reference intake RfD = reference dose
LOAEL = lowest-observed-adverse-effect level
Table 38. Estimated Exposure Doses for Chemicals in Scarboro Compared to Cancer Screening Guidelines
Substance Name |
2nd Tier Screening Concentration (ppm) |
Estimated Lifetime Exposure Dose (mg/kg/day) |
EPA’s Oral Cancer Slope Factor (mg/kg/day)-1 |
Risk |
Does the Estimated Exposure Dose Exceed the Cancer Screening Guideline (10-4)? |
---|---|---|---|---|---|
Surface Soil |
|||||
Arsenic |
6.03 |
1.5E-06 |
1.5 |
2.2E-06 |
No |
gamma-Chlordane |
3.01 |
7.4E-07 |
0.35 |
2.6E-07 |
No |
Heptachlor epoxide |
1.20 |
2.9E-07 |
9.1 |
2.7E-06 |
No |
Iron |
25,600 |
Evaluated for noncarcinogenic effects (see Table 37) |
|||
Sediment |
|||||
Arsenic |
5.25 |
1.1E-07 |
1.5 |
1.6E-07 |
No |
Iron |
26,200 |
Evaluated for noncarcinogenic effects (see Table 37) |
|||
Surface Water |
|||||
Arsenic |
0.0009 |
9.0E-08 |
1.5 |
1.3E-07 |
No |
Lead |
0.0012 |
Evaluated for noncarcinogenic effects (see Table 37) |
Soil doses were calculated using the following formula:
lifetime dose = (second-tier screening concentration×0.00005 kg/day×291.2 days/year×70 years)/(70 kg×(365 days/year×70 years))
Sediment doses were calculated using the following formula:
lifetime dose = (second-tier screening concentration×0.0001 kg/day×12 days/year×70 years)/(70 kg×(365 days/year×70 years))
Surface water doses were calculated using the following formula:
lifetime dose = (second-tier screening concentration×0.5 L/day×12 days/year×70 years)/(70 kg×(365 days/year×70 years))
Risk was calculated by multiplying the exposure dose by EPA's oral cancer slope factor.
mg/kg/day = milligram per kilogram per day
ppm = parts per million
The Agency for Toxic Substances and Disease Registry (ATSDR) is a federal public health agency with headquarters in Atlanta, Georgia, and 10 regional offices throughout the United States. ATSDR's mission is to serve the public by using the best science, taking responsive public health actions, and providing trusted health information to prevent harmful exposures and diseases related to toxic substances. ATSDR is not a regulatory agency—unlike the U.S. Environmental Protection Agency (EPA), which is the federal agency that develops and enforces environmental laws to protect the environment and human health.
This glossary defines words used by ATSDR in communications with the public. It is not a complete dictionary of environmental health terms. If you have questions or comments, call ATSDR's toll-free telephone number, 1-800-CDC-INFO (1-800-232-4636).
Table B-1. Chemicals Detected in Off-Site Soil
Substance Name |
Average Concentration (ppm) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/ |
---|---|---|---|---|---|
Inorganics |
|||||
Thorium |
28 |
3.4E-04 |
0.6–18 ppm |
ATSDR/NCRP |
Yes |
Organics |
|||||
4-Aminobiphenyl |
3.4 |
3.4E-04 |
5 ppm |
FDA 21CFR74 |
No |
1-Bromo-4-phenoxy benzene |
1.2 |
4.2E-05 |
10 ppm |
ATSDR-benzene |
No |
bis(2-Chloroethoxy)methane |
1.2 |
1.5E-05 |
100 ppm |
PADEP |
No |
P-Chloro-m-cresol |
0.51 |
1.5E-05 |
1,000 ppm |
Anbesol Teething Gel |
No |
alpha-Chloronaphthalene |
4.1 |
6.3E-06 |
8.0E-02 mg/kg/day |
EPA RfD for beta-chloronaphthalene |
No |
4-Chlorophenyl phenyl ether |
1.1 |
5.0E-05 |
0.8 ppm |
TCEQ-TRRP for soil |
Yes |
Dibenz(a,j)acridine |
4.1 |
1.4E-05 |
1.4E-04 mg/kg/day |
Calculated from CalEPA TEF and EPA oral slope factor (benzo(a)pyrene) |
No |
p(Dimethylamino)azobenzene |
4.1 |
5.0E-05 |
2.2E-05 mg/kg/day |
Calculated from CalEPA oral unit risk factor |
Yes |
7,12-Dimethylbenz(a)anthracene |
4.1 |
5.0E-05 |
4.0E-07 mg/kg/day |
Calculated from CalEPA oral unit risk factor |
Yes |
Endosulfan sulfate |
0.022 |
5.0E-05 |
100 ppm |
CEMEG (endosulfan) |
No |
Endrin ketone |
0.022 |
2.7E-07 |
20 ppm |
CEMEG (endrin) |
No |
Ethyl methanesulfonate |
4.1 |
2.7E-07 |
100 ppm |
PADEP |
No |
2-Fluorophenol |
1.4 |
5.0E-05 |
1.6 ppm |
TCEQ-TRRP for soil as 2-chlorophenol |
No |
Methyl methanesulfonate |
4.1 |
1.7E-05 |
100 ppm |
PADEP as ethyl methanesulfonate |
No |
3-Methylcholanthrene |
4.1 |
5.0E-05 |
4.5E-06 mg/kg/day |
Calculated from CalEPA oral unit risk factor |
Yes |
beta-Naphthylamine |
6.9 |
5.0E-05 |
2.7 ppm |
TCEQ—media-specific concentration residential soil |
Yes |
The average concentrations are rounded. Averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest doses were calculated using the following formula:
child dose = (average concentration×0.0002 kg/day×291.2 days/year×6 years)/(13 kg×(365 days/year×6 years))
CalEPA = California Environmental Protection Agency
CEMEG = chronic environmental media evaluation guide
PHA = public health assessment
EPA = U.S. Environmental Protection Agency
ppm = parts per million
FDA = U.S. Food and Drug Administration
RfD = reference dose
mg/kg/day = milligram per kilogram per day
TEF = toxic equivalency factor
NCRP = National Council on Radiation Protection and Measurements
URF = unit risk factors
PADEP = Pennsylvania Department of Environmental Protection
TCEQ = Texas Commission on Environmental Quality
TRRP = Texas Risk Reduction Program
Table B-2. Chemicals Detected in Off-Site Sediment
Substance Name |
Average Concentration (ppm) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/ Concentration Exceed the Screening Guideline? |
---|---|---|---|---|---|
Inorganics |
|||||
Phosphate |
406 |
1.0E-04 |
FDA—generally recognized as safe |
No |
|
Silicon |
410 |
1.0E-04 |
Biologically inert |
No |
|
Thorium |
54 |
1.4E-05 |
0.6–18 ppm |
ATSDR/NCRP |
Yes |
Organics |
|||||
Acetic acid |
0.011 |
2.8E-09 |
40,000–80,000 ppm |
Vinegar |
No |
1-Bromo-4-phenoxy benzene |
0.77 |
1.9E-07 |
0.28 ppm |
TCEQ—TRRP as bromophenyl phenylether, -4 |
Yes |
Bis(2-chloroethoxy) methane |
0.77 |
1.9E-07 |
100 ppm |
PADEP |
No |
Carbon-14 |
19,000 |
4.8E-03 |
ATSDR—radiation dose screening PHA |
||
Chlorine atom |
18,000 |
4.6E-03 |
32 ppm |
TCEQ—TRRP for soil |
Yes |
p-Chloro-m-cresol |
0.77 |
1.9E-07 |
20 ppm |
ATSDR—EMEG 4-chlorophenol |
No |
4-Chlorophenyl phenyl ether |
0.77 |
1.9E-07 |
0.8 ppm |
TCEQ—TRRP for soil |
No |
Cyclotetrasiloxane |
0.027 |
6.8E-09 |
NJ value |
Data QA/QC |
No—presumptive evidence/ estimated value |
Dodacane |
0.0074 |
1.9E-09 |
NJ value |
Data QA/QC |
No—presumptive evidence/ estimated value |
Endosulfan sulfate |
0.45 |
1.1E-07 |
100 ppm |
CEMEG (endosulfan) |
No |
Endrin ketone |
0.46 |
1.2E-07 |
20 ppm |
CEMEG (endrin) |
No |
Hydrocarbon |
13 |
3.3E-06 |
880 ppm |
NM TPH screening guidelines |
No |
Nitrogen, kjeldahl |
1,600 |
4.0E-04 |
20,000 ppm |
EMEG (ammonia) |
No |
Total combustible organics |
198,000 |
5.0E-02 |
10 ppm |
EMEG (benzene) |
Yes |
Total petroleum hydrocarbons |
150 |
3.8E-05 |
880 ppm |
NM TPH screening guidelines |
No |
The average concentrations are rounded. Averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest doses were calculated using the following formula:
child dose = (average concentration×0.0001 kg/day×12 days/year×6 years)/(13 kg×(365 days/year×6 years))
CEMEG = chronic environmental media evaluation guide
NM = New Mexico
EMEG = environmental media evaluation guide
PHA = public health assessment
FDA = U.S. Food and Drug Administration
ppm = parts per million
mg/kg/day = milligram per kilogram per day
QA/QC = quality assurance/quality control
NCRP = National Council on Radiation Protection and Measurements
TPH = total petroleum hydrocarbons
PADEP = Pennsylvania Department of Environmental Protection
TRRP = Texas Risk Reduction Program
TCEQ = Texas Commission on Environmental Quality
Table B-3. Chemicals Detected in Off-Site Surface Water
Substance Name |
Average Concentration (ppb) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/ Concentration Exceed the Screening Guideline? |
---|---|---|---|---|---|
Inorganics |
|||||
Bicarbonate, dissolved |
180,000 |
2.3E-01 |
500,000 ppb |
Alkalinity EPA—SMCL |
No |
Cesium |
0.61 |
7.7E-07 |
1 ppb |
ATSDR background |
No |
Chloride |
119,000 |
5.1E-01 |
250,000 ppb |
EPA—SMCL |
No |
Silicon |
2,100 |
2.7E-03 |
Biologically inert |
No |
|
Sulfate |
625,000 |
3.1E+00 |
250,000 ppb |
EPA—SMCL |
No |
Sulfide |
4,000 |
5.1E-03 |
500 ppb |
Rotten egg odor in water |
Yes, as hydrogen sulfide |
Sulfur |
8,200 |
1.0E-02 |
250,000 ppb |
EPA—SMCL as sulfate |
No |
Organics |
|||||
bis(2-Chloroethoxy)methane* |
10 |
1.3E-05 |
5 ppb |
NYSDEC groundwater quality standard |
Yes |
Bromide* |
59 |
1.8E-04 |
300,000 ppb |
Secondary MCL for chloride |
No |
1-Bromo-4-phenoxy benzene* |
10 |
1.3E-05 |
5 ppb |
Benzene MCL |
Yes |
4-Chlorophenyl phenyl ether* |
10 |
1.3E-05 |
0.061 ppb |
TCEQ TRRP residential ground water (2 liters/day) |
Yes |
Orthophosphate* |
287 |
4.0E-04 |
Food grade chemical—added to drinking water to reduce lead leaching |
No |
|
p-Chloro-m-cresol* |
10 |
1.3E-05 |
1 ppb |
NYSDEC groundwater quality standard |
Yes |
Thorium* |
0.87 |
1.1E-06 |
ATSDR—Radiation Dose Screening PHA |
||
Tetraoxo-sulfate(1-) |
21,000 |
2.7E-02 |
250,000 ppb |
EPA—SMCL as sulfate |
No |
Total petroleum hydrocarbons |
1,050 |
1.3E-03 |
1,400 ppb |
New Mexico TPH screening guidelines |
No |
*Chemical was detected in less than 10% of the samples. The average concentration was estimated using 1/2 the detection limit for nondetected samples.
The average concentrations are rounded. Unless otherwise noted, averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest doses were calculated using the following formula:
child dose = ((average concentration/1,000)×0.5 liters/day×12 days/year×6 years)/(13 kg×(365 days/year×6 years))
EPA = U.S. Environmental Protection Agency
ppb = parts per billion
FDA = U.S. Food and Drug Administration
SMCL = secondary maximum contaminant level
MCL = maximum contaminant level
TCEQ = Texas Commission on Environmental Quality
mg/kg/day = milligram per kilogram per day
TPH = total petroleum hydrocarbons
NYSDEC = New York State Department of Environmental Conservation
TRRP = Texas Risk Reduction Program
Table B-4. Chemicals Detected in Fish Collected Off-Site
Substance Name |
Location |
Average Concentration (ppm) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/ Concentration Exceed the Screening Guideline? |
---|---|---|---|---|---|---|
Inorganics |
||||||
Lead |
Clinch River |
0.44 |
6.8E-04 |
2.0 ppm |
FDA 21CFR173 |
No |
WBR |
0.32 |
4.9E-04 |
2.0 ppm |
FDA 21CFR173 |
No |
|
Organics |
||||||
Endosulfan sulfate |
Clinch River |
0.075 |
1.2E-04 |
8.1 ppm |
RBC (endosulfan) |
No |
Endrin ketone |
Clinch River |
0.079 |
1.2E-04 |
0.41 ppm |
RBC (endrin) |
No |
WBR |
0.066 |
1.0E-04 |
No |
|||
Endrin aldehyde |
Clinch River |
0.011 |
1.7E-05 |
0.41 ppm |
RBC (endrin) |
No |
WBR |
0.021 |
3.2E-05 |
No |
|||
2,2’,3,4’,5’,6-Hexachloro-1,1’-biphenyl |
Clinch River |
0.031 |
4.8E-05 |
2.0E-05 mg/kg/day |
CMRL (Aroclor 1254) |
Yes for noncancer (No for cancer) |
WBR |
0.019 |
2.9E-05 |
Yes for noncancer (No for cancer) |
|||
3,3’,4,4’,5,5’-Hexachloro-1,1’-biphenyl |
WBR |
0.01 |
1.5E-05 |
2.0E-05 mg/kg/day |
CMRL (Aroclor 1254) |
No for cancer and noncancer |
Nonachlor, cis- |
Clinch River |
0.027 |
4.2E-05 |
0.0006 mg/kg/day |
CMRL (chlordane) |
No |
WBR |
0.017 |
2.6E-05 |
No |
|||
Nonachlor, trans- |
Clinch River |
0.047 |
7.2E-05 |
0.0006 mg/kg/day |
CMRL (chlordane) |
No |
WBR |
0.033 |
5.1E-05 |
No |
|||
Nonachlor, trans- |
Clinch River |
0.006 |
9.2E-06 |
0.0006 mg/kg/day |
CMRL (chlordane) |
No |
WBR |
0.0092 |
1.4E-05 |
No |
The average concentrations are rounded. Averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest doses were calculated using the following formula:
subsistence child dose = (average concentration×0.02 kg/day×365 days/year×6 years)/(13 kg×(365 days/year×6 years))
CMRL = chronic minimal risk level
FDA = U.S. Food and Drug Administration
mg/kg/day = milligram per kilogram per day
PCB = polychlorinated biphenyl
ppm = parts per million
RBC = risk-based concentration
WBR = Watts Bar Reservoir
Table B-5. Chemicals Detected in Off-Site Game
Substance Name |
Average Concentration (ppm) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/Concentration Exceed the Screening Guideline? |
---|---|---|---|---|---|
Organics |
|||||
Nonachlor, cis |
0.0055 |
4.2E-07 |
0.0006 mg/kg/day |
CMRL |
No |
Nonachlor, trans |
0.0051 |
3.9E-07 |
0.0006 mg/kg/day |
CMRL (chlordane) |
No |
The average concentrations are rounded. Averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest doses were calculated using the following formula:
child dose = (average concentration×0.001 kg/day×365 days/year×6 years)/(13 kg×(365 days/year×6 years))
CMRL = chronic minimal risk level
mg/kg/day = milligram per kilogram per day
ppm = parts per million
Screening guidelines are available for all chemicals detected in vegetation and air.
Table B-6. Chemicals Detected in Scarboro
Substance Name |
Average Concentration (ppm) |
Highest Dose (mg/kg/day) |
Surrogate Screening Guideline |
Surrogate Screening Guideline Source |
Does the Dose/Concentration Exceed the screening Guideline? |
---|---|---|---|---|---|
Soil |
|||||
Acetic acid |
0.012 |
1.4E-07 |
40,000–80,000 ppm |
Vinegar |
No |
alpha-Pinene |
0.045 |
5.5E-07 |
37.5 mg/kg/day lowest NOAEL |
EPA: Federal Register [FR Doc. 98-31063] (11/19/1998) |
No |
Benzene ethanamine |
0.0088 |
1.1E-07 |
0.1 mg/kg/day |
FDA—amphetamine pediatric dose of 10 mg/tablet |
No |
Cyclotetrasiloxane |
0.043 |
5.3E-07 |
NJ value |
Data QA/QC |
No—presumptive evidence/estimated value |
Sediment |
|||||
Acetic acid |
0.011 |
2.7E-09 |
40,000–80,000 ppm |
Vinegar |
No |
Cyclotetrasiloxane |
0.027 |
6.9E-09 |
NJ value |
Data QA/QC |
No—presumptive evidence/estimated value |
Dodacane |
0.0074 |
1.9E-09 |
NJ value |
Data QA/QC |
No—presumptive evidence/estimated value |
The average concentrations are rounded. Averages were calculated using detected concentrations only and do not take into account nondetected values.
Highest soil doses were calculated using the following formula:
non-pica child dose = (average concentration×0.0002 kg/day×291.2 days/year×6 years)/(13 kg×(365 days/year×6 years))
Highest sediment doses were calculated using the following formula:
child dose = (average concentration×0.0001 kg/day×12 days/year×6 years)/(13 kg×(365 days/year×6 years))
mg/kg/day = milligram per kilogram per day
ppm = parts per million
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