Appendix E
SECTION 1
Parameter | ||||
pH | 6.8 | 7.8 | ||
Nitrate (as N) | 51.1 | 1,700 | ||
Phosphate | 0.238 | 17.3 | ||
Suspended solids | 1 | 14 | ||
Oil and Grease | <1 | 11.9 | ||
Uranium | <0.02 | 0.128 | ||
Lead | <0.0012 | 0.0225 | ||
Nickel | <0.012 | <0.3 | ||
Silver | <0.0005 | <0.0025 | ||
Chromium | <0.02 | <0.1 | ||
Aluminum | <0.05 | 1.3 | ||
Copper | <0.004 | 0.03 | ||
Zinc | <0.01 | 0.085 | ||
Cyanide | <0.005 | <0.005 | ||
Cadmium | <0.01 | <0.05 | ||
Gross Alpha Radioactivity | 0.306k | 4.99k | ||
Nonvolatile (dissolved) Beta Radioactivity | 0.408k | 5.33k | ||
Tritium | 303k | 1,560k |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as a part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration
equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a unit of radioactivity; one trillionth
of a curie.
d. Limits imposed by SCDHEC NPDES Permit SC#0000175.
e. 1993 results reported to SCDHEC on the monthly Discharge Monitoring Report (DMR).
f. The minimum concentration was the minimum concentration found in samples analyzed in 1993. The maximum concentration is the highest single result found during the 1993 sampling events.
g. First number is the minimum acceptable pH while the second number is the maximum acceptable pH.
h. RR = measure and report.
i. First number represents the daily average limit while the second number represents the daily maximum limit.
j. Radioactive limits are not included on the NPDES Permit.
k. Collected near the mouth of Tim's Branch, downstream of M-Area.
pH | 6.4 | 9.0 | ||
Temperature | 14 | 30 | ||
BOD5 | <1 | 5 | ||
Nitrate (as N) | 1.78 | 66 | ||
Ammonia as Nitrogen | <0.01 | 0.15 | ||
Suspended Solids | <1 | 2 | ||
Oil and Grease | <1 | 10.1 | ||
Uranium | <0.02 | <0.1 | ||
Lead | <0.0005 | 0.0094 | ||
Nickel | <0.03 | <0.05 | ||
Mercury | <0.0001 | <0.0005 | ||
Chromium | <0.02 | <0.03 | ||
Aluminum | <0.05 | 0.053 | ||
Copper | <0.01 | 0.013 | ||
Zinc | <0.01 | 0.414 | ||
Manganese | <0.005 | 0.0343 | ||
Total Chlorine | <0.01 | 0.37 | ||
Gross Alpha Radioactivity | 0.53h | 3.90h | ||
Nonvolatile (dissolved) Beta Radioactivity | 0.497h | 3.94h | ||
Tritium | 607h | 13,200h | ||
Strontium-89,90 | 0.783h | |||
Uranium/Plutonium | 0.298h |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as a part of ongoing monitoring programs.
c. mg/L= milligrams per liter; a measure of concentration
equivalent to the weight/volume ratio.
pCi/L= picocuries per liter; a unit of radioactivity; one trillionth
of a curie.
d. Limits imposed by the SCDHEC NPDES Permit SC#0000175.
e. 1993 results reported to SCDHEC on the monthly Discharge Monitoring Report (DMR).
f. The minimum concentration is the minimum concentration found in samples analyzed in 1993. The maximum concentration is the highest single result found during the 1993 sampling events.
g First number is the minimum acceptable pH while the second number is the maximum acceptable pH.
h. Collected downstream of Outfall H-016 on Upper Three Runs near Road C.
i. First number represents the monthly average limit while the second number represents the daily maximum limit.
j. RR = measure and report.
k. Radioactive limits are not included on the NPDES Permit.
l. <DL = analytical result less than the test procedure detection limit.
Table E.1-3. Water quality in Beaver Creek Dam on SRS (calendar year 1992).a,b
Unit of measurec | MCLd,e or DCGf | Minimumg | Maximumg | |
Aluminum | mg/L | 0.05-0.2h | 3.59 | 4.14 |
Ammonia | mg/L | NAi,j | 0.048 | 0.40 |
Cadmium | mg/L | 0.005d | <0.00004 | 0.0025 |
Calcium | mg/L | NA | 2.68 | 4.41 |
Cesium-137 | pCi/L | 120 | ||
Chloride | mg/L | 250h | 2.4 | 8.6 |
Chromium | mg/L | 0.1d | <0.0004 | 0.0668 |
Copper | mg/L | 1.3k | <0.0004 | 0.014 |
Dissolved oxygen | mg/L | >5.0l | 5.8 | 10.0 |
Fecal coliform | Colonies per 100 ml | 1,000l | 3 | 22 |
Gross alpha radioactivity | pCi/L | 15d | <DL | 1.15 |
Iron | mg/L | 0.3h | 0.567 | 3.81 |
Lead | mg/L | 0.015k | <0.0004 | 0.015 |
Magnesium | mg/L | NA | 1.02 | 1.82 |
Manganese | mg/L | 0.05h | <0.0004 | 0.412 |
Nickel | mg/L | 0.1d,e | <0.0004 | 0.015 |
Nonvolatile (dissolved) beta radioactivity | pCi/L | 50d | 0.5 | 5.8 |
pH | pH units | 6.5-8.5h | 6.2 | 7.6 |
Phosphate | mg/L | NA | <0.01 | 1.5 |
Sodium | mg/L | NA | 3.83 | 10.6 |
Sulfate | mg/L | 250h | 3.98 | 13.1 |
Suspended solids | mg/L | NA | 1.0 | 31.8 |
Temperature | °C | 32.2m | 14.5 | 34 |
Tritium | pCi/L | 20,000d,e | 0.05 | 228 |
Zinc | mg/L | 5h | <0.0004 | 0.017 |
a. Sources: Wike et al. (1994); Cummins, Martin, and Todd (1991).
b. Parameters are those DOE routinely measures as a regulatory requirement or as part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a picocurie is a unit of radioactivity; one trillionth of a curie.
d. Maximum Contaminant Level (MCL), EPA National
Primary Drinking Water Standards (40 CFR Part 141).
See glossary.
e. Maximum Contaminant Level, SCDHEC (1976). See glossary.
f. DOE Derived Concentration Guides (DCGs) for water (DOE Order 5400.5). DCG values are based on committed effective doses of 4 millirem per year for consistency with drinking water MCL of 4 millirem per year. See glossary.
g. Minimum concentrations of samples taken at the downstream monitoring station. The maximum listed concentration is the highest single result found during one sampling event. Less than (<) indicates concentration below analysis detection limit (DL).
h. Secondary Maximum Contaminant Level (SMCL), EPA
National Secondary Drinking Water Regulations
(40 CFR Part 143).
i. NA = none applicable.
j. Depends on pH and temperature.
k. Action level for lead and copper.
l. WQS = water quality standard. See glossary.
m. Shall not exceed weekly average of 32.2°C (90°F) after mixing nor rise more than 2.8°C (5°F) in 1 week unless appropriate temperature criterion mixing zone has been established.
Table E.1-4. Water quality in Fourmile Branch on SRS (calendar year 1993).a,b
Unit of measurec | MCLd,e or DCGf | Minimumg | Maximumg | |
Aluminum | mg/L | 0.05-0.2h | 0.08 | 0.34 |
Ammonia | mg/L | NAi,j | NDk | 0.04 |
Cadmium | mg/L | 0.005d | ND | ND |
Calcium | mg/L | NA | 2.24 | 3.35 |
Cesium-137 | pCi/L | 120 | 8.44 | 19.4 |
Chemical oxygen demand | mg/L | NA | ND | ND |
Chloride | mg/L | 250h | 2 | 5 |
Chromium | mg/L | 0.1d | ND | ND |
Copper | mg/L | 1.3l | ND | ND |
Dissolved oxygen | mg/L | >5.0m | 6.4 | 11.3 |
Fecal coliform | Colonies per 100 ml | 1,000m | 23 | 440 |
Gross alpha radioactivity | pCi/L | 15d | 0.073 | 2.68 |
Iron | mg/L | 0.3h | 0.364 | 1.14 |
Lead | mg/L | 0.015l | ND | 0.003 |
Magnesium | mg/L | NA | 0.565 | 0.636 |
Manganese | mg/L | 0.05h | 0.079 | 0.104 |
Mercury | mg/L | 0.002d,e | ND | ND |
Nickel | mg/L | 0.1d | ND | ND |
Nitrite/Nitrate (as nitrogen) | mg/L | 10d | 1.42 | 2.85 |
Nonvolatile (dissolved) beta radioactivity | pCi/L | 50d | 20.5 | 43.5 |
pH | pH units | 6.5-8.5h | 5.7 | 7.7 |
Phosphate | mg/L | NA | ND | ND |
Sodium | mg/L | NA | 6.29 | 10.6 |
Strontium-89/90 | pCi/L | - | 10.3 | 15.3 |
Sulfate | mg/L | 250h | 4 | 9 |
Suspended solids | mg/L | NA | 2 | 9 |
Temperature | °C | 32.2n | 10 | 25.5 |
Total dissolved solids | mg/L | 500h | 40 | 78 |
Tritium | pCi/L | 20,000d,e | 33,600 | 68,900 |
Zinc | mg/L | 5h | ND | 0.011 |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a picocurie is a unit of radioactivity; one trillionth of a curie.
d. Maximum Contaminant Level (MCL), EPA National
Primary Drinking Water Standards (40 CFR Part 141).
See glossary.
e. Maximum Contaminant Level, SCDHEC (1976). See glossary.
f. DOE Derived Concentration Guides (DCGs) for water (DOE Order 5400.5). DCG values are based on committed effective doses of 4 millirem per year for consistency with drinking water MCL of 4 millirem per year. See glossary.
g. Minimum concentrations of samples taken at the downstream monitoring station. The maximum listed concentration is the highest single result found during one sampling event.
h. Secondary Maximum Contaminant Level (SMCL), EPA
National Secondary Drinking Water Regulations
(40 CFR Part 143).
i. NA = none applicable.
j. Depends on pH and temperature.
k. ND = none detected.
l. Action level for lead and copper.
m. WQS = water quality standard. See glossary.
n. Shall not exceed weekly average of 32.2°C (90°F) after mixing nor rise more than 2.8°C (5°F) in 1 week unless appropriate temperature criterion mixing zone has been established.
Table E.1-5. Water quality in Pen Branch on SRS (calendar year 1993).a,b
Unit of measurec | MCLd,e or DCGf | Minimumg | Maximumg | |
Aluminum | mg/L | 0.05-0.2h | 0.096 | 0.398 |
Ammonia | mg/L | NAi,j | NDk | 0.09 |
Cadmium | mg/L | 0.005d | ND | ND |
Calcium | mg/L | NA | 0.976 | 5.03 |
Chemical oxygen demand | mg/L | NA | ND | ND |
Chloride | mg/L | 250h | 3 | 10 |
Chromium | mg/L | 0.1d | ND | ND |
Copper | mg/L | 1.3l | 0.041 | 0.098 |
Dissolved oxygen | mg/L | >5.0m | 6.3 | 10.6 |
Fecal coliform | Colonies per 100 ml | 1,000m | 18 | 320 |
Gross alpha radioactivity | pCi/L | 15d | <DLn | 1.27 |
Iron | mg/L | 0.3h | 0.361 | 0.705 |
Lead | mg/L | 0.015l | ND | 0.002 |
Magnesium | mg/L | NA | 0.71 | 1.08 |
Manganese | mg/L | 0.05h | 0.038 | 0.096 |
Mercury | mg/L | 0.002d,e | ND | ND |
Nickel | mg/L | 0.1d | ND | ND |
Nitrite/Nitrate (as nitrogen) | mg/L | 10d | 0.15 | 0.26 |
Nonvolatile (dissolved) beta radioactivity | pCi/L | 50d | 0.368 | 2.86 |
pH | pH units | 6.5-8.5h | 5.9 | 7.8 |
Phosphate | mg/L | NA | ND | 0.04 |
Sodium | mg/L | NA | 3.49 | 9.35 |
Strontium-89/90 | pCi/L | - | <DL | 0.49 |
Sulfate | mg/L | 250h | 4 | 7 |
Suspended solids | mg/L | NA | 2 | 12 |
Temperature | °C | 32.2o | 10.3 | 26.5 |
Total dissolved solids | mg/L | 500h | 42 | 79 |
Tritium | pCi/L | 20,000d,e | 17,200 | 65,000 |
Zinc | mg/L | 5h | ND | 0.012 |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a picocurie is a unit of radioactivity; one trillionth of a curie.
d. Maximum Contaminant Level (MCL), EPA National
Primary Drinking Water Standards ( 40 CFR Part 141).
See glossary.
e. Maximum Contaminant Level, SCDHEC (1976). See glossary.
f. DOE Derived Concentration Guides (DCGs) for water (DOE Order 5400.5). DCG values are based on committed effective doses of 4 millirem per year for consistency with drinking water MCL of 4 millirem per year. See glossary.
g. Minimum concentrations of samples taken at the downstream monitoring station. The maximum listed concentration is the highest single result found during one sampling event.
h. Secondary Maximum Contaminant Level (SMCL). EPA
National Secondary Drinking Water Regulations
(40 CFR Part 143).
i. NA = none applicable.
j. Depends on pH and temperature.
k. ND = none detected.
l. Action level for lead and copper.
m. WQS = water quality standard. See glossary.
n. Less than (<) indicates concentration below analysis detection limit (DL).
o. Shall not exceed weekly average of 32.2°C (90°F) after mixing nor rise more than 2.8°C (5°F) in 1 week unless appropriate temperature criterion mixing zone has been established.
Table E.1-6. Water quality in Steel Creek on SRS (calendar year 1993).a,b
Unit of measurec | MCLd,e or DCGf | Minimumg | Maximumg | |
Aluminum | mg/L | 0.05-0.2h | NDi | 0.138 |
Ammonia | mg/L | NAj,k | ND | 0.05 |
Cadmium | mg/L | 0.005d | ND | ND |
Calcium | mg/L | NA | 1.92 | 2.28 |
Cesium-137 | pCi/L | 120 | 3.75 | 3.75 |
Chemical oxygen demand | mg/L | NA | ND | ND |
Chloride | mg/L | 250h | 4 | 9 |
Chromium | mg/L | 0.1d | ND | ND |
Copper | mg/L | 1.3l | ND | ND |
Dissolved oxygen | mg/L | >5.0m | 6.4 | 11.4 |
Fecal coliform | Colonies per 100 ml | 1,000m | 2 | 142 |
Gross alpha radioactivity | pCi/L | 15d | <DLn | 1.22 |
Iron | mg/L | 0.3h | 0.053 | 0.224 |
Lead | mg/L | 0.015l | ND | 0.004 |
Magnesium | mg/L | NA | 0.947 | 1.16 |
Manganese | mg/L | 0.05k | ND | 0.024 |
Mercury | mg/L | 0.002d,e | ND | ND |
Nickel | mg/L | 0.1d | ND | ND |
Nitrite/Nitrate (as nitrogen) | mg/L | 10d | ND | 0.17 |
Nonvolatile (dissolved) beta radioactivity | pCi/L | 50d | 0.688 | 2.79 |
pH | pH units | 6.5-8.5h | 5.9 | 7.9 |
Phosphate | mg/L | NA | ND | ND |
Sodium | mg/L | NA | 5.44 | 8.53 |
Strontium-90 | pCi/L | 8f | <DL | 0.818 |
Sulfate | mg/L | 250h | 4 | 6 |
Suspended solids | mg/L | NA | ND | 5 |
Temperature | °C | 32.2o | 10.2 | 29.6 |
Total dissolved solids | mg/L | 500h | 39 | 67 |
Tritium | pCi/L | 20,000d,e | 4,130 | 6,200 |
Zinc | mg/L | 5h | ND | 0.014 |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a picocuries is a unit of radioactivity; one trillionth of a curie.
d. Maximum Contaminant Level (MCL), EPA National
Primary Drinking Water Standards (40 CFR Part 141).
See glossary.
e. Maximum Contaminant Level, SCDHEC (1976). See glossary.
f. DOE Derived Concentration Guides (DCGs) for water (DOE Order 5400.5). DCG values are based on committed effective doses of 4 millirem per year for consistency with drinking water MCL of 4 millirem per year. See glossary.
g. Minimum concentrations of samples taken at the downstream monitoring station. The maximum listed concentration is the highest single result found during one sampling event.
h. Secondary Maximum Contaminant Level (SMCL), EPA
National Secondary Drinking Water Regulations
(40 CFR Part 143).
i. ND = none detected.
j. NA = none applicable.
k. Depends on pH and temperature.
l. Action level for lead and copper.
m. WQS = water quality standard. See glossary.
n. Less than (<) indicates concentration below analysis detection limit (DL).
o. Shall not exceed weekly average of 32.2°C (90°F) after mixing nor rise more than 2.8°C (5°F) in 1 week unless appropriate temperature criterion mixing zone has been established.
Table E.1-7. Water quality in Lower Three Runs on SRS (calendar year 1993).a,b
Unit of measurec | MCLd,e or DCGf | Minimumg | Maximumg | |
Aluminum | mg/L | 0.05-0.2h | NDi | 0.092 |
Ammonia | mg/L | NAj,k | ND | 0.06 |
Cadmium | mg/L | 0.005d | ND | ND |
Calcium | mg/L | NA | 5.63 | 12.8 |
Chemical oxygen demand | mg/L | NA | ND | ND |
Chloride | mg/L | 250h | 3 | 5 |
Chromium | mg/L | 0.1d | ND | ND |
Copper | mg/L | 1.3l | ND | ND |
Dissolved oxygen | mg/L | >5.0m | 6.7 | 10.2 |
Fecal coliform | pCi/L | 1,000m | 72 | 12,200 |
Gross alpha radioactivity | mg/L | 15d | <DLn | 0.69 |
Iron | mg/L | 0.3h | 0.138 | 0.275 |
Lead | mg/L | 0.015l | ND | 0.002 |
Magnesium | mg/L | NA | 0.553 | 0.79 |
Manganese | mg/L | 0.05h | ND | 0.024 |
Mercury | mg/L | 0.002d,e | ND | ND |
Nickel | mg/L | 0.1d | ND | ND |
Nitrite/Nitrate (as nitrogen) | mg/L | 10d | ND | 0.18 |
Nonvolatile (dissolved) beta radioactivity | pCi/L | 50d | 1.16 | 3.43 |
pH | pH units | 6.5-8.5h | 5.9 | 7.5 |
Phosphate | mg/L | NA | ND | ND |
Sodium | mg/L | NA | 1.97 | 2.98 |
Strontium-90 | pCi/L | 8f | <DL | 0.048 |
Sulfate | mg/L | 250h | 2 | 4 |
Suspended solids | mg/L | NA | ND | 10 |
Temperature | °C | 32.2o | 10.3 | 26.0 |
Total dissolved solids | mg/L | 500h | 33 | 69 |
Tritium | pCi/L | 20,000d,e | 131 | 907 |
Zinc | mg/L | 5h | ND | 0.031 |
a. Source: Arnett (1994).
b. Parameters are those DOE routinely measures as a regulatory requirement or as part of ongoing monitoring programs.
c. mg/L = milligrams per liter; a measure of concentration equivalent to the weight/volume ratio.
pCi/L = picocuries per liter; a picocurie is a unit of radioactivity; one trillionth of a curie.
d. Maximum Contaminant Level (MCL), EPA National
Primary Drinking Water Standards (40 CFR Part 141).
See glossary.
e. Maximum Contaminant Level, SCDHEC (1976). See glossary.
f. DOE Derived Concentration Guides (DCGs) for water (DOE 5400.5). DCG values are based on committed effective doses of 4 millirem per year for consistency with drinking water MCL of 4 millirem per year. See glossary.
g. Minimum concentrations of samples taken at the downstream monitoring station. The maximum listed concentration is the highest single result found during one sampling event.
h. Secondary Maximum Contaminant Level (SMCL), EPA
National Secondary Drinking Water Regulations
(40 CFR Part 143).
i. ND = none detected.
j. NA = none applicable.
k. Depends on pH and temperature.
l. Action level for lead and copper.
m. WQS = water quality standard. See glossary.
n. Less than (<) indicates concentration below analysis detection limit (DL).
o. Shall not exceed weekly average of 32.2°C (90°F) after mixing nor rise more than 2.8°C (5°F) in 1 week unless appropriate temperature criterion mixing zone has been established.
SECTION 2
at SRS boundary (µg/m3) | standardc | ||
Low Toxicity Category | |||
Acetonitrile | 1,750.00 | 0.00018 | 0.00 |
Ammonium Chloride | 250.00 | 0.02379 | 0.01 |
Antimony | 2.50 | 0.00112 | 0.04 |
Chlorine | 75.00 | 7.63023 | 10.17 |
Cyanide | 125.00 | 0.00000 | 0.00 |
Ethanolamine | 200.00 | 0.00101 | 0.00 |
Formic Acid | 225.00 | 2.41990 | 1.08 |
Furfural | 200.00 | 0.00180 | 0.00 |
Hydrochloric Acid (Hydrogen Chloride) | 175.00 | 1.05622 | 0.60 |
Hydrogen Cyanide | 250.00 | 0.12935 | 0.05 |
Methyl Ethyl Ketone (2-Butone) | 14,750.00 | 5.12159 | 0.03 |
Methyl Methacrylate | 10,250.00 | 0.00002 | 0.00 |
Methylene Chloride | 8,750.00 | 10.46781 | 0.12 |
Methyl Tert-Butyl Ether | 0.49390 | ||
Naphthalene | 1,250.00 | 0.00452 | 0.00 |
Nitric Acid | 125.00 | 50.95952 | 40.77 |
Phosphoric Acid | 25.00 | 0.46236 | 1.85 |
Styrene | 5,325.00 | 0.00079 | 0.00 |
Trichloroethylene | 6,750.00 | 6.43130 | 0.10 |
Moderate Toxicity Category | |||
Acetaldehyde | 1,800.00 | 0.00180 | 0.00 |
Acrylamide | 0.30 | 0.00180 | 0.60 |
Aldicarb | 6.00 | 0.00737 | 0.12 |
Cresol | 220.00 | 0.00180 | 0.00 |
Cumene | 9.00 | 0.00110 | 0.01 |
p-Dichlorobenzene | 4,500.00 | 0.00180 | 0.00 |
Diethanaolamine | 129.00 | 0.00364 | 0.00 |
Dioctyl Phthalate | 50.00 | 0.02569 | 0.05 |
Ethyl Benzene | 4,350.00 | 0.58773 | 0.01 |
Ethyl Chloride | 26,400.00 | 0.00007 | 0.00 |
Ethylene Dibromide | 770.00 | 0.00180 | 0.00 |
Furfuryl Alcohol | 400.00 | 0.00037 | 0.00 |
1,6-Diisocyanatehexamethylene | 0.34 | 0.00110 | 0.32 |
Hydrogen Sulfide | 140.00 | 0.20149 | 0.14 |
Hydroquinone | 20.00 | 0.00010 | 0.00 |
Isophorone | 250.00 | 0.00154 | 0.00 |
Maleic Anhydride | 10.00 | 0.00180 | 0.02 |
Table E.2-1. (continued).
at SRS boundary (µg/m3) | standardc | ||
Methyl Isobutyl Ketone | 2,050.00 | 2.96016 | 0.14 |
Oxalic Acid | 10.00 | 0.00026 | 0.00 |
Pentachlorophenol | 5.00 | 0.00180 | 0.04 |
Phenol | 190.00 | 0.02745 | 0.01 |
Phosgene (Carbonyl Chloride) | 4.00 | 0.00180 | 0.05 |
Phosphorus (Yellow or White) | 0.50 | 0.00013 | 0.03 |
Sodium Hydroxide | 20.00 | 0.00940 | 0.05 |
Sulfuric Acid | 10.00 | 0.00951 | 0.10 |
Tetrachloroethylene | 3,350.00 | 2.00935 | 0.06 |
Xylene | 4,350.00 | 39.36740 | 0.90 |
m-Xylene | 4,350.00 | 0.00180 | 0.00 |
o-Xylene | 4,350.00 | 0.00181 | 0.00 |
p-Xylene | 4,350.00 | 0.00180 | 0.00 |
High Toxicity Category | |||
Acetophenone | 0.00180 | ||
Acrolein | 1.25 | 0.01585 | 1.27 |
Acrylic Acid | 147.50 | 0.00182 | 0.00 |
Acrylonitrile | 22.50 | 0.01646 | 0.07 |
Aniline | 50.00 | 0.00180 | 0.00 |
Arsenic | 1.00 | 0.00191 | 0.19 |
Benzene | 150.00 | 31.71134 | 21.14 |
Benzidine | 0.00180 | ||
Benzotrichloride | 300.00 | 0.00180 | 0.00 |
Benzyl Chloride | 25.00 | 0.00180 | 0.01 |
Beryllium | 0.01 | 0.00000 | 0.00 |
Biphenyl | 6.00 | 0.00138 | 0.02 |
Bis (chloromethyl) Ether | 0.03 | 0.00180 | 6.00 |
Bromoform | 25.85 | 0.00475 | 0.02 |
Cadmium Oxide | 0.25 | 0.02136 | 8.54 |
Cadmium | 0.25 | 0.00028 | 0.11 |
Carbon Disulfide | 150.00 | 0.00208 | 0.00 |
Carbon Tetrachloride | 150.00 | 0.00209 | 0.00 |
Catechol | 297.00 | 0.00009 | 0.00 |
Chlordane | 2.50 | 0.00181 | 0.07 |
Chlorobenzene | 1,725.00 | 0.00209 | 0.00 |
Chloroform | 250.00 | 4.95658 | 1.98 |
Chloromethyl Methyl Ether | 0.00180 | ||
Cobalt | 0.25 | 0.20628 | 82.51 |
2,4-Dichlorphenoxy Acetic Acid | 50.00 | 0.00180 | 0.00 |
Table E.2-1. (continued).
at SRS boundary (µg/m3) | standardc | ||
Dibutyl Phthalate | 25.00 | 0.13246 | 0.53 |
3,3-Dichlorobenzidine | 0.15 | 0.00180 | 1.20 |
1,3-Dichloropropene | 7.00 | 0.00208 | 0.03 |
Diethyl Phthalate | 25.00 | 0.00000 | 0.00 |
3,3-Dimethoxybenzidene | 0.30 | 0.00180 | 0.60 |
3,3-Dimethylbenzidine | 0.00180 | ||
Dimethylformamide | 149.50 | 0.00024 | 0.00 |
Dimethyl Phthalate | 25.00 | 0.00180 | 0.01 |
Dimethyl Sulfate | 2.50 | 0.00180 | 0.07 |
2,4-Dinitrophenol | 0.00180 | ||
2,4-Dinitrotoluene | 1.50 | 0.00180 | 0.12 |
Dioxane | 450.00 | 0.00184 | 0.00 |
1,2-Diphenyl Hydrazine | 0.00180 | ||
Epichlorohydrin | 50.00 | 0.00180 | 0.00 |
1,2-Butylene Oxide | 0.00877 | ||
Ethylene Dichloride | 200.00 | 0.00183 | 0.00 |
Ethylene Glycol | 650.00 | 0.19536 | 0.03 |
Ethylene Oxide | 10.00 | 0.00180 | 0.02 |
Ethylene Thiourea | 0.00180 | ||
Ethylenimine | 5.00 | 0.01802 | 0.36 |
1,1-Dichloroethane | 2,025.00 | 0.00116 | 0.00 |
Formaldehyde | 7.50 | 0.00269 | 0.04 |
Glycol Ethers | 0.00031 | ||
Heptachlor | 2.50 | 0.00737 | 0.29 |
Hexachlorobenzene | 0.00180 | ||
Hexachlorobutadiene | 1.20 | 0.00180 | 0.15 |
Hexachlorocylopentadiene | 0.50 | 0.00180 | 0.36 |
Hexachloroethane | 48.50 | 0.00180 | 0.00 |
Hexachloronapthalene | 1.00 | 0.00000 | 0.00 |
Hexane | 200.00 | 0.20551 | 0.10 |
Hydrazine | 0.50 | 0.00180 | 0.36 |
Lindane | 2.50 | 0.00180 | 0.07 |
Manganese Oxide | 25.00 | 0.00066 | 0.00 |
Manganese | 25.00 | 0.82129 | 3.29 |
Mercury | 0.25 | 0.01393 | 5.57 |
Methyl Alcohol | 1,310.00 | 2.87804 | 0.22 |
Methoxychlor | 50.00 | 0.00180 | 0.00 |
Methyl Bromide | 100.00 | 0.00158 | 0.00 |
Methyl Chloride | 515.00 | 0.00200 | 0.00 |
Table E.2-1. (continued).
at SRS boundary (µg/m3) | standardc | ||
1,1,1-Trichloroethane | 9,550.00 | 80.83216 | 0.85 |
Methyl Hydrazine | 1.75 | 0.00180 | 0.10 |
Methyl Iodide | 58.00 | 0.00180 | 0.00 |
Curene | 1.10 | 0.00180 | 0.16 |
Nickel Oxide | 5.00 | 0.00183 | 0.04 |
Nickel | 0.50 | 0.27106 | 54.21 |
Nitrobenzene | 25.00 | 0.00314 | 0.01 |
p-Nitrophenol | 0.00 | 0.00180 | |
2-Nitropropane | 182.00 | 0.00180 | 0.00 |
Parathion | 0.50 | 0.00737 | 1.47 |
Pentachloronitrobenzene | 0.00180 | ||
Phthalic Anhydride | 30.30 | 0.00180 | 0.01 |
Polycyclic Organic Matter | 160.00 | 0.00000 | 0.00 |
Propylene Dichloride | 1,750.00 | 0.00079 | 0.00 |
Selenium | 1.00 | 0.00000 | 0.00 |
Tetrachlorinated Dibenzo-p-Dioxins | 0.00 | 0.00000 | |
1,1,2,2-Tetrachloroethane | 35.00 | 0.00208 | 0.01 |
Toluene | 200.00 | 9.27688 | 0.46 |
Toxaphene | 2.50 | 0.00737 | 0.29 |
1,1,2-Trichloroethane | 273.00 | 0.01646 | 0.01 |
2,4,6-Trichlorophenol | 0.00180 | ||
Triethylamine | 207.00 | 0.00010 | 0.00 |
Vinyl Acetate | 176.00 | 0.05518 | 0.03 |
Vinyl Chloride | 50.00 | 0.00183 | 0.00 |
1,1-Dichloroethylene | 99.00 | 0.00180 | 0.00 |
a. Source: WSRC (1993).
b. Concentrations are based on maximum potential emissions.
c. Percent of standard =
d. No standard established by regulatory agency.
e. NA - not applicable.
| ||||||||||||
M-Area Vendor | ||||||||||||
Nitrogen dioxide | 9,000 | 37.45 | 43.70 | 37.45 | 43.70 | 37.45 | 43.70 | |||||
Sulfur dioxide | 1.3´104 | 1.65 | 1.92 | 1.65 | 1.92 | 1.65 | 1.92 | |||||
PM10d | 5,000 | 1.97 | 2.30 | 1.97 | 2.30 | 1.97 | 2.30 | |||||
Bld waste hazardous waste storage) | ||||||||||||
Total suspended particulates | 1.5×104 | 25.13 | 10.56 | 13.10 | 5.51 | 41.28 | 17.36 | |||||
PM10 | 5,000 | 8.79 | 3.70 | 4.49 | 1.89 | 14.54 | 6.11 | |||||
Bldg. 645-2N (mixed waste mixed waste storage) | ||||||||||||
Total suspended particulates | 1.5×104 | 6.60 | 2.78 | 1.78 | 0.75 | 32.84 | 13.81 | |||||
PM10 | 5,000 | 2.32 | 0.97 | 0.62 | 0.26 | 11.50 | 4.84 | |||||
Soil sort facilities | ||||||||||||
Total suspended particulates | 1.5×104 | 11.00 | 4.63 | 0.31 | 0.13 | 54.74 | 23.02 | |||||
PM10 | 5,000 | 3.84 | 1.61 | 0.11 | 0.05 | 1.92 | 0.81 | |||||
(Four) new solvent tanks | ||||||||||||
Vinyl chloride | 2,600 | 5.08 | 3.95 | 3.78 | 2.94 | 4.29 | 3.34 | |||||
1,1 Dichloroethane | N/Ae | 0.38 | 0.30 | 0.29 | 0.22 | 0.33 | 0.25 | |||||
Methyl ethyl Ketone | 5.9×105 | 22.00 | 17.11 | 16.39 | 12.75 | 18.61 | 14.48 | |||||
Chloroform | 9,780 | 2.36 | 1.84 | 1.76 | 1.37 | 2.00 | 1.56 | |||||
Carbon tetrachloride | 1.26×104 | 0.19 | 0.15 | 0.14 | 0.11 | 0.16 | 0.13 | |||||
Benzene | 3,250 | 3.08 | 2.40 | 2.29 | 1.78 | 2.61 | 2.03 | |||||
1,2 Dichloroethane | N/A | 0.13 | 0.10 | 0.09 | 0.07 | 0.11 | 0.08 | |||||
Trichloroethane | 2.7×105 | 0.12 | 0.09 | 0.09 | 0.07 | 0.10 | 0.08 | |||||
Tetrachloroethylene | 1.7×105 | 0.03 | 0.02 | 0.02 | 0.02 | 0.02 | 0.02 | |||||
Chlorobenzene | 3.5×105 | 0.02 | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 | |||||
Transuranic waste characterization/ certification facility | ||||||||||||
Vinyl chloride | 2,600 | 0.02 | 0.01 | 0.01 | 0.01 | 0.39 | 0.34 | |||||
1,1 Dichloroethane | N/A | 0.001 | 9.8×10-4 | 8.1×10-4 | 7.0×10-4 | 0.30 | 0.25 | |||||
Methyl ethyl ketone | 5.9×105 | 0.07 | 0.06 | 0.05 | 1.70 | 1.46 | ||||||
Chloroform | 9,780 | 0.01 | 0.01 | 0.01 | 0.18 | 0.16 | ||||||
Carbon tetrachloride | 1.26×104 | 5.6×10-4 | 4.8×10-4 | 4.0×10-4 | 0.015 | 0.013 | ||||||
Benzene | 3,250 | 0.009 | 0.008 | 0.007 | 0.237 | 0.204 | ||||||
1,2 Dichloroethane | N/A | 3.8×10-4 | 3.2×10-4 | 2.7×10-4 | 0.010 | 0.008 | ||||||
Trichloroethane | 2.7×105 | 3.6×10-4 | 3.1×10-4 | 2.5×10-4 | 0.009 | 0.008 | ||||||
Tetrachloroethylene | 1.7×105 | 7.9×10-5 | 6.8×10-5 | 5.6×10-5 | 0.002 | 0.002 | ||||||
Chlorobenzene | 3.5×105 | 5.0×10-5 | 4.3×10-5 | 3.5×10-5 | 0.001 | 0.001 | ||||||
Containment building | ||||||||||||
Total suspended particulates | 1.5×104 | 4.34 | 2.64 | 2.28 | 15.41 | 9.36 | ||||||
PM10 | 5,000 | 4.34 | 2.64 | 15.41 | 9.36 |
Table E.2-2. (continued).
| |||||||||||
Vinyl chloride | 2,600 | 0.24 | 0.15 | 0.13 | 0.08 | 1.08 | 0.66 | ||||
1,1 Dichloroethane | N/A | 0.02 | 0.01 | 0.01 | 0.01 | 0.08 | 0.05 | ||||
Methyl ethyl ketone | 5.9×105 | 26.40 | 16.04 | 25.46 | 15.47 | 32.38 | 19.68 | ||||
Chloroform | 9,780 | 0.11 | 0.07 | 0.06 | 0.04 | 0.50 | 0.31 | ||||
Carbon tetrachloride | 1.26×104 | 0.01 | 0.01 | 0.005 | 0.003 | 0.04 | 0.02 | ||||
Benzene | 3,250 | 0.15 | 0.08 | 0.06 | 0.04 | 0.66 | 0.40 | ||||
1,2 Dichloroethane | N/A | 0.006 | 0.004 | 0.003 | 0.002 | 0.03 | 0.02 | ||||
Trichloroethane | 2.7×105 | 0.006 | 0.004 | 0.003 | 0.002 | 0.03 | 0.02 | ||||
Tetrachloroethylene | 1.7×105 | 0.001 | 7.4×10-4 | 5.4×10-4 | 3.3×10-4 | 0.006 | 0.003 | ||||
Chlorobenzene | 3.5×105 | 7.6×10-4 | 4.6×10-4 | 3.4×10-4 | 2.1×10-4 | 0.004 | 0.002 |
a. Source: NIOSH (1990).
b. OSHA PEL - Occupational Safety and Health Administration Permissible Exposure Limits.
c. To convert to feet multiply by 3.281.
d. Particulate matter less than 10 microns in diameter.
e. Not Applicable - No OSHA PEL assigned - Exposure should be kept as low as possible.
| meters | |||||||||||||||
M-Area Vendor | ||||||||||||||||
Nitrogen dioxide | 9,000 | 37.45 | 43.70 | 37.45 | 43.70 | 37.30 | 43.52 | |||||||||
Sulfur dioxide | 1.3×104 | 1.65 | 1.92 | 1.65 | 1.92 | 1.65 | 1.92 | |||||||||
PM10d | 5,000 | 1.97 | 2.30 | 1.97 | 2.30 | 1.97 | 2.30 | |||||||||
Bldg. 645-2N (mixed waste mixed waste storage) | ||||||||||||||||
Total suspended particulates | 15,000 | 6.60 | 2.78 | 1.78 | 0.75 | 32.84 | 13.81 | |||||||||
PM10 | 5,000 | 2.32 | 0.97 | 0.62 | 0.26 | 11.50 | 4.84 | |||||||||
Soil sort facilities | ||||||||||||||||
Total suspended particulates | 15,000 | 15.63 | 6.57 | 4.34 | 1.83 | 75.38 | 31.69 | |||||||||
PM10 | 5,000 | 5.47 | 2.30 | 1.52 | 0.64 | 26.38 | 11.09 | |||||||||
(Four) new solvent tanks | ||||||||||||||||
Vinyl chloride | 2,600 | 3.99 | 3.10 | 3.92 | 3.05 | 4.17 | 3.24 | |||||||||
1,1 Dichloroethane | N/Ae | 0.30 | 0.23 | 0.30 | 0.23 | 0.32 | 0.25 | |||||||||
Methyl ethyl ketone | 5.9×105 | 17.28 | 13.44 | 17.00 | 13.22 | 18.06 | 14.04 | |||||||||
Chloroform | 9,780 | 1.86 | 1.44 | 1.82 | 1.42 | 1.94 | 1.51 | |||||||||
Carbon tetrachloride | 1.26×104 | 0.15 | 0.12 | 0.15 | 0.11 | 0.16 | 0.12 | |||||||||
Benzene | 3,250 | 2.42 | 1.88 | 2.38 | 1.85 | 2.53 | 1.97 | |||||||||
1,2 Dichloroethane | N/A | 0.10 | 0.08 | 0.10 | 0.08 | 0.10 | 0.08 | |||||||||
Trichloroethane | 2.7×105 | 0.09 | 0.07 | 0.09 | 0.07 | 0.10 | 0.08 | |||||||||
Tetrachloroethylene | 1.7×105 | 0.02 | 0.02 | 0.02 | 0.02 | 0.02 | 0.02 | |||||||||
Chlorobenzene | 3.5×105 | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 | |||||||||
Transuranic waste characterization/ certification facility | ||||||||||||||||
Vinyl chloride | 2,600 | 0.015 | 0.013 | 0.011 | 0.009 | 0.389 | 0.335 | |||||||||
1,1 Dichloroethane | N/A | 0.001 | 0.001 | 0.001 | 0.001 | 0.029 | 0.025 | |||||||||
Methyl ethyl ketone | 5.9×105 | 0.065 | 0.056 | 0.046 | 0.040 | 1.687 | 1.450 | |||||||||
Chloroform | 9,780 | 0.007 | 0.006 | 0.005 | 0.004 | 0.181 | 0.155 | |||||||||
Carbon tetrachloride | 1.26×104 | 5.6×10-4 | 4.8×10-4 | 4.0×10-4 | 3.4×10-4 | 0.015 | 0.013 | |||||||||
Benzene | 3,250 | 0.009 | 0.008 | 0.006 | 0.006 | 0.236 | 0.203 | |||||||||
1,2 Dichloroethane | N/A | 3.7×10-4 | 3.2×10-4 | 2.7×10-4 | 2.3×10-4 | 0.010 | 0.008 | |||||||||
Trichloroethane | 2.7×105 | 3.5×10-4 | 3.0×10-4 | 2.5×10-4 | 2.2×10-4 | 0.009 | 0.008 | |||||||||
Tetrachloroethylene | 1.7×105 | 7.9×10-5 | 6.8×10-5 | 5.6×10-5 | 4.8×10-5 | 0.002 | 0.002 | |||||||||
Chlorobenzene | 3.5×105 | 4.9×10-5 | 4.2×10-5 | 3.5×10-5 | 3.0×10-5 | 0.001 | 0.001 | |||||||||
Containment building | ||||||||||||||||
Vinyl chloride | 2,600 | 0.059 | 0.036 | 0.028 | 0.017 | 0.219 | 0.133 | |||||||||
1,1 Dichloroethane | N/A | 0.004 | 0.003 | 0.002 | 0.001 | 0.017 | 0.010 | |||||||||
Methyl ethyl ketone | 5.9×105 | 24.91 | 15.13 | 24.65 | 14.98 | 26.21 | 15.92 | |||||||||
Chloroform | 9,780 | 0.028 | 0.017 | 0.013 | 0.008 | 0.102 | 0.062 | |||||||||
Carbon tetrachloride | 1.26×104 | 0.002 | 0.001 | 0.001 | 6.5×10-4 | 0.008 | 0.005 | |||||||||
Benzene | 3,250 | 0.036 | 0.022 | 0.017 | 0.010 | 0.133 | 0.081 | |||||||||
1,2 Dichloroethane | N/A | 0.001 | 9.0×10-4 | 7.1×10-4 | 4.3×10-4 | 0.005 | 0.003 | |||||||||
Trichloroethane | 2.7×105 | 0.004 | 0.002 | 0.002 | 9.2×10-4 | 0.011 | 0.007 | |||||||||
Tetrachloroethylene | 1.7×105 | 8.1×10-4 | 4.9×10-4 | 3.4×10-4 | 2.1×10-4 | 0.002 | 0.001 | |||||||||
Chlorobenzene | 3.5×105 | 5.1×10-4 | 3.1×10-4 | 2.1×10-4 | 1.3×10-4 | 0.002 | 9.3×10-4 |
Table E.2-3. (continued).
| PELb | meters | meters | ||||||
Non-alpha vitrification | |||||||||
Total suspended particulates | 1.5×104 | 1.5×10-9 | 0.215 | 4.4×10-10 | 0.065 | 7.2×10-9 | 1.056 | ||
PM10 | 5,000 | 1.5×10-9 | 0.215 | 4.4×10-10 | 0.065 | 7.2×10-9 | 1.056 | ||
Nitrogen oxides | 9,000 | 3.2×10-9 | 0.478 | 9.7×10-10 | 0.143 | 1.6×10-8 | 2.344 | ||
Sulfur dioxide | 1.3×104 | 2.0×10-11 | 0.003 | 6.1×10-12 | 9.0×10-4 | 1.0×10-10 | 0.015 | ||
Carbon monoxide | 4.0×104 | 2.9×10-12 | 4.3×10-4 | 8.7×10-13 | 1.3×10-4 | 1.4×10-11 | 0.002 | ||
Lead | 100 | 3.0×10-12 | 4.4×10-4 | 8.9×10-13 | 1.3×10-4 | 1.5×10-11 | 0.002 | ||
Acetaldehyde | 1.8×105 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Acrylamide | 30 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Acrylonitrile | 4,420 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Arsenic pentoxide | 10 | 2.9×10-12 | 4.3×10-4 | 1.5×10-12 | 2.2×10-4 | 6.5×10-12 | 9.6×10-4 | ||
Asbestos | 0.2 fibers/m3 | 6.6×10-14 | 9.8×10-6 | 1.6×10-14 | 2.3×10-6 | 1.8×10-13 | 2.6×10-5 | ||
Benzene | 3,250 | 7.1×10-11 | 0.010 | 3.6×10-11 | 0.005 | 1.6×10-10 | 0.023 | ||
Benzidine | N/A | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Bis(chloromethyl)ether | N/A | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Bromoform | 5,000 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Carbon tetrachloride | 1.2×6104 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Chlordane | 500f | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Chloroform | 9,780 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Cr(+6) Compounds | 50f | 2.0×10-14 | 2.9×10-6 | 1.0×10-14 | 1.5×10-6 | 4.4×10-14 | 6.5×10-6 | ||
Formaldehyde | 1,224 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Heptachlor | 500 | 1.5×10-12 | 2.2×10-4 | 7.6×10-13 | 1.1×10-4 | 2.2×10-12 | 4.8×10-4 | ||
Hexachlorobenzene | N/A | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Hexachlorobutadiene | 210f | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Hydrazine | 100 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Nickel oxide | 1,000 | 3.3×10-11 | 0.005 | 7.9×10-12 | 0.001 | 8.9×10-11 | 0.013 | ||
1,1,2,2-Tetrachloroethane | 7,000 | 1.2×10-11 | 0.002 | 6.1×10-12 | 8.9×10-4 | 2.6×10-11 | 0.004 | ||
1,1,2-Trichloroethane | 4.5×104 | 5.9×10-13 | 8.7×10-5 | 3.0×10-13 | 4.5×10-5 | 1.3×10-12 | 1.9×10-4 | ||
Toxaphene | 500 | 1.5×10-12 | 2.2×10-4 | 7.6×10-13 | 1.1×10-4 | 3.2×10-12 | 4.8×10-4 | ||
Alpha vitrification | |||||||||
Total suspended particulates | 1.5×104 | 8.2×10-10 | 0.12 | 4.9×10-10 | 0.07 | 2.1×10-8 | 3.06 | ||
PM10 | 5,000 | 8.2×10-10 | 0.12 | 4.9×10-10 | 0.07 | 2.1×10-8 | 3.06 | ||
Nitrogen oxides | 9,000 | 1.8×10-9 | 0.27 | 1.1×10-9 | 0.16 | 4.6×10-8 | 6.78 | ||
Sulfur dioxide | 1.3×104 | 1.1×10-11 | 0.002 | 6.8×10-12 | 0.001 | 2.9×10-11 | 0.004 | ||
Carbon monoxide | 4.0×104 | 1.6×10-12 | 2.4×10-4 | 9.7×10-13 | 1.44×10-4 | 4.1×10-11 | 0.01 | ||
Lead | 100 | 1.7×10-12 | 2.45×10-4 | 1.0×10-12 | 1.47×10-4 | 4.2×10-11 | 0.01 | ||
Asbestos | 0.2 fibers/m3 | 6.6×10-15 | 9.8×10-7 | 4.0×10-15 | 5.9×10-7 | 1.7×10-13 | 2.5×10-5 | ||
Nickel oxide | 1,000 | 3.3×10-12 | 4.9×10-4 | 2.0×10-12 | 2.93×10-4 | 8.4×10-10 | 0.01 |
a. Source: NIOSH (1990).
b. OSHA PEL - Occupational Safety and Health Administration permissible exposure limits.
c. To convert to feet multiply by 3.281.
d. Particulate matter less than 10 microns in diameter.
e. N/A = not applicable. No OSHA PEL assigned. Exposure should be kept as low as possible.
f. Threshold limit value, time-weighted average (ACGIH 1993).
| meters | meters | meters | meters | ||||||||
M-Area Vendor | ||||||||||||
Nitrogen dioxide | 9,000 | 37.45 | 43.70 | 37.45 | 43.70 | 37.30 | 43.52 | |||||
Sulfur dioxide | 1.3×10-4 | 1.65 | 1.92 | 1.65 | 1.92 | 1.65 | 1.92 | |||||
PM10d | 5,000 | 1.97 | 2.30 | 1.97 | 2.30 | 1.97 | 2.30 | |||||
Bldg. 645-N (hazardous waste storage) | ||||||||||||
Total suspended particulates | 1.5×104 | 25.13 | 10.56 | 13.10 | 5.51 | 41.28 | 17.36 | |||||
PM10 | 5,000 | 8.79 | 3.70 | 4.49 | 1.89 | 14.54 | 6.11 | |||||
Bldg. 645-2N (mixed waste mixed waste storage) | ||||||||||||
Total suspended particulates | 15,000 | 6.60 | 2.78 | 1.78 | 0.75 | 32.84 | 13.81 | |||||
PM10 | 5,000 | 2.32 | 0.97 | 0.62 | 0.26 | 11.50 | 4.84 | |||||
Soil sort facilities | ||||||||||||
Total suspended particulates | 15,000 | 10.79 | 4.54 | 3.39 | 1.43 | 64.79 | 27.24 | |||||
PM10 | 5,000 | 3.77 | 1.58 | 1.19 | 0.50 | 22.61 | 9.51 | |||||
(Four) new solvent tanks | ||||||||||||
Vinyl chloride | 2,600 | 4.71 | 3.66 | 4.28 | 3.33 | 4.25 | 3.31 | |||||
1,1 Dichloroethane | N/Ae | 0.36 | 0.28 | 0.32 | 0.25 | 0.32 | 0.25 | |||||
Methyl ethyl ketone | 5.9×105 | 20.39 | 15.86 | 18.56 | 14.43 | 18.39 | 14.30 | |||||
Chloroform | 9,780 | 2.19 | 1.70 | 1.99 | 1.55 | 1.98 | 1.54 | |||||
Carbon tetrachloride | 1.26×104 | 0.18 | 0.14 | 0.16 | 0.12 | 0.16 | 0.12 | |||||
Benzene | 3,250 | 2.86 | 2.22 | 2.60 | 2.02 | 2.58 | 2.00 | |||||
1,2 Dichloroethane | N/A | 0.12 | 0.09 | 0.11 | 0.08 | 0.11 | 0.08 | |||||
Trichloroethane | 2.7×105 | 0.11 | 0.09 | 0.10 | 0.08 | 0.10 | 0.08 | |||||
Tetrachloroethylene | 1.7×105 | 0.02 | 0.02 | 0.02 | 0.02 | 0.02 | 0.02 | |||||
Chlorobenzene | 3.5×105 | 0.02 | 0.01 | 0.01 | 0.01 | 0.01 | 0.01 | |||||
Transuranic waste characterization/ certification facility | ||||||||||||
Vinyl chloride | 2,600 | 0.02 | 0.01 | 0.01 | 0.009 | 0.39 | 0.33 | |||||
1,1 Dichloroethane | N/A | 0.001 | 9.7×10-4 | 8.0×10-4 | 6.9×10-4 | 0.29 | 0.25 | |||||
Methyl ethyl Ketone | 5.9×105 | 0.07 | 0.06 | 0.05 | 0.04 | 1.69 | 1.45 | |||||
Chloroform | 9,780 | 0.007 | 0.006 | 0.005 | 0.004 | 0.18 | 0.16 | |||||
Carbon tetrachloride | 1.26×104 | 5.6×10-4 | 4.8×10-4 | 3.9×10-4 | 3.4×10-4 | 0.01 | 0.01 | |||||
Benzene | 3,250 | 0.009 | 0.008 | 0.006 | 0.006 | 0.24 | 0.20 | |||||
1,2 Dichloroethane | N/A | 3.7×10-4 | 3.2×10-4 | 2.7×10-4 | 2.3×10-4 | 0.010 | 0.008 | |||||
Trichloroethane | 2.7×105 | 3.5×10-4 | 3.1×10-4 | 2.5×10-4 | 2.2×10-4 | 0.009 | 0.008 | |||||
Tetrachloroethylene | 1.7×105 | 7.9×10-5 | 6.8×10-5 | 5.6×10-5 | 4.8×10-5 | 0.002 | 0.002 | |||||
Chlorobenzene | 3.5×105 | 5.0×10-5 | 4.3×10-5 | 3.5×10-5 | 3.0×10-5 | 0.001 | 0.001 | |||||
Containment building | ||||||||||||
Total suspended particulates | 1.5×104 | 2.96 | 1.80 | 1.48 | 0.90 | 10.26 | 6.23 | |||||
PM10 | 5,000 | 2.96 | 1.80 | 1.48 | 0.90 | 10.26 | 6.23 | |||||
Vinyl chloride | 2,600 | 0.17 | 0.10 | 0.08 | 0.05 | 0.74 | 0.45 | |||||
1,1 Dichloroethane | N/A | 0.01 | 0.01 | 0.01 | 15.25 | 29.82 | 0.03 | |||||
Methyl ethyl Ketone | 5.9×105 | 25.77 | 15.66 | 25.10 | 0.22 | 3.22 | 18.12 | |||||
Chloroform | 9,780 | 0.08 | 0.05 | 0.04 | 0.02 | 0.34 | 0.21 | |||||
Carbon tetrachloride | 1.26×104 | 0.01 | 0.004 | 0.003 | 0.002 | 0.03 | 0.02 | |||||
Benzene | 3,250 | 0.10 | 0.06 | 0.05 | 0.03 | 0.45 | 0.27 | |||||
1,2 Dichloroethane | N/A | 0.004 | 0.003 | 0.002 | 0.001 | 0.02 | 0.01 | |||||
Trichloroethane | 2.7×105 | 0.004 | 0.002 | 0.002 | 0.001 | 0.02 | 0.01 | |||||
Tetrachloroethylene | 1.7×105 | 7.8×10-4 | 4.7×10-4 | 3.7×10-4 | 2.2×10-4 | 3.9×10-3 | 2.4×10-3 | |||||
Chlorobenzene | 3.5×105 | 4.9×10-4 | 3.0×10-4 | 2.3×10-4 | 1.4×10-4 | 2.4×10-3 | 1.5×10-3 |
Table E.2-4. (continued).
| metersc | meters | meters | meters | meters | meters | |||||||
Non-alpha vitrification | |||||||||||||
Total suspended particulates | 1.5×104 | ||||||||||||
PM10 | 5,000 | ||||||||||||
Nitrogen oxides | 9,000 | ||||||||||||
Sulfur dioxide | 1.3×104 | ||||||||||||
Carbon monoxide | 4.0×104 | ||||||||||||
Lead | 100 | ||||||||||||
Acetaldehyde | 1.8×105 | ||||||||||||
Acrylamide | 30 | ||||||||||||
Acrylonitrile | 4,420 | ||||||||||||
Arsenic pentoxide | 10 | ||||||||||||
Asbestos | 0.2 fibers/ m3 | ||||||||||||
Benzene | 3,250 | ||||||||||||
Benzidine | N/A | ||||||||||||
Bis(chloromethyl)ether | N/A | ||||||||||||
Bromoform | 5,000 | ||||||||||||
Carbon tetrachloride | 1.26×104 | ||||||||||||
Chlordane | 500g | ||||||||||||
Chloroform | 9,780 | ||||||||||||
Cr(+6) Compounds | 50g | ||||||||||||
Formadelhyde | 1,224 | ||||||||||||
Heptachlor | 500 | ||||||||||||
Hexachlorobenzene | N/A | ||||||||||||
Hexachlorobutadiene | 210f | ||||||||||||
Hydrazine | 100 | ||||||||||||
Nickel oxide | 1,000 | ||||||||||||
1,1,2,2-Tetrachloroethane | 7,000 | ||||||||||||
1,1,2-Trichloroethane | 4.5×104 | ||||||||||||
Toxaphene | 500 | ||||||||||||
Alpha vitrification | |||||||||||||
Total suspended particulates | 1.5×104 | ||||||||||||
PM10 | 5,000 | ||||||||||||
Nitrogen oxides | 9,000 | ||||||||||||
Sulfur dioxide | 1.3×104 | ||||||||||||
Carbon monoxide | 4.0×104 | ||||||||||||
Lead | 100 | ||||||||||||
Asbestos | 0.2 fibers/ m3 | ||||||||||||
Nickel oxide | 1,000 |
a. Source: NIOSH (1990).
b. OSHA PEL - Occupational Safety and Health Administration Permissible Exposure Limits.
c. To convert to feet multiply by 3.281.
d. Particulate matter less than 10 microns in diameter.
e. N/A = Not Applicable. No OSHA PEL assigned. Exposure should be kept as low as possible.
f. no vit. = no non-alpha vitrification occurring.
g. Threshold limit value, time-weighted average (ACGIH 1993).
Lead | 1.0E-05 | 1.0E-05 | 1.0E-05 | 3.0E-05 | 3.0E-05 | 6.0E-05 | 2.5E-05 | 1.9E-05 | 6.6E-05 | ||||
Dioxane | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Ethylene dibromide | 4.1E-07 | 2.5E-07 | 3.1E-07 | 3.5E-07 | 1.7E-07 | 3.0E-07 | 1.1E-06 | 5.9E-07 | 2.5E-06 | ||||
Ethylene dichloride | 4.1E-07 | 2.5E-07 | 3.1E-07 | 3.5E-07 | 1.7E-07 | 3.0E-07 | 1.1E-06 | 5.9E-07 | 2.5E-06 | ||||
Parathion | 4.1E-07 | 2.5E-07 | 3.1E-07 | 3.5E-07 | 1.7E-07 | 3.0E-07 | 1.1E-06 | 5.9E-07 | 2.5E-06 | ||||
Aniline | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Cresols | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Chloromethyl methyl Ether | 1.45E-07 | 2.41E-08 | 8.77E-08 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
3, 3-Dichlorobenzidene | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
1, 2-Diphenylhydrazine | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
2, 4-Dinitrotoluene | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Methyl iodide | 1.45E-07 | 2.41E-08 | 8.77E-08 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Pentachlorophenol | 1.6E-07 | 9.9E-08 | 1.2E-07 | 1.4E-07 | 6.8E-08 | 1.2E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 | ||||
Benzyl chloride | 1.0E-04 | 1.0E-04 | 1.0E-04 | 8.0E-08 | 4.1E-08 | 4.4E-07 | 4.6E-07 | 2.4E-07 | 1.0E-06 |
a. Source: EPA (1994).
b. Integrated Risk Information System (IRIS) contains EPA health risk information for Class A, B, and C (suspected, probable, and possible) carcinogens.
SECTION 3
Table E.3-1. Hazardous waste shipments during 30-year period of interest.
| container | truck | volume (m3) | volume (m3) |
shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | |||||||
ONSITE SHIPMENTSc | ||||||||||||||||||||
Inorganic debris | 90 cu. ft. box | 6 | 4,280 | 8,283 | 11,489 | 280 | 541 | 751 | 280 | 541 | 751 | 280 | 541 | 751 | ||||||
Soils | 45 cu. ft. box | 10 | 146,784 | 282,935 | 465,392 | 11,468 | 22,106 | 36,361 | 11,468 | 22,106 | 36,361 | 11,468 | 22,106 | 36,361 | ||||||
Filters | 45 cu. ft. box | 1 | 2,267 | 4,285 | 6,495 | 17,71 | 3,348 | 5,074 | 1,771 | 3,348 | 5,074 | 1,771 | 3,348 | 5,074 | ||||||
Aqueous liquids | 3000 gal. truck | 1 | 8,206 | 35,943 | 38,345 | 714 | 3,142 | 3,376 | 714 | 3,142 | 3,376 | 714 | 3,142 | 3,376 | ||||||
Organic debris | 90 cu. ft. box | 1 | 28 | 28 | 28 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | ||||||
Organic sludge | 55 gal. drum | 1 | 2,327 | 4,545 | 6,867 | 11,635 | 22,725 | 34,335 | 11,635 | 22,725 | 34,335 | 11,635 | 22,725 | 34,335 | ||||||
Heterogeneous debris | 90 cu. ft. box | 2 | 6,188 | 11,690 | 15,642 | 1,213 | 2,292 | 3,067 | 1,213 | 2,292 | 3,067 | 1,213 | 2,292 | 3,067 | ||||||
Lead | 22.5 cu. ft. box | 1 | 2,764 | 5,266 | 7,725 | 4,339 | 8,267 | 12,127 | 4,339 | 8,267 | 12,127 | 4,339 | 8,267 | 12,127 | ||||||
Organic liquids | 3000 gal. truck | 1 | 2,238 | 4,523 | 6,495 | 197 | 398 | 572 | 197 | 398 | 572 | 197 | 398 | 572 | ||||||
CIF ashcreted | 55 gal. drum | 48 | 72 | 132 | 198 | 72 | 132 | 198 | 55 | 66 | 73 | |||||||||
Bulk | Bulk box | 1 | 3,389 | 6,642 | 9,474 | 62 | 122 | 174 | 62 | 122 | 174 | 62 | 122 | 174 | ||||||
Inorganic sludge | 55 gal. drum | 30 | 2,327 | 4,545 | 6,867 | 388 | 758 | 1,145 | 388 | 758 | 1,145 | 388 | 758 | 1,145 | ||||||
Metal debris | 90 cu. ft. box | 4 | 7,800 | 14,220 | 20,974 | 765 | 1,394 | 2,056 | 765 | 1,394 | 2,056 | 765 | 1,394 | 2,056 | ||||||
Sand/rock/gravel | 45 cu. ft. box | 6 | 19,698 | 38,060 | 62,091 | 2,565 | 4,956 | 8,085 | 2,565 | 4,956 | 8,085 | 2,565 | 4,956 | 8,085 | ||||||
Paint waste | 55 gal. drum | 4 | 2,294 | 4,062 | 6,122 | 2,868 | 5,078 | 7,653 | 2,868 | 5,078 | 7,653 | 2,868 | 5,078 | 7,653 | ||||||
Glass debris | 55 gal. drum | 60 | 4,297 | 7,999 | 12,245 | 358 | 667 | 1,020 | 358 | 667 | 1,020 | 358 | 667 | 1,020 | ||||||
PCBs | 55 gal. drum | 1 | 2,437 | 2,437 | 2,280 | 12,185 | 12,185 | 11,400 | 12,185 | 12,185 | 11,400 | 12,185 | 12,185 | 11,400 | ||||||
OFFSITE SHIPMENTSf | ||||||||||||||||||||
Various typesg | 40 foot van | (h) | (h) | (h) | 8,093 | 14,745 | 24,843 | 7,713 | 14,725 | 23,780 | 6,558 | 7,944 | 9,233 | |||||||
(No-Action) | ||||||||||||||||||||
14 | 8 | 14 | 20 | 8 | 14 | 20 | 8 | 13 | 18 |
Source: Rollins (1995).
a. Cubic meters.
b. Expected waste volume is assumed to be the same as for the no-action alternative.
c. Onsite shipments average 8 kilometers (5 miles) each.
d. CIF = Consolidated Incineration Facility. Volumes from the Consolidated Incineration Facility vary depending on alternative. Source: Hess (1994a, b, c, and d).
e. Ashcrete volume varies depending on alternative (Ashcrete is not a hazardous waste).
f. Offsite shipments average 1,609 kilometers (1,000 miles) each.
g. Offsite shipments of hazardous waste types vary
depending on alternative.
h. Hazardous waste volume varies depending on alternatives.
i. Daily shipments are estimated by totaling all shipments for each alternative/forecast and dividing this sum by 30 years and 250 working days per year.
Table E.3-2. Low-level and transuranic (TRU) waste shipments during the 30-year period of interest.
| container | truck | volume (m3) | volume (m3) | shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | |||||||||||
ONSITE SHIPMENTSc | ||||||||||||||||||||||||
Tritiated equipment | 90 cu. ft. box | 10 | 461 | 1,184 | 1,622 | 18 | 46 | 64 | 18 | 46 | 64 | 18 | 46 | 64 | ||||||||||
Spent deionizers | Liner | 1 | 30 | 30 | 30 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | 11 | ||||||||||
LLW job-controld | 90 cu. ft. box | 6 | 309,115 | 366,285 | 413,812 | 21,375 | 25,112 | 28,218 | 20,204 | 23,940 | 27,047 | 20,204 | 23,940 | 27,047 | ||||||||||
Offsite job-control | 90 cu. ft. box | 10 | 12,600 | 12,600 | 25,200 | 494 | 494 | 988 | 494 | 494 | 988 | 494 | 494 | 988 | ||||||||||
LLW equipment | 90 cu. ft. box | 6 | (e) | (e) | (e) | 2,220 | 4,543 | 15,386 | 1,707 | 3,319 | 10,525 | 1,177 | 2,089 | 5,471 | ||||||||||
ILW job-controlf | 90 cu. ft. box | 2 | 12,477 | 22,335 | 28,111 | 2,446 | 4,449 | 5,512 | 2,446 | 4,449 | 5,512 | 2,446 | 4,449 | 5,512 | ||||||||||
Long-lived waste | 55 gal. drum | 1 | 1,003 | 3,302 | 4,643 | 5,015 | 16,510 | 23,215 | 5,015 | 16,510 | 23,215 | 5,015 | 16,510 | 23,215 | ||||||||||
Tritiated job-control | 90 cu. ft. box | 10 | 1,558 | 3,860 | 133,994 | 61 | 151 | 5,255 | 61 | 151 | 5,255 | 61 | 151 | 5,255 | ||||||||||
Low-level soils | 45 cu. ft. box | 10 | 8,068 | 19,791 | 311,923 | 630 | 1,548 | 24,371 | 630 | 1,548 | 24,371 | 630 | 1,548 | 24,371 | ||||||||||
Suspect soils | 45 cu. ft. box | 10 | 12,102 | 29,669 | 467,884 | 946 | 2,318 | 36,556 | 946 | 2,318 | 36,556 | 946 | 2,318 | 36,556 | ||||||||||
Tritiated soils | 45 cu. ft. box | 10 | 575 | 1,532 | 2,492 | 45 | 119 | 195 | 45 | 119 | 195 | 45 | 119 | 195 | ||||||||||
CIF ashcreteg | 55 gal. drum | 48 | 0 | 0 | 0 | 1,922 | 1,527 | 3,471 | 737 | 947 | 1,033 | |||||||||||||
TRU wastei 10100 nCij | 55 gal. drum | 15 | 3,164 | 4,400 | 252,919 | 1,055 | 1,467 | 84,298 | 1,055 | 1,467 | 84,298 | 1,055 | 1,467 | 84,298 | ||||||||||
TRU wastei>100 nCi, <0.5 Cik | 55 gal. drum | 15 | 2,165 | 3,112 | 51,295 | 722 | 1,036 | 17,097 | 722 | 1,036 | 17,097 | 722 | 1,036 | 17,097 | ||||||||||
TRU wastei>0.5 Cil | 55 gal. drum | 15 | 2,228 | 3,202 | 52,780 | 742 | 1,066 | 17,591 | 742 | 1,066 | 17,591 | 742 | 1,066 | 17,591 | ||||||||||
TRU wastei bulk | Bulk box | 1 | 8,146 | 11,707 | 192,989 | 150 | 215 | 3,547 | 150 | 215 | 3,547 | 150 | 215 | 3,547 | ||||||||||
TRU wastei remote | Bulk box | 1 | 146 | 209 | 3,449 | 3 | 4 | 63 | 3 | 4 | 63 | 3 | 4 | 63 | ||||||||||
OFFSITE SHIPMENTSm | ||||||||||||||||||||||||
Offsite smelter | Railroad Car | 0 | 0 | 0 | 54 | 762 | 332 | 37 | 479 | 173 | ||||||||||||||
LLW offsiteo | 40 ft van | 25m3 | (p) | 0 | 0 | 0 | 18,540 | 30,525 | 77,815 | 0 | 0 | 0 | ||||||||||||
(No-Action) | ||||||||||||||||||||||||
1 | <1 | 1 | 16 | <1 | 1 | 16 | <1 | 1 | 16 | |||||||||||||||
7 | 4 | 7 | 19 | 6 | 9 | 20 | 4 | 7 | 17 |
Source: Rollins (1995).
a. Cubic meters.
b. Expected waste volume is assumed to be the same as for the no-action alternative.
c. Onsite shipments average 8 kilometers (5 miles) each.
d. LLW = low-level waste.
e. Volumes of low-level equipment vary with alternative.
f. ILW = intermediate-level waste.
g. CIF = Consolidated Incineration Facility.
h. Volumes from the Consolidated Incineration Facility
vary depending on alternative. Source: Hess (1994a, b, c, and
d).
i. TRU = transuranic.
j. Includes mixed and nonmixed transuranic waste at 10-100 nanocuries per drum.
k. Includes mixed and nonmixed transuranic waste between 100 nanocuries and 0.5 curies per drum.
l. Includes mixed and nonmixed transuranic waste greater than 0.5 curies per drum.
m. Offsite shipments average 541 kilometers (336 miles) each.
n. Volumes to Offsite Smelter Facility vary with alternative.
o. Includes return shipments of processed waste.
p. Offsite low-level waste shipments vary by alternative.
q. Daily shipments are estimated by totaling all shipments for each alternative/forecast and dividing this sum by 30 years and 250 working days per year.
Table E.3-3. Mixed waste shipments during the 30-year period of interest.
| container | volume (m3) | volume (m3) | shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | shipments | |||||||||||||||
ONSITE SHIPMENTSc | |||||||||||||||||||||||||||
Inorganic debris | 90 cu. ft. box | 6 | 6,240 | 15,170 | 23,516 | 408 | 992 | 1,537 | 408 | 992 | 1537 | 408 | 992 | 1,537 | |||||||||||||
Waste filters | 45 cu. ft. box | 1 | 1,256 | 2,851 | 3,858 | 981 | 2,227 | 3,014 | 981 | 2,236 | 3,014 | 981 | 2,227 | 3,014 | |||||||||||||
Aqueous liquids | 3000 gal. truck | 1 | 8,957 | 32,862 | 51,026 | 788 | 2,893 | 4,492 | 788 | 2,893 | 4,492 | 788 | 2,893 | 4,492 | |||||||||||||
Organic debris | 90 cu. ft. box | 1 | 242 | 241 | 27,769 | 95 | 95 | 10,890 | 95 | 95 | 10,890 | 95 | 95 | 10,890 | |||||||||||||
Organic sludge | 55 gal. drum | 1 | 1,335 | 3,672 | 5,113 | 6,675 | 18,360 | 25,565 | 6,675 | 18,360 | 25,565 | 6,675 | 18,360 | 25,565 | |||||||||||||
Heterogenous debris | 90 cu. ft. box | 2 | 10,594 | 25,699 | 126,967 | 2,077 | 5,039 | 24,896 | 2,077 | 5,039 | 24,896 | 2,077 | 5,039 | 24,896 | |||||||||||||
Gold traps | 55 gal. drum | 1 | 3 | 3 | 3 | 14 | 14 | 14 | 14 | 14 | 14 | 14 | 14 | 14 | |||||||||||||
M-Area glass | 71 gal. drum | 3 | 2,058 | 2,058 | 2,058 | 2,618 | 2,618 | 2,618 | 2,618 | 2,618 | 2,618 | 2,618 | 2,618 | 2,618 | |||||||||||||
Lead | 22.5 cu. ft. box | 1 | 1,280 | 5,956 | 7,677 | 2,009 | 4,675 | 12,052 | 2,009 | 4,675 | 12,052 | 2,009 | 4,675 | 12,052 | |||||||||||||
PUREX solvents | 3000 gal. truck | 1 | 345 | 345 | 345 | 30 | 30 | 30 | 30 | 30 | 30 | 30 | 30 | 30 | |||||||||||||
Organic liquids | 3000 gal. truck | 1 | 1,149 | 2,879 | 7,873 | 101 | 253 | 693 | 101 | 253 | 693 | 101 | 253 | 693 | |||||||||||||
CIF ashcreted | 55 gal. drum | 48 | 4,941 | 13,301 | 82,407 | 4,897 | 445 | 1,331 | 62 | 109 | 849 | ||||||||||||||||
Bulk | Bulk box | 1 | 4,202 | 10,358 | 32,295 | 77 | 190 | 594 | 77 | 190 | 594 | 77 | 190 | 594 | |||||||||||||
Inorganic sludge | 55 gal. drum | 30 | 1,299 | 3,636 | 5,046 | 217 | 606 | 841 | 217 | 606 | 841 | 217 | 606 | 841 | |||||||||||||
Metal debris | 90 cu. ft. box | 4 | 6,768 | 12,897 | 53,719 | 664 | 1,264 | 5,267 | 664 | 1,264 | 5,267 | 664 | 1,264 | 5,267 | |||||||||||||
Soils/sand/rock/gravel | 45 cu. ft. box | 6 | 22,186 | 88,329 | 440,062 | 2,889 | 11,501 | 57,300 | 2,889 | 11,501 | 57,300 | 2,889 | 11,501 | 57,300 | |||||||||||||
Paint waste | 55 gal. drum | 4 | 1,468 | 2,133 | 2,598 | 1,835 | 2,666 | 3,248 | 1,835 | 2,666 | 3,248 | 1,835 | 2,666 | 3,248 | |||||||||||||
Glass debris | 55 gal. drum | 60 | 1,652 | 2,997 | 7,558 | 138 | 250 | 630 | 138 | 250 | 630 | 138 | 250 | 630 | |||||||||||||
OFFSITE SHIPMENTSf | |||||||||||||||||||||||||||
Lead | 22.5 cu. ft. box | 1 | 2,115 | 4,802 | 12,237 | 2,115 | 4,802 | 12,237 | 2,112 | 4,799 | 12,234 | ||||||||||||||||
(No-Action) | |||||||||||||||||||||||||||
8 | 4 | 10 | 33 | 4 | 8 | 22 | 3 | 8 | 22 |
Source: Rollins (1995).
a. Cubic meters.
b. Expected waste volume is assumed to be the same as for the no-action alternative.
c. Onsite shipments average 8 kilometers (5 miles) each.
d. CIF = Consolidated Incineration Facility.
e. Volumes from the Consolidated Incineration Facility vary depending on alternative. Source: Hess (1994a, b, c, and d).
f. Offsite shipments average 541 kilometers (336 miles) each.
g. Volumes to offsite treatment facilities vary with alternative.
h. Daily shipments are estimated by totaling all shipments for each alternative and forecast and dividing this sum by 30 years and 250 working days per year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debris | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcreteg | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:h | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction.
g. Consolidated Incineration Facility does not operate under the no-action alternative so there would be no ashcrete.
h. For incident-free dose, the sum of waste streams 1 through 11 are used to calculate the corresponding dose of low level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitute the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction.
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction.
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
workera | workers | |||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debrisb | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcrete | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint waste | ||||
28. Glass debris | ||||
Totals:g | ||||
Low-level | ||||
Mixed | ||||
Transuranic |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction..
g. For incident-free dose, the sum of waste streams 1 through 12 are used to calculate the corresponding dose of low-level waste in Chapter 4 transportation sections; 12 through 14 and 16 through 28 constitute the mixed waste dose; and 15a through 15e constitutes the transuranic dose. For each waste type, assumes the same individual has maximum exposure to each waste stream in a single year.
1. Tritiated equipment | ||||||||||||||
2. Spent deionizers | ||||||||||||||
3. Low-level job-control | ||||||||||||||
4. Offsite job-control | ||||||||||||||
5. Low-activity equip. | ||||||||||||||
6. Inter.-level job-control | ||||||||||||||
7. Long-lived | ||||||||||||||
8. Tritiated job-control | ||||||||||||||
9. Low-level waste soils | ||||||||||||||
10. Suspect soils | ||||||||||||||
11. Tritiated soils | ||||||||||||||
12. MW inorganic debrisa | ||||||||||||||
13. Mixed waste soil | ||||||||||||||
14. MW comp. filters | ||||||||||||||
15a. 0.01 Ci/m3 TRU wasteb,c | ||||||||||||||
15b. 1.5 Ci/m3 TRU waste | ||||||||||||||
15c. 208 Ci/m3 TRU waste | ||||||||||||||
15d. Bulk eq. TRU waste | ||||||||||||||
15e. Bulk eq. Rmt. TRUd | ||||||||||||||
16. MW aqueous liquids | ||||||||||||||
17. MW organic debris | ||||||||||||||
18. Organic sludge | ||||||||||||||
19. Heterogeneous debris | ||||||||||||||
19a. Lead | ||||||||||||||
20. PUREX solventse |
Table E.3-14. (continued).
21. Organic liquids | ||||||||||||||
22. Ashcretef | ||||||||||||||
23. Bulk Waste | ||||||||||||||
24. Inorganic Sludge | ||||||||||||||
25. Metal Debris | ||||||||||||||
26. Sand/Rock/Gravel | ||||||||||||||
27. Paint Chips/Solids | ||||||||||||||
28. Glass Debris |
Source: Washburn (1995).
a. MW = Mixed waste.
b. Ci/m3 = Curie per cubic meter.
c. TRU = Transuranic.
d. Rmt = Remotely-handled.
e. PUREX = Plutonium-uranium extraction
f. See Table E.3-16.
workers | workers |
| ||
1. Tritiated equipment | ||||
2. Spent deionizers | ||||
3. Low-level job-control | ||||
4. Offsite job-control | ||||
5. Low-activity equip. | ||||
6. Inter.-level job-control | ||||
7. Long-lived low-level waste | ||||
8. Tritiated job-control | ||||
9. Low-level waste soils | ||||
10. Suspect soils | ||||
11. Tritiated soils | ||||
12. MW inorganic debris | ||||
13. Mixed waste soil | ||||
14. MW comp. filters | ||||
15a. 0.01 Ci/m3 TRU wastec,d | ||||
15b. 1.5 Ci/m3 TRU waste | ||||
15c. 208 Ci/m3 TRU waste | ||||
15d. Bulk eq. TRU waste | ||||
15e. Bulk eq. Rmt. TRUe | ||||
16. MW aqueous liquids | ||||
17. MW organic debris | ||||
18. Organic sludge | ||||
19. Heterogeneous debris | ||||
19a. Lead | ||||
20. PUREX solventsf | ||||
21. Organic liquids | ||||
22. Ashcreteg | ||||
23. Bulk waste | ||||
24. Inorganic sludge | ||||
25. Metal debris | ||||
26. Sand/rock/gravel | ||||
27. Paint chips/solids | ||||
28. Glass debris |
Source: Washburn (1995).
a. Dose in rem; all other doses in person-rem.
b. MW = Mixed waste.
c. Ci/m3 = Curie per cubic meter.
d. TRU = Transuranic.
e. Rmt = Remotely-handled.
f. PUREX = Plutonium-uranium extraction.
g. The dose from an accident involving ashcrete varies among alternatives. See Table E.316.
Waste forecast |
population | population | ||
Expected | ||||
Low-level waste | ||||
Mixed waste | ||||
Minimum | ||||
Low-level waste | ||||
Mixed waste | ||||
Maximum | ||||
Low-level waste | ||||
Mixed waste | ||||
Expected | ||||
Low-level waste | ||||
Mixed waste | ||||
Minimum | ||||
Low-level waste | ||||
Mixed waste | ||||
Maximum | ||||
Low-level waste | ||||
Mixed waste | ||||
Expected | ||||
Low-level waste | ||||
Mixed waste | ||||
Minimum | ||||
Low-level waste | ||||
Mixed waste | ||||
Maximum | ||||
Low-level waste | ||||
Mixed waste |
Source: HNUS (1995).
a. The Consolidated Incineration Facility would not operate under the no-action alternative, so no ashcrete would be generated.
b. MEI = Maximally exposed individual.
Low-activity equipmentb | |||||||||
Lead | |||||||||
Low-activity equipmentb | |||||||||
Lead | |||||||||
Low-activity equipmentb | |||||||||
Lead | |||||||||
Low-activity equipment | |||||||||
Lead | |||||||||
Low-level volume reduction | |||||||||
Low-activity equipment | |||||||||
Lead | |||||||||
Low-level volume reduction | |||||||||
Low-activity equipment | |||||||||
Lead | |||||||||
Low-level volume reduction | |||||||||
Low-activity equipment | |||||||||
Lead | |||||||||
Low-activity equipment | |||||||||
Lead | |||||||||
Low-activity equipment | |||||||||
Lead |
Source: Washburn (1995).
a. Remote maximally exposed individual along transportation route. Dose is rem; all others in person-rem.
b. No low-activity equipment would be shipped offsite under alternative A.
c. NA = not applicable.
Table E.3-18. Waste volumes (in cubic meters) shipped in each alternative.
1. Tritiated equipment | 1.18E+03 | 1.18E+03 | 4.61E+02 | 1.62E+03 | 1.18E+03 | 4.61E+02 | 1.62E+03 | 1.18E+03 | 4.61E+02 | 1.62E+03 | ||
2. Spent deionizers | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | 3.00E+01 | ||
3. Low-level job-control | 3.66E+05 | 3.66E+05 | 3.09E+05 | 4.14E+05 | 3.66E+05 | 3.09E+05 | 4.14E+05 | 3.66E+05 | 3.09E+05 | 4.14E+05 | ||
4. Offsite job job-control | 1.26E+04 | 1.26E+04 | 1.26E+04 | 2.52E+04 | 1.26E+04 | 1.26E+04 | 2.52E+04 | 1.26E+04 | 1.26E+04 | 2.52E+04 | ||
5. Low-activity equip. | 1.33E+04 | 6.95E+04 | 3.40E+04 | 2.35E+05 | 5.08E+04 | 2.61E+04 | 1.61E+05 | 3.20E+04 | 1.80E+04 | 8.37E+04 | ||
6. Inter.-level job-control | 2.27E+04 | 2.27E+04 | 1.25E+04 | 2.81E+04 | 2.27E+04 | 1.25E+04 | 2.81E+04 | 2.27E+04 | 1.25E+04 | 2.81E+04 | ||
7. Long-lived | 3.30E+03 | 3.30E+03 | 1.00E+03 | 4.64E+03 | 3.30E+03 | 1.00E+03 | 4.64E+03 | 3.30E+03 | 1.00E+03 | 4.64E+03 | ||
8. Tritiated job-control | 3.86E+03 | 3.86E+03 | 1.56E+03 | 1.34E+05 | 3.86E+03 | 1.56E+03 | 1.34E+05 | 3.86E+03 | 1.56E+03 | 1.34E+05 | ||
9. Low-level waste soils | 1.98E+04 | 1.98E+04 | 8.07E+03 | 3.12E+05 | 1.98E+04 | 8.07E+03 | 3.12E+05 | 1.98E+04 | 8.07E+03 | 3.12E+05 | ||
10. Suspect soils | 2.97E+04 | 2.97E+04 | 1.21E+04 | 4.68E+05 | 2.97E+04 | 1.21E+04 | 4.68E+05 | 2.97E+04 | 1.21E+04 | 4.68E+05 | ||
11. Tritiated soils | 1.53E+03 | 1.53E+03 | 5.75E+02 | 2.49E+03 | 1.53E+03 | 5.75E+02 | 2.49E+03 | 1.53E+03 | 5.75E+02 | 2.49E+03 | ||
12. MW inorganic debrisa | 1.52E+04 | 1.52E+04 | 6.24E+03 | 2.35E+04 | 1.52E+04 | 6.24E+03 | 2.35E+04 | 1.52E+04 | 6.24E+03 | 2.35E+04 | ||
13. Mixed waste soil | 7.56E+04 | 7.56E+04 | 1.90E+04 | 3.77E+05 | 7.56E+04 | 1.90E+04 | 3.77E+05 | 7.56E+04 | 1.90E+04 | 3.77E+05 | ||
14. MW comp. filters | 2.85E+03 | 2.85E+03 | 1.26E+03 | 3.86E+03 | 2.85E+03 | 1.26E+03 | 3.86E+03 | 2.85E+03 | 1.26E+03 | 3.86E+03 | ||
15a. 0.01 ci/m3 TRU wasteb,c | 4.40E+03 | 4.40E+03 | 3.16E+03 | 2.53E+05 | 4.40E+03 | 3.16E+03 | 2.53E+05 | 4.40E+03 | 3.16E+03 | 2.53E+05 | ||
15b. 1.5 ci/m3 TRU waste | 3.11E+03 | 3.11E+03 | 2.16E+03 | 5.13E+04 | 3.11E+03 | 2.16E+03 | 5.13E+04 | 3.11E+03 | 2.16E+03 | 5.13E+04 | ||
15c. 208 ci/m3 TRU waste | 3.20E+03 | 3.20E+03 | 2.23E+03 | 5.28E+04 | 3.20E+03 | 2.23E+03 | 5.28E+04 | 3.20E+03 | 2.23E+03 | 5.28E+04 | ||
15d. Bulk eq. TRU waste | 1.17E+04 | 1.17E+04 | 8.14E+03 | 1.93E+05 | 1.17E+04 | 8.14E+03 | 1.93E+05 | 1.17E+04 | 8.14E+03 | 1.93E+05 | ||
15e. Bulk eq. rmt. TRUd | 2.09E+02 | 2.09E+02 | 1.46E+02 | 3.45E+03 | 2.09E+02 | 1.46E+02 | 3.45E+03 | 2.09E+02 | 1.46E+02 | 3.45E+03 | ||
16. MW aqueous liquids | 3.27E+04 | 3.27E+04 | 8.81E+03 | 5.09E+04 | 3.27E+04 | 8.81E+03 | 5.09E+04 | 3.27E+04 | 8.81E+03 | 5.09E+04 | ||
17. MW organic debris | 2.42E+02 | 2.42E+02 | 2.42E+02 | 2.78E+04 | 2.42E+02 | 2.42E+02 | 2.78E+04 | 2.42E+02 | 2.42E+02 | 2.78E+04 | ||
18. Organic sludge | 3.67E+03 | 3.67E+03 | 1.34E+03 | 5.11E+03 | 3.67E+03 | 1.34E+03 | 5.11E+03 | 3.67E+03 | 1.34E+03 | 5.11E+03 | ||
19. Heterogeneous debris | 2.57E+04 | 2.57E+04 | 1.06E+04 | 1.27E+05 | 2.57E+04 | 1.06E+04 | 1.27E+05 | 2.57E+04 | 1.06E+04 | 1.27E+05 | ||
19a. Lead | 5.96E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | ||
20. PUREX solventse | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | 3.45E+02 | ||
21. Organic liquids | 8.45E+03 | 8.45E+03 | 6.72E+03 | 1.34E+04 | 8.45E+03 | 6.72E+03 | 1.34E+04 | 8.45E+03 | 6.72E+03 | 1.34E+04 | ||
22. Ashcretef | 0.00E+00 |
TE
Table E.3-18. (continued).
23. Bulk waste | 1.04E+04 | 1.04E+04 | 4.20E+03 | 3.23E+04 | 1.04E+04 | 4.20E+03 | 3.23E+04 | 1.04E+04 | 4.20E+03 | 3.23E+04 | ||
24. Inorganic sludge | 3.64E+03 | 3.64E+03 | 1.30E+-3 | 5.05E+03 | 3.64E+03 | 1.30E+-3 | 5.05E+03 | 3.64E+03 | 1.30E+-3 | 5.05E+03 | ||
25. Metal debris | 1.29E+04 | 1.29E+04 | 6.77E+03 | 5.37E+04 | 1.29E+04 | 6.77E+03 | 5.37E+04 | 1.29E+04 | 6.77E+03 | 5.37E+04 | ||
26. Sand/rock/gravel | 1.27E+04 | 1.27E+04 | 3.19E+03 | 6.32E+04 | 1.27E+04 | 3.19E+03 | 6.32E+04 | 1.27E+04 | 3.19E+03 | 6.32E+04 | ||
27. Paint waste | 2.13E+03 | 2.13E+03 | 1.47E+03 | 2.60E+03 | 2.13E+03 | 1.47E+03 | 2.60E+03 | 2.13E+03 | 1.47E+03 | 2.60E+03 | ||
28. Glass debris | 3.00E+03 | 3.00E+03 | 1.65E+03 | 7.56E+03 | 3.00E+03 | 1.65E+03 | 7.56E+03 | 3.00E+03 | 1.65E+03 | 7.56E+03 | ||
29. Low-activity equipmentg | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 1.68E+04 | 8.68E+03 | 5.31E+04 | 1.05E+04 | 5.94E+03 | 2.76E+04 | ||
30. Leadg | 0.00E+00 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | ||
31. Low Level Job Controlh | ||||||||||||
32. Low Activity Equiph | ||||||||||||
33. LLW from Deconh | ||||||||||||
34. Supercompactedh,i | ||||||||||||
35. Incinerate/S'compactedh,i | ||||||||||||
36. Reduce/ Repkg (CIF) h,i | ||||||||||||
37. Reduce/Repkg (vaults)h,i | ||||||||||||
38. Metal / Supercompacth,i | ||||||||||||
39. Supercompacted Equip.h,i | ||||||||||||
40. Supercompacted Deconh,i | ||||||||||||
Onsite totals: Low-level waste | 4.74E+05 | 5.30E+05 | 3.92E+05 | 1.63E+06 | 5.26E+05 | 4.03E+05 | 1.58E+06 | 5.02E+05 | 3.83E+05 | 1.48E+06 | ||
Mixed waste | 2.15E+05 | 3.40E+05 | 1.22E+05 | 1.59E+06 | 2.17E+05 | 1.21E+05 | 8.14E+05 | 2.14E+05 | 7.50E+04 | 8.09E+05 | ||
Transuranic waste | 2.24E+04 | 2.24E+04 | 1.57E+04 | 5.50E+05 | 2.24E+04 | 1.57E+04 | 5.50E+05 | 2.24E+04 | 1.57E+04 | 5.50E+05 | ||
Offsite totals: Low-level waste | 0.00E+00 | 0.00E+00 | 0.00E+00 | 0.00E+00 | 1.05E+04 | 5.94E+03 | 2.76E+04 | |||||
Mixed waste | 0.00E+00 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 | 2.98E+03 | 1.28E+03 | 7.68E+03 |
Source: Washburn (1995), Sinkowski (1995).
a. MW = mixed waste.
b. Ci/m3 = Curies per cubic meter.
c. TRU = transuranic.
d. Rmt. = Remote-handled.
e. PUREX = Plutonium-uranium solution.
f. Ashcrete values are the result of processing of low-level and mixed waste only.
g. Offsite shipments.
h. Low-level volume reduction offsite shipments.
i. Low-level volume reduction return shipments to SRS.
SECTION 4
Table E.4-1. Average number of workers assigned to onsite facilities.
E-Area Vaults | 7 | 7 | 7 | 14 | 7 | 7 | 14 | 3 | 3 | 5 | ||
Containment building | 0 | 10 | 10 | 25 | 10 | 10 | 19 | 10 | 10 | 13 | ||
RCRA-Permitted Disposal Vaults | 1 | 5 | 6 | 11 | 5 | 5 | 11 | 5 | 5 | 11 | ||
Long-Lived Waste Storage Building | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
MW Storage Buildingsb | 39 | 10 | 16 | 67 | 9 | 14 | 65 | 10 | 13 | 65 | ||
Non-alpha vitrification facility | 0 | 0 | 0 | 0 | 0 | 13 | 25 | 51 | 63 | 79 | ||
Shallow land disposal | 8 | 8 | 8 | 16 | 8 | 8 | 16 | 8 | 8 | 16 | ||
TRU waste characterization/certification facilityc | 5 | 26 | 38 | 122 | 20 | 20 | 107 | 20 | 20 | 107 | ||
TRU waste retrieval operations | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | ||
TRU Waste Storage Pads | 14 | 10 | 10 | 96 | 10 | 10 | 97 | 11 | 11 | 99 | ||
Alpha vitrification facility | 0 | 0 | 0 | 0 | 40 | 40 | 119 | 40 | 40 | 119 | ||
Soil sort facility | 0 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | ||
Aqueous and Organic Waste Storage Tanks | 15 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Consolidated Incineration Facility | 0 | 26 | 26 | 26 | 26 | 26 | 26 | 10 | 10 | 10 | ||
F/H-Area Effluent Treatment Facility | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | ||
H-Area Tank Farm | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | 1,562 | ||
Replacement High-Level Waste Evaporator | 15 | 15 | 15 | 15 | 15 | 15 | 15 | 15 | 15 | 15 | ||
Waste removal operations | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | ||
M-Area Compaction Facility | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | ||
MArea Liquid Effluent Treatment Facility | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | ||
M-Area Vendor Treatment Facility | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | ||
SRTC MW Tanks/Ion Exchanged | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | ||
D-Area Ion Exchange Process | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
F-Area Tank Farm | 308 | 308 | 308 | 308 | 308 | 308 | 308 | 308 | 308 | 308 | ||
253-H Compaction Facility | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | ||
Waste management workers (average yearly) | 2,082 | 2,098 | 2,117 | 2,373 | 2,131 | 2,148 | 2,495 | 2,163 | 2,178 | 2,520 |
a. Source: Hess (1994e).
b. MW = mixed waste.
c. TRU = transuranic.
d. SRTC = Savannah River Technology Center.
No-Action | |||||||||||
E-Area Vaults | 16 | 112 | 112 | 112 | 224 | 112 | 112 | 224 | 41 | 41 | 82 |
Containment building | 250 | 0 | 2,375 | 2,375 | 6,333 | 2,375 | 2,375 | 4,750 | 2,375 | 2,375 | 3,167 |
RCRA-Permitted Disposal Vaults | 16 | 12 | 86 | 97 | 172 | 86 | 86 | 172 | 86 | 86 | 172 |
Long-Lived Waste Storage Building | 16 | 16 | 16 | 16 | 16 | 16 | 16 | 16 | 16 | 16 | 16 |
MW Storage Buildingsc | 16 | 624 | 160 | 256 | 1,072 | 144 | 224 | 1,040 | 160 | 208 | 1,040 |
Non-alpha vitrification facility | 250 | 0 | 0 | 0 | 0 | 0 | 3167 | 6,333 | 12,667 | 15,833 | 19,792 |
Shallow Land Disposal | 16 | 128 | 128 | 128 | 256 | 128 | 128 | 256 | 128 | 128 | 256 |
TRU waste characterization/certification facilityd | 220 | 1,100 | 5,720 | 8,360 | 26,840 | 4,400 | 4,400 | 23,540 | 4,400 | 4,400 | 23,540 |
TRU waste retrieval operations | 220 | 880 | 880 | 880 | 880 | 880 | 880 | 880 | 880 | 880 | 880 |
TRU Waste Storage Pads | 220 | 3,080 | 2,200 | 2,200 | 21,120 | 2,200 | 2,200 | 21,340 | 2,420 | 2,420 | 21,780 |
Alpha vitrification facility | 250 | 0 | 0 | 0 | 0 | 9,917 | 9,917 | 29,750 | 9,917 | 9,917 | 29,750 |
Soil sort facility | 220 | 0 | 697 | 697 | 697 | 697 | 697 | 697 | 697 | 697 | 697 |
Aqueous and Organic Waste Storage Tanks | 16 | 240 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Consolidated Incineration Facility | 350 | 0 | 9,135 | 9,135 | 9,135 | 9,135 | 9,135 | 9,135 | 3,465 | 3,465 | 3,465 |
F/H-Area Effluent Treatment Facility | 1 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 | 40 |
H-Area Tank Farm | 21 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 | 32,804 |
Replacement High-Level Waste Evaporator | 149 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 | 2,235 |
Waste removal operations | 21 | 210 | 210 | 210 | 210 | 210 | 210 | 210 | 210 | 210 | 210 |
M-Area Compaction Facility | 1 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 |
MArea Liquid Effluent Treatment Facility | 1 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 | 31 |
M-Area Vendor Treatment Facility | 250 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 | 2,500 |
SRTC MW Tanks/Ion Exchangee | 8 | 32 | 32 | 32 | 32 | 32 | 32 | 32 | 32 | 32 | 32 |
D-Area Ion Exchange Process | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 |
F-Area Tank Farm | 26 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 | 8,000 |
253-H Compaction Facility | 1 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 | 3 |
Total annual dose, person-millirem | 52,000 | 67,000 | 70,000 | 113,000 | 76,000 | 79,000 | 144,000 | 83,000 | 86,000 | 150,000 | |
Average worker dosef, millirem per year | 25 | 32 | 33 | 47 | 36 | 37 | 58 | 38 | 40 | 60 |
a. Source: Hess (1994e).
b. Average annual dose for a facility worker.
c. MW = mixed waste.
d. TRU = transuranic.
e. SRTC = Savannah River Technology Center.
f. Average annual worker dose from all facilities.
| |||||||||||||
Consolidated Incineration Facility | 0.09 | 0.212 | 0.568 | 0.255 | 0.318 | 0.689 | |||||||
Compaction facilities | 1.55E-06 | 1.55E-06 | 1.55E-06 | 1.55E-06 | 5.18-08 | 5.18E-08 | 5.18E-08 | ||||||
Onsite vitrification facilities | (b) | 0.315 | 0.561 | 8.08 | 2.56 | 5.20 | 118 | ||||||
M-Area Vendor Treatment Facilityc | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | 0.00371 | |||
Soil sort facilities | (b) | 2.58E-06 | 1.28E-05 | 8.17E-07 | 2.87E-06 | 1.75E-05 | 5.52E-07 | 2.03E-06 | 1.18E-05 | ||||
Transuranic waste characterization/certification facility | (b) | 0.111 | 1.83 | 0.0775 | 0.111 | 1.83 | 0.0775 | 0.110 | 1.83 | ||||
F/H-Area Effluent Treatment Facility | (d) | (d) | (d) | ||||||||||
Containment building | 1.22E-06 | 2. 41E-06 | 8.26E-06 | 7.99E-07 | 1.59E-06 | 5.55E-06 | 3.24E-07 | 6.82E-07 | 2.51E-06 | ||||
30-year total | 0.0037 | 0.171 | 0.327 | 2.41 | 0.651 | 0.994 | 10.6 | 2.71 | 5.40 | 120 | |||
Average annual dosee
| 1.24E-04 | 0.00571 | 0.0109 | 0.802 | 0.217 | 0.331 | 0.354 | 0.0902 | 0.18 | 4.02 | |||
Supercompaction, sorting | 6.66E-06 | 1.52E-05 | 3.88E-05 | 3.83E-04 | 4.85E-04 | 6.86E-04 | 6.66E-06 | 1.52E-05 | 3.88E-05 | ||||
Smelt, incinerate, metal melt | 0.0377 | 0.0514 | 0.0927 | 0.00607 | 0.0108 | 0.0284 | |||||||
30-year total | 6.66E-06 | 1.52E-05 | 3.88E-05 | 0.0381 | 0.0519 | 0.0934 | 0.00608 | 0.0108 | 0.0284 | ||||
Average annual dosee | 2.22E-07 | 5.08E-07 | 1.29E-06 | 0.00127 | 0.00173 | 0.00311 | 2.03E-04 | 3.61E-04 | 9.47E-04 |
Source: Chesney (1995).
a. Except where noted, the doses reported are for
the 30-year period of interest.
b. Facility not operated in this alternative.
c. Doses are calculated from the center of SRS due to unavailability of other population data.
d. Routine operations are not expected to provide atmospheric releases.
e. Offsite-maximally-exposed individual average annual dose is determined by dividing the 30-year dose by 30. For onsite facilities the offsite maximally exposed individual is within 80 kilometers (50 miles) of SRS. For offsite facilities the offsite maximally exposed individual is considered to be within 80 kilometers (50 miles) of Oak Ridge, Tennessee.
Consolidated Incineration Facility | 5.31 | 12.6 | 33.9 | 15.1 | 18.8 | 36.2 | |||||
Compaction facilities | 6.15E-05 | 6.15E-05 | 6.15E-05 | 6.15E-05 | 2.05E-06 | 2.05E-06 | 2.05E-06 | ||||
Onsite vitrification facilities | 12.5 | 24.4 | 330 | 141 | 293 | 6,790 | |||||
M-Area Vendor Treatment Facilityc | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | 0.00851 | |
Soil sort facilities | 2.75E-05 | 1.02E-04 | 5.08E-04 | 3.23E-05 | 1.14E-04 | 6.93E-04 | 2.56E-05 | 9.38E-05 | 5.47E-04 | ||
Transuranic waste characterization/ certification facility | 2.92 | 4.19 | 69.1 | 2.92 | 4.19 | 69.1 | 2.92 | 4.19 | 69.1 | ||
F/H-Area Effluent Treatment Facility | (d) | ||||||||||
Containment building | 4.83E-05 | 9.56E-05 | 3.27E-04 | 3.16E-05 | 6.31E-05 | 2.20E-04 | 1.28E-05 | 2.70E-05 | 9.93E-05 | ||
30-year total | 0.0857 | 8.24 | 16.8 | 103 | 30.5 | 47.4 | 436 | 148 | 302 | 6,880 | |
Average annual dosee
| 2.86E-04 | 0.275 | 0.560 | 3.43 | 1.02 | 1.58 | 14.5 | 4.92 | 10.1 | 220 | |
Offsite facilities | |||||||||||
Supercompaction, sorting | 3.03E-06 | 6.93E-06 | 1.77E-05 | 1.74E-04 | 2.21E-04 | 3.13E-04 | 3.03E-06 | 6.93E-06 | 1.77E-05 | ||
Smelt, incinerate, metal melt | 0.251 | 0.346 | 0.624 | 0.0409 | 0.0728 | 0.191 | |||||
30-year total | 3.03E-06 | 6.93E-06 | 1.77E-05 | 0.254 | 0.346 | 0.625 | 0.0409 | 0.0728 | 0.191 | ||
Average annual dosee | 1.01E-07 | 2.31E-07 | 5.89E-07 | 0.00847 | 0.0115 | 0.0208 | 0.00136 | 0.00243 | 0.00637 |
Source: Chesney (1995).
a. Except where noted, the doses reported are for the 30-year period of interest.
b. Facility not operated in this alternative.
c. Doses are calculated from the center of SRS due to unavailability of other population data.
d. Routine operations are not expected to provide atmospheric releases.
e. Average annual dose is determined by dividing the 30-year dose by 30. For onsite facilities the offsite maximally exposed individual is within 80 kilometers (50 miles) of SRS. For offsite facilities the offsite maximally exposed individual is considered to be within 80 kilometers (50 miles) of Oak Ridge, Tennessee.
Consolidated Incineration Facility | 1.77 | 4.25 | 11.5 | 5.07c | 6.28 | 9.76 | 1.32 | 1.81 | 4.12 | ||
Compaction facilities | 6.01E-05 | 6.01E-05 | 6.01E-05 | 6.01E-05 | 2.00E-06 | 2.00E-06 | 2.00E-06 | 7.67E-06 | 9.27E-06 | 9.59E-06 | |
Onsite vitrification facilities | 1.60 | 4.52 | 48.8 | 42.7 | 92 | 219 | |||||
M-Area Vendor Treatment Facility | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | 0.00856 | |
Soil sort facilities | 2.69E-05 | 9.95E-05 | 4.96E-04 | 3.16E-05 | 1.11E-04 | 6.76E-04 | 6.76E-06 | 2.48E-05 | 1.45E-04 | ||
Transuranic waste characterization/ certification facility | 3.26 | 4.68 | 77.1 | 3.26 | 4.68 | 77.1 | 3.26 | 4.68 | 77.1 | ||
F/H-Area Effluent Treatment Facility | (d) | ||||||||||
Containment building | 4.72E-05 | 9.33E-05 | 3.19E-04 | 3.09E-05 | 6.16E-05 | 2.14E-04 | 1.25E-05 | 2.64E-05 | 9.69E-05 | ||
Average annual dosee
| 2.85E-04 | 0.0109 | 0.156 | 2.57 | 0.169 | 0.209 | 2.57 | 1.42 | 3.07 | 73 | |
Supercompaction, sorting | |||||||||||
Smelt, incinerate, metal melt |
Source: Chesney (1995).
a. Except where noted, the doses reported are for a 30-year period of interest.
b. Facility not operated in this alternative.
c. Italics indicate the facility that would produce the highest dose to any individual under each alternative/forecast. This maximum dose was used to calculate the average annual dose.
d. Routine operations are not expected to provide atmospheric releases.
e. Maximally exposed individual doses are not added; average annual dose is determined by dividing the 30-year dose from the highest impact facility (shown in italics) by 30.
f. The 640 meter worker is a receptor unique to DOE and is not evaluated by the Nuclear Regulatory Commission or agreement state licensees.
Consolidated Incineration Facility | 5.14 | 12.2 | 32.8 | 14.6 | 18.1 | 32.4 | 3.80 | 5.23 | 12 | ||
Compaction facilities | 0.00169 | 0.00169 | 0.00169 | 0.00169 | 5.64E-05 | 5.64E-05 | 5.64E-05 | ||||
Onsite vitrification facilities | 12.2 | 23.8 | 323 | 136c | 283 | 6,580 | |||||
M-Area Vendor Treatment Facility | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | 0.304 | |
Soil sort facilities | 7.57E-04 | 0.0028 | 0.014 | 8.88E-04 | 0.00312 | 0.019 | 2.56E-05 | 9.40E-05 | 5.47E-04 | ||
Transuranic waste characterization/ certification facility | 112 | 161 | 2,650 | 112 | 161 | 2,650 | 111 | 161 | 2,650 | ||
F/H-Area Effluent Treatment Facility | |||||||||||
Containment building | 0.00133 | 0.00263 | 0.00899 | 8.69E-04 | 0.00173 | 0.00604 | 3.53E-04 | 7.42E-04 | 0.00273 | ||
Average annual dosee
| 0.0102 | 3.73 | 5.37 | 88.3 | 3.73 | 5.37 | 88.3 | 4.53 | 9.43 | 219 | |
Supercompaction, sorting | (f) | ||||||||||
Smelt, incinerate, metal melt |
Source: Chesney (1995).
a. Except where noted, the doses reported are for a 30-year period of interest.
b. Facility not operated in this alternative.
c. Italics indicate the facility that would produce the highest dose to any individual under each alternative/forecast. This maximum dose was used to calculate the average annual dose.
d. Routine operations are not expected to provide atmospheric releases.
e. Maximally exposed individual doses are not added; average annual dose is determined by dividing the 30-year dose from the highest impact facility (shown in italics) by 30.
f. The 100 meter worker is a receptor unique to DOE and is not evaluated by the Nuclear Regulatory Commission or agreement state licensees.
| ||||||||||
Consolidated Incineration Facility | ||||||||||
Compaction facilities | ||||||||||
Onsite vitrification facilities | ||||||||||
M-Area Vendor Treatment Facility | ||||||||||
Soil sort facilities | ||||||||||
Transuranic waste characterization/certification facility | ||||||||||
F/H-Area Effluent Treatment Facility | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 |
Containment building | 2.07E-05 | 1.41E-05 | ||||||||
30-year total | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 | 0.0208 |
Average annual dose
| 6.93E-04 | 6.93E-04 | 6.93E-04 | 6.94E-04 | 6.93E-04 | 6.93E-04 | 6.94E-04 | 6.93E-04 | 6.93E-04 | 6.94E-04 |
Offsite facilities | ||||||||||
Supercompaction, sorting | ||||||||||
Smelt, incinerate, metal melt |
Source: Chesney (1995).
a. Except where noted, the doses reported are for a 30-year period
of interest.
b. Facility not operated in this alternative.
c. Routine operations are not expected to provide liquid releases.
Consolidated Incineration Facility | |||||||||||
Compaction facilities | |||||||||||
Onsite vitrification facilities | |||||||||||
M-Area Vendor Treatment Facility | |||||||||||
Soil sort facilities | |||||||||||
Transuranic waste characterization/ certification facility | |||||||||||
F/H-Area Effluent Treatment Facility | |||||||||||
Containment building | 1.82E-04 | 1.24E-04 | |||||||||
30-year total | |||||||||||
Average annual dose
| 0.00678 | 0.00678 | 0.00678 | 0.00679 | 0.00678 | 0.00678 | 0.00679 | 0.00678 | 0.00678 | 0.00678 | |
Offsite facilities | |||||||||||
Supercompaction, sorting | |||||||||||
Smelter, incinerator, metal metal |
Source: Chesney (1995).
a. Except where noted, the doses reported are for the 30-year period of interest.
b. Facility not operated in this alternative.
c. Routine operations are not expected to provide liquid releases.
Table E.4-9. Compactor facility dose distribution by isotope for the no-action alternative.
| (2,100 feet) | |||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0e | <1.0e | 1.51 | <1.0e |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0e | <1.0e | <1.0e | 1.35 |
Ruthenium-106 | 1.13 | <1.0e | <1.0e | <1.0e |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Otherf | 3.88 | 4.28 | 3.62 | 4.13 |
Total doseg,h |
Source: Blankenhorn (1994); Hess (1994f, g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Dose to 640-meter and 100-meter uninvolved workers are based on an 80-hour work week.
e. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" category.
f. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
g. Dose refers to committed effective dose equivalent (see glossary).
h. Total doses are for the 30-year period of interest.
Table E.4-10. Consolidated Incineration Facilitydose distribution by isotope for alternative A.
| (2,100 feet) | |||
Cobalt-60 | 2.29 | <1.0d | 3.33 | 3.38 |
Cesium-134 | 20.25 | 11.00 | 16.03 | 15.89 |
Cesium-137 | 66.44 | 81.97 | 78.79 | 77.00 |
Strontium-90 | 7.62 | 2.83 | <1.0d | <1.0d |
Othere | 3.40 | 4.20 | 1.75 | 3.74 |
Total dosef,g | ||||
Expected | 0.21 | 12.60 | 4.25 | 12.20 |
Maximum | 0.57 | 34.00 | 11.50 | 32.80 |
Minimum | 0.090 | 5.31 | 1.77 | 5.14 |
Source: Blankenhorn (1994); Hertel et al. (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose is to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-11. Compactor facilities dose distribution by isotope for alternative A.
| (2,100 feet) | |||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0d | <1.0d | 1.51 | <1.0d |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | 1.35 |
Ruthenium-106 | 1.13 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Othere | 3.88 | 4.28 | 3.62 | 4.13 |
Total dosef,g | ||||
Expected | 1.55E-06 | 6.15E-05 | 6.01E-05 | 1.69E-03 |
Maximum | 1.55E-06 | 6.15E-05 | 6.01E-05 | 1.69E-03 |
Minimum | 1.55E-06 | 6.15E-05 | 6.01E-05 | 1.69E-03 |
Source: Blankenhorn (1994); Hess (1994f, g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-12. Soil sort facility dose distribution by isotope for alternative A.
| (2,100 feet) | |||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0d | <1.0d | 1.51 | <1.0d |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | 1.35 |
Ruthenium-106 | 1.13 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Othere | 3.88 | 4.28 | 3.62 | 4.13 |
Total dosef,g | ||||
Expected | 2.58E-06 | 1.02E-04 | 9.95E-05 | 2.80E-03 |
Maximum | 1.28E-05 | 5.08E-04 | 4.96E-04 | 1.40E-02 |
Minimum | 6.96E-07 | 2.75E-05 | 2.69E-05 | 7.57E-04 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
| (2,100 feet) | |||
Plutonium-238 | 83.65 | 83.66 | 83.85 | 83.89 |
Plutonium-239 | 15.38 | 15.37 | 15.17 | 15.13 |
Otherd | 0.97 | 0.97 | 0.98 | 0.98 |
Total dosee,f | ||||
Expected | 0.111 | 4.19 | 4.68 | 161 |
Maximum | 1.83 | 69.1 | 77 | 2.650 |
Minimum | 0.0775 | 2.92 | 3.26 | 112 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
Table E.4-14. Containment building dose distribution by isotope for alternative A.
(percent of total dose) | (percent of total dose) | ||||||
| (2,100 feet) | (328 feet) |
| ||||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 | <1.0c | 5.97 | |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 | 81.85 | 21.81 | |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 | <1.0c | <1.0c | |
Europium-154 | <1.0c | <1.0c | 1.51 | <1.0c | <1.0c | <1.0c | |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 | 10.51 | 32.22 | |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 | 4.62 | 28.48 | |
Plutonium-239 | <1.0c | <1.0c | <1.0c | 1.35 | <1.0c | <1.0c | |
Ruthenium-106 | 1.13 | <1.0c | <1.0c | <1.0c | <1.0c | 2.37 | |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 | <1.0c | <1.0c | |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 | <1.0c | <1.0c | |
Otherd | 3.88 | 4.28 | 3.62 | 4.13 | 3.02 | 9.17 | |
Total dosee,f | |||||||
Expected | 2.41E-06 | 9.56E-05 | 9.33E-05 | 0.00263 | |||
Maximum | 8.26E-06 | 3.27E-04 | 3.19E-04 | 0.00899 | |||
Minimum | 1.22E-06 | 4.83E-05 | 4.72E-05 | 0.00133 |
Source: Blankenhorn (1994); Hess (1994g, h); Simpkins (1994a); and Chesney (1995).
a. MEI = maximally exposed individual.
b. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS. For aqueous releases, the dose is to the people using the Savannah River from SRS to the Atlantic Ocean.
c. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
g. Routine operations are not expected to produce aqueous releases.
Table E.4-15. Mixed wasteoffsite vendor dose distribution by isotope for alternative A.
Cesium-134 | <1.0d | 1.62 |
Cesium-137 | 1.68 | 1.92 |
Tritium | 75.92 | 32.52 |
Plutonium-238 | 13.54 | 44.04 |
Plutonium-239 | <1.0d | 1.39 |
Strontium-90 | 1.49 | <1.0d |
Uranium-234 | 3.68 | 12.12 |
Uranium-236 | <1.0d | 2.13 |
Othere | 3.69 | 4.26 |
Total dosef,g | ||
Expected | 1.52E-05 | 6.93E-06 |
Maximum | 3.88E-05 | 1.77E-05 |
Minimum | 6.66E-06 | 3.03E-06 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-16. Consolidated Incineration Facilitydose distribution by isotope for alternative B.
| (2,100 feet) | |||
Cobalt-60 | 2.26 | 1.72 | 3.32 | 3.33 |
Cesium-134 | 19.92 | 10.88 | 15.99 | 15.78 |
Cesium-137 | 65.28 | 80.97 | 78.62 | 76.38 |
Strontium-90 | 7.50 | 2.80 | <1.0d | <1.0d |
Tritium | 2.30 | <1.0d | <1.0d | <1.0d |
Othere | 2.74 | 3.63 | 2.06 | 4.48 |
Total dosef,g | ||||
Expected | 0.318 | 18.8 | 6.28 | 18.1 |
Maximum | 0.689 | 32.6 | 9.76 | 32.4 |
Minimum | 0.255 | 15.1 | 5.07 | 14.6 |
Source: Blankenhorn (1994); Hertel et al. (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose is to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-17. Onsite compactor facility dose distribution by isotope for alternative B.
| (2,100 feet) | |||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0d | <1.0d | 1.51 | <1.0d |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | 1.35 |
Ruthenium-106 | 1.13 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Othere | 3.88 | 4.28 | 3.62 | 4.13 |
Total dosef,g | ||||
Expected | 5.18E-08 | 2.05E-06 | 2.00E-06 | 5.64E-05 |
Maximum | 5.18E-08 | 2.06E-06 | 2.00E-06 | 5.64E-05 |
Minimum | 5.18E-08 | 2.05E-06 | 2.00E-06 | 5.64E-05 |
Source: Blankenhorn (1994); Hess (1994f, g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" category.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-18. Onsite vitrificationfacilities dose distribution by isotope for alternative B.
| (2,100 feet) | |||
Cesium-134 | 4.04 | 3.00 | 7.97 | 4.30 |
Cesium-137 | 13.21 | 22.25 | 39.07 | 20.75 |
Plutonium-238 | 67.42 | 61.29 | 42.37 | 61.47 |
Plutonium-239 | 12.26 | 11.16 | 7.80 | 11.16 |
Otherd | 3.07 | 2.30 | 2.79 | 2.31 |
Total dosee,f | ||||
Expected | 0.561 | 24.4 | 4.52 | 23.8 |
Maximum | 8.08 | 330 | 48.8 | 323 |
Minimum | 0.315 | 12.5 | 1.60 | 12.2 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
Table E.4-19. Soil sort facility dose distribution by isotope for alternative B.
| (2,100 feet) | uninvolved worker (328 feet) | ||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0d | <1.0d | 1.51 | <1.0d |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | 1.35 |
Ruthenium-106 | 1.13 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Othere | 3.88 | 4.28 | 3.62 | 4.13 |
Total dosef,g | ||||
Expected | 2.87E-06 | 1.14E-04 | 1.11E-04 | 0.00312 |
Maximum | 1.75E-05 | 6.93E-04 | 6.76E-04 | 0.0190 |
Minimum | 8.17E-07 | 3.23E-05 | 3.16E-05 | 8.88E-04 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
| (2,100 feet) | |||
Plutonium-238 | 83.65 | 83.66 | 83.85 | 83.89 |
Plutonium-239 | 15.38 | 15.37 | 15.17 | 15.13 |
Otherd | 0.97 | 0.97 | 0.98 | 0.98 |
Total dosee,f | ||||
Expected | 0.111 | 4.19 | 4.68 | 161 |
Maximum | 1.83 | 69.1 | 77.1 | 2,650 |
Minimum | 0.0775 | 2.92 | 3.26 | 112 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
Table E.4-21. Containment building dose distribution by isotope for alternative B.
(percent of total dose) | (percent of total dose) | ||||||
|
| (328 feet) |
| ||||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 | <1.0c | 5.97 | |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 | 81.85 | 21.81 | |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 | <1.0c | <1.0c | |
Europium-154 | <1.0c | <1.0c | 1.51 | <1.0c | <1.0c | <1.0c | |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 | 10.51 | 32.22 | |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 | 4.62 | 28.48 | |
Plutonium-239 | <1.0c | <1.0c | <1.0c | 1.35 | <1.0c | <1.0c | |
Ruthenium-106 | 1.13 | <1.0c | <1.0c | <1.0c | <1.0c | 2.37 | |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 | <1.0c | <1.0c | |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 | <1.0c | <1.0c | |
Otherd | 3.88 | 4.28 | 3.62 | 4.13 | 3.02 | 9.17 | |
Total dosee,f | |||||||
Expected | |||||||
Maximum | |||||||
Minimum |
Source: Blankenhorn (1994); Hess (1994g, h); Simpkins (1994a); and Chesney (1995).
a. MEI = maximally exposed individual.
b. For atmospheric releases, the dose to the population populationwithin 80 kilometers (50 miles) of SRS. For aqueous releases, the dose is to the people using the Savannah River Savannah Riverfrom SRS to the Atlantic.
c. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
g. Routine operations are not expected to produce aqueous releases.
Cesium-134 | <1.0d | 1.62 |
Cesium-137 | 1.68 | 1.92 |
Tritium | 75.92 | 32.52 |
Plutonium-238 | 13.54 | 44.04 |
Plutonium-239 | <1.0d | 1.39 |
Strontium-90 | 1.49 | <1.0d |
Uranium-234 | 3.68 | 12.12 |
Uranium-236 | <1.0d | 2.13 |
Othere | 3.69 | 4.26 |
Total dosef,g | ||
Expected | 4.85E-04 | 2.21E-04 |
Maximum | 6.86E-04 | 3.13E-04 |
Minimum | 3.83E-04 | 1.74E-04 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Cesium-134 | 31.68 | 31.37 |
Cesium-137 | 44.16 | 36.07 |
Strontium-90 | 11.09 | 3.18 |
Uranium-234 | 9.24 | 21.21 |
Uranium-236 | <1.0d | 3.71 |
Othere | 3.83 | 4.46 |
Total dosef,g | ||
Expected | 0.0514 | 0.346 |
Maximum | 0.0927 | 0.624 |
Minimum | 0.0377 | 0.254 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-24. Consolidated Incineration Facilitydose distribution by isotope for alternative C.
| (2,100 feet) | (328 feet) | ||
Cobalt-60 | 2.26 | 1.72 | 3.32 | 3.35 |
Cesium-134 | 19.93 | 10.88 | 15.97 | 15.77 |
Cesium-137 | 65.45 | 81.11 | 78.67 | 76.46 |
Strontium-90 | 7.50 | 2.80 | <1.0d | <1.0d |
Othere | 4.86 | 3.49 | 2.04 | 4.42 |
Total dosef,g | ||||
Expected | 0.091 | 5.42 | 1.81 | 5.23 |
Maximum | 0.215 | 12.60 | 4.12 | 12.00 |
Minimum | 0.0667 | 3.95 | 1.32 | 3.81 |
Source: Blankenhorn (1994); Hertel et al. (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose is to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-25. Compactor facilities dose distribution by isotope for alternative C.
| (2,100 feet) | |||
Cobalt-60 | 7.08 | 6.13 | 11.21 | 8.56 |
Cesium-134 | 6.13 | 3.94 | 5.15 | 3.90 |
Cesium-137 | 19.81 | 28.86 | 25.85 | 19.39 |
Europium-154 | <1.0d | <1.0d | 1.51 | <1.0d |
Tritium | 18.44 | 18.31 | 11.37 | 12.11 |
Plutonium-238 | 31.18 | 29.68 | 33.96 | 41.53 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | 1.35 |
Ruthenium-106 | 1.13 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 8.36 | 4.44 | 1.75 | 2.16 |
Uranium-234 | 3.99 | 4.37 | 5.57 | 6.87 |
Othere | 3.88 | 4.28 | 3.62 | 4.13 |
Total dosef,g | ||||
Expected | 2.40E-07 | 9.49E-06 | 9.27E-06 | 2.61E-04 |
Maximum | 2.48E-07 | 9.82E-06 | 9.59E-06 | 2.70E-04 |
Minimum | 1.99E-07 | 7.86E-06 | 7.67E-06 | 2.16E-04 |
Source: Blankenhorn (1994); Hess (1994f, g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-26. Onsite vitrificationfacilities dose distribution by isotope for alternative C.
| (2,100 feet) | (328 feet) | ||
Cobalt-60 | <1.0d | <1.0d | 3.11 | 2.94 |
Strontium-90 | 6.41 | 2.51 | <1.0d | <1.0d |
Cesium-134 | 17.13 | 9.82 | 15.37 | 14.21 |
Cesium-137 | 56.08 | 22.99 | 75.48 | 68.69 |
Plutonium-238 | 13.96 | 9.81 | 3.99 | 9.93 |
Plutonium-239 | 2.54 | <1.0d | <1.0d | <1.0d |
Othere | 3.88 | 4.86 | 2.05 | 4.24 |
Total dosef,g | ||||
Expected | 5.20 | 293 | 92 | 283 |
Maximum | 118 | 6,790 | 2,190 | 6,580 |
Minimum | 2.56 | 141 | 42.70 | 136 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-27. Soil sort facility dose distribution by isotope for alternative C.
| (2,100 feet) | (328 feet) | ||
Cobalt-60 | 8.37 | 8.14 | 19.89 | 15.29 |
Cesium-134 | 7.38 | 5.15 | 9.57 | 7.19 |
Cesium-137 | 24.12 | 38.23 | 46.91 | 34.70 |
Europium-154 | <1.0d | <1.0d | 2.78 | 2.15 |
Tritium | 11.81 | 10.41 | 3.89 | 7.38 |
Plutonium-238 | 29.92 | 25.60 | 12.37 | 24.98 |
Plutonium-239 | <1.0d | <1.0d | <1.0d | <1.0d |
Ruthenium-106 | 1.32 | <1.0d | <1.0d | <1.0d |
Strontium-90 | 9.92 | 4.74 | <1.0d | <1.0d |
Uranium-234 | 3.34 | 3.49 | <1.0d | 4.15 |
Othere | 3.82 | 4.24 | 4.58 | 4.16 |
Total dosef,g | ||||
Expected | ||||
Maximum | ||||
Minimum |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
| (2,100 feet) | (328 feet) | ||
Plutonium-238 | 83.65 | 83.66 | 83.85 | 83.89 |
Plutonium-239 | 15.38 | 15.37 | 15.17 | 15.13 |
Otherd | 0.97 | 0.97 | 0.98 | 0.98 |
Total dosee,f | Millirem | |||
Expected | 0.111 | 4.19 | 4.68 | 161 |
Maximum | 1.83 | 69.1 | 77 | 2,650 |
Minimum | 0.0775 | 2.92 | 3.26 | 112 |
Source: Blankenhorn (1995); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
Table E.4-29. Containment building dose distribution by isotope for alternative C.
| (2,100 feet) | uninvolved worker (328 feet) | ||
Cobalt-60 | <1.0d | <1.0d | <1.0d | <1.0d |
Cesium-134 | <1.0d | <1.0d | <1.0d | <1.0d |
Cesium-137 | <1.0d | <1.0d | <1.0d | <1.0d |
Europium-154 | <1.0d | <1.0d | <1.0d | <1.0d |
Tritiume | 99 | 99 | 99 | 99 |
Plutonium-238 | <1.0d | <1.0d | <1.0d | <1.0d |
Plutonium-239 | <1.0d | <1.0d | <1.0d | <1.0d |
Ruthenium-106 | <1.0d | <1.0d | <1.0d | <1.0d |
Strontium-90 | <1.0d | <1.0d | <1.0d | <1.0d |
Uranium-234 | <1.0d | <1.0d | <1.0d | <1.0d |
Otherf | <1.0d | <1.0d | <1.0d | <1.0d |
Total doseg,h | ||||
Expected | ||||
Maximum | ||||
Minimum |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Tritium releases due to processing of tritium contaminated mercury pumps.
f. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
g. Dose refers to committed effective dose equivalent (see glossary).
h. Total doses are for the 30-year period of interest.
Table E.4-30. Mixed wasteoffsite vendor dose distribution by isotope for alternative C.
Cesium-134 | <1.0d | 1.62 |
Cesium-137 | 1.68 | 1.92 |
Tritium | 75.92 | 32.52 |
Plutonium-238 | 13.54 | 44.04 |
Plutonium-239 | <1.0d | 1.39 |
Strontium-90 | 1.49 | <1.0d |
Uranium-234 | 3.68 | 12.12 |
Uranium-236 | <1.0d | 2.13 |
Othere | 3.69 | 4.26 |
Total dosef,g | ||
Expected | ||
Maximum | ||
Minimum |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Table E.4-31. Offsite smelter dose distribution by isotope for alternative C.
Cesium-134 | 31.68 | 31.37 |
Cesium-137 | 44.16 | 36.07 |
Strontium-90 | 11.09 | 3.18 |
Uranium-234 | 9.24 | 21.21 |
Uranium-236 | <1.0d | 3.71 |
Othere | 3.83 | 4.46 |
Total dosef,g | ||
Expected | 0.0108 | 0.0728 |
Maximum | 0.0284 | 0.191 |
Minimum | 0.00607 | 0.0409 |
Source: Blankenhorn (1994); Hess (1994g); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. The contribution from this radionuclide to the given receptor is less than or equal to 1.0 percent and is accounted for in the "Other" total.
e. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
f. Dose refers to committed effective dose equivalent (see glossary).
g. Total doses are for the 30-year period of interest.
Cesium-137 | 70.52 | 18.79 |
Tritium | 28.95 | 79.91 |
Otherd | .053 | 1.30 |
Total dosee,f,g | 0.0208 | 0.203 |
Source: Blankenhorn (1994); Hess (1994g, i); Poirier and Wiggins (1994), Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce atmospheric releases.
b. MEI = maximally exposed individual.
c. For aqueous releases, the dose is to the people using the Savannah River from SRS to Atlantic Ocean.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
g. Includes releases from processing of Defense Waste Processing Facility recycle. Remains essentially constant for all alternatives.
Table E.4-33. M-Area Vendor Treatment Facility dose distribution by isotope for all alternatives.
| (2,100 feet) | (328 feet) | ||
Uranium-234 | 32.67 | 31.49 | 32.10 | 32.31 |
Uranium-238 | 64.93 | 65.98 | 65.48 | 65.31 |
Otherd | 2.40 | 2.53 | 2.43 | 2.38 |
Total dosee,f | ||||
All alternatives | 0.00371 | 0.00851 | 0.00856 | 0.304 |
Source: Blankenhorn (1994); Hamby (1994); Hess (1994g, j); Simpkins (1994a); and Chesney (1995).
a. Routine operations are not expected to produce aqueous releases.
b. MEI = maximally exposed individual.
c. For atmospheric releases, the dose to the populationwithin 80 kilometers (50 miles) of SRS.
d. Refer to Table E.4-34 for a listing of the radionuclides included in "Other."
e. Dose refers to committed effective dose equivalent (see glossary).
f. Total doses are for the 30-year period of interest.
Table E.4-34. Radionuclides listed under "Other" in Tables E.4-9 through E.4-33.
Silver-110 | Curium-246 | Promethium-147 | Strontium-89 |
Silver-110m | Curium-248 | Promethium-148 | Strontium-90 |
Aluminum-26 | Chromium-51 | Promethium-148m | Tantalum-182 |
Americium-241 | Europium-154 | Praseodymium-143 | Terbium-160 |
Americium-243 | Europium-155 | Praseodymium-144 | Technetium-99 |
Barium-137m | Europium-156 | Plutonium-238 | Tellurium-125m |
Barium-140 | Iron-55 | Plutonium-239 | Tellurium-127 |
Carbon-14 | Iron-59 | Plutonium-240 | Tellurium-127m |
Cadmium-113 | Tritium | Plutonium-241 | Tellurium-129 |
Cerium-141 | Hafnium-181 | Plutonium-242 | Tellurium-129m |
Cerium-144 | Iodine-129 | Rhodium-106 | Uranium-233 |
Cobalt-58 | Indium-113m | Ruthenium-103 | Uranium-234 |
Cobalt-60 | Indium-114 | Ruthenium-103m | Uranium-235 |
Cesium-134 | Krypton-85 | Ruthenium-106 | Uranium-236 |
Cesium-135 | Lanthanum-140 | Antimony-125 | Uranium-238 |
Cesium-137 | Manganese-54 | Scandium-46 | Yttrium-90 |
Californium-249 | Nickel-59 | Selenium-79 | Yttrium 91 |
Californium-251 | Nickel-63 | Samarium-151 | Zinc-65 |
Californium-252 | Niobium-94 | Tin-113 | Zirconium-93 |
Californium-242 | Niobium-95 | Tin-119m | Zirconium-95 |
Californium-243 | Niobium-95m | Tin-121m | Other Alpha |
Californium-244 | Neptunium-237 | Tin-123 | Other B/Gb |
Californium-245 | Palladium-107 | Tin-126 |
Source: Blankenhorn (1994), Hunt (1994), and Chesney (1995).
a. Each of the listed radionuclides contribute less than or equal to 1.0 percent of the total dose unless identified as a major contributor to total dose.
b. B/G = Unidentifiable beta/gamma emitting radionuclides.
SECTION 5
Figure 4-6 is a map of the area around SRS out to
a distance of 80 kilometers (50 miles). This map identifies annular
sectors around SRS by a letter-number combination. Table E.5-1
uses these annular sector identifiers to show:
- The fraction of total
population dose in each annular sector.
- The fraction of total
population dose that the average person in each
annular sector will receive (the per capita dose in each sector).
The total population dose for any
of the alternatives and forecasts can be multiplied by the appropriate
fraction associated with any annular sector to obtain the total
population dose to the annular sector, or the per capita dose
in that sector for any of the forecasts.
Tables E.5-2 through E.5-11 show the estimated per
capita 30-year dose for identified types of communities within
the 80 kilometer region for each of the alternatives and forecasts.
Table E.5-1. Annular sector factors for local dose evaluations.
(5-10 mi)b | (10-20 mi) | (20-30 mi) | (30-40 mi) | (40-50 mi) | (5-10 mi) | (10-20 mi) | (20-30 mi) | (30-40 mi) | (40-50 mi) | ||
Sectorc | |||||||||||
A (N) | 3.09E-04 | 2.79E-02 | 2.70E-02 | 8.63E-03 | 1.49E-02 | 1.19E-05 | 5.25E-06 | 2.69E-06 | 1.70E-06 | 1.22E-06 | |
B (NNE) | 5.86E-05 | 5.75E-03 | 4.71E-03 | 6.5-E-03 | 1.51E-02 | 9.77E-06 | 4.35E-06 | 2.28E-06 | 1.46E-06 | 1.05E-06 | |
C (NE) | 1.02E-05 | 1.35E-02 | 7.03E-03 | 8.33E-03 | 1.17E-02 | 1.02E-05 | 4.57E-06 | 2.40E-06 | 1.58E-06 | 1.15E-06 | |
D (ENE) | 2.76E-04 | 1.29E-02 | 9.56E-03 | 7.43E-03 | 4.15E-02 | 1.02E-05 | 4.12E-06 | 2.13E-06 | 1.39E-06 | 1.02E-06 | |
E (E) | 1.28E-03 | 2.21E-02 | 8.91E-03 | 9.67E-03 | 3.48E-03 | 8.27E-06 | 3.27E-06 | 1.68E-06 | 1.10E-06 | 8.02E-07 | |
F (ESE) | 2.55E-04 | 4.37E-03 | 2.79E-03 | 2.56E-03 | 2.24E-03 | 7.07E-06 | 2.81E-06 | 1.45E-06 | 9.44E-07 | 6.90E-07 | |
G (SE) | 1.29E-04 | 1.11E-03 | 6.78E-03 | 4.54E-03 | 4.25E-03 | 4.96E-06 | 2.02E-06 | 1.04E-06 | 6.79E-07 | 4.95E-07 | |
H (SSE) | 1.61E-04 | 6.63E-04 | 6.92E-04 | 8.10E-04 | 1.12E-03 | 4.04E-06 | 1.70E-06 | 9.00E-07 | 5.97E-07 | 4.40E-07 | |
I (S) | 2.25E-06 | 5.48E-04 | 7.24E-04 | 2.69E-03 | 9.34E-04 | 2.25E-06 | 9.83E-07 | 5.44E-07 | 3.71E-07 | 2.80E-07 | |
J (SSW) | 1.29E-05 | 2.42E-03 | 2.90E-03 | 4.11E-03 | 2.12E-03 | 6.46E-06 | 2.70E-06 | 1.45E-06 | 9.82E-07 | 7.22E-07 | |
K (SW) | 1.87E-04 | 4.17E-03 | 5.22E-03 | 4.06E-03 | 3.02E-03 | 1.10E-06 | 4.41E-06 | 2.33E-06 | 1.56E-06 | 1.14E-06 | |
L (WSW) | 5.18E-04 | 3.87E-03 | 1.32E-02 | 2.84E-03 | 5.31E-03 | 8.64E-06 | 3.50E-06 | 1.86E-06 | 1.24E-06 | 9.13E-07 | |
M (W) | 3.43E-04 | 8.52E-03 | 1.11E-02 | 7.51E-03 | 4.62E-03 | 6.24E-06 | 2.57E-06 | 1.40E-06 | 9.40E-07 | 6.82E-07 | |
N (WNW) | 2.89E-03 | 9.16E-03 | 1.57E-01 | 4.99E-02 | 8.33E-03 | 6.43E-06 | 2.74E-06 | 1.47E-06 | 9.92E-07 | 7.22E-07 | |
O (NW) | 2.23E-03 | 2.08E-02 | 1.57E-01 | 3.04E-02 | 2.48E-03 | 8.22E-06 | 3.52E-06 | 1.79E-06 | 1.14E-06 | 8.21E-07 | |
P (NNW) | 3.97E-03 | 8.47E-02 | 6.28E-02 | 9.74E-03 | 6.34E-03 | 1.09E-05 | 4.70E-06 | 2.31E-06 | 1.46E-06 | 1.04E-06 |
a. Source: Simpkins (1994b).
b. No population resides within 8 kilometers (5 miles) of the center of SRS.
c. Sector letter is letter shown on Figure 4-6. Letters in parentheses after the sector letter indicate the compass direction of the sector.
| ||||||
0-16 km (0-10 miles) | 9.37E-08 | 8.49E-08 | 9.97E-08 | 8.67E-08 | 9.02E-08 | 9.55E-08 |
0-32 km
(0-20 miles) | 4.50E-08 | 3.54E-08 | 6.20E-08 | 4.10E-08 | 4.27E-08 | 4.57E-08 |
0-48 km
(0-30 miles) | 2.42E-08 | 1.89E-08 | 2.95E-08 | 2.49E-08 | 2.57E-08 | 2.37E-08 |
0-64 km
(0-40 miles) | 1.97E-08 | 1.73E-08 | 2.28E-08 | 1.94E-08 | 2.11E-08 | 1.93E-08 |
0-80 km
(0-50 miles) | 1.84E-08 | 1.59E-08 | 2.03E-08 | 1.88E-08 | 1.93E-08 | 1.82E-08 |
Total population populationdose = 0.0086 person-rem. |
|
| |||||
0-16 km (0-10 miles) | 1.85E-04 | 1.68E-04 | 1.97E-04 | 1.71E-04 | 1.78E-04 | 1.89E-04 |
0-32 km
(0-20 miles) | 8.89E-05 | 7.00E-05 | 1.22E-04 | 8.11E-05 | 8.45E-05 | 9.04E-05 |
0-48 km
(0-30 miles) | 4.78E-05 | 3.74E-05 | 5.84E-05 | 4.92E-05 | 5.09E-05 | 4.69E-05 |
0-64 km
(0-40 miles) | 3.89E-05 | 3.43E-05 | 4.51E-05 | 3.83E-05 | 4.17E-05 | 3.82E-05 |
0-80 km
(0-50 miles) | 3.64E-05 | 3.15E-05 | 4.01E-05 | 3.71E-05 | 3.81E-05 | 3.60E-05 |
Total population populationdose = 17 person-rem. |
| ||||||
0-16 km (0-10 miles) | 8.93E-05 | 8.10E-05 | 9.51E-05 | 8.26E-05 | 8.60E-05 | 9.10E-05 |
0-32 km
(0-20 miles) | 4.29E-05 | 3.37E-05 | 5.91E-05 | 3.91E-05 | 4.07E-05 | 4.36E-05 |
0-48 km
(0-30 miles) | 2.30E-05 | 1.81E-05 | 2.82E-05 | 2.37E-05 | 2.45E-05 | 2.26E-05 |
0-64 km
(0-40 miles) | 1.88E-05 | 1.65E-05 | 2.17E-05 | 1.85E-05 | 2.01E-05 | 1.84E-05 |
0-80 km
(0-50 miles) | 1.76E-05 | 1.52E-05 | 1.94E-05 | 1.79E-05 | 1.84E-05 | 1.73E-05 |
Total population populationdose = 8.2 person-rem. |
| ||||||
0-16 km (0-10 miles) | 1.12E-03 | 1.02E-03 | 1.19E-03 | 1.04E-03 | 1.08E-03 | 1.14E-03 |
0-32 km
(0-20 miles) | 5.39E-04 | 4.24E-04 | 7.42E-04 | 4.91E-04 | 5.12E-04 | 5.48E-04 |
0-48 km
(0-30 miles) | 2.89E-04 | 2.27E-04 | 3.54E-04 | 2.98E-04 | 3.08E-04 | 2.84E-04 |
0-64 km
(0-40 miles) | 2.36E-04 | 2.08E-04 | 2.73E-04 | 2.32E-04 | 2.53E-04 | 2.32E-04 |
0-80 km
(0-50 miles) | 2.21E-04 | 1.91E-04 | 2.43E-04 | 2.25E-04 | 2.31E-04 | 2.18E-04 |
Total population populationdose = 103 person-rem. |
| ||||||
0-16 km (0-10 miles) | 3.29E-03 | 2.98E-03 | 3.50E-03 | 3.04E-03 | 3.17E-03 | 3.35E-03 |
0-32 km
(0-20 miles) | 1.58E-03 | 1.24E-03 | 2.18E-03 | 1.44E-03 | 1.50E-03 | 1.61E-03 |
0-48 km
(0-30 miles) | 8.49E-04 | 6.65E-04 | 1.04E-03 | 8.73E-04 | 9.04E-04 | 8.33E-04 |
0-64 km
(0-40 miles) | 6.92E-04 | 6.09E-04 | 8.01E-04 | 6.81E-04 | 7.41E-04 | 6.79E-04 |
0-80 km
(0-50 miles) | 6.47E-04 | 5.59E-04 | 7.13E-04 | 6.59E-04 | 6.76E-04 | 6.39E-04 |
Total population populationdose = 302 person-rem. |
| ||||||
0-16 km (0-10 miles) | 1.61E-03 | 1.46E-03 | 1.72E-03 | 1.49E-03 | 1.55E-03 | 1.64E-03 |
0-32 km
(0-20 miles) | 7.74E-04 | 6.09E-04 | 1.07E-03 | 7.06E-04 | 7.35E-04 | 7.87E-04 |
0-48 km
(0-30 miles) | 4.16E-04 | 3.26E-04 | 5.08E-04 | 4.28E-04 | 4.43E-04 | 4.08E-04 |
0-64 km
(0-40 miles) | 3.39E-04 | 2.99E-04 | 3.92E-04 | 3.34E-04 | 3.63E-04 | 3.33E-04 |
0-80 km
(0-50 miles) | 3.17E-04 | 2.74E-04 | 3.50E-04 | 3.23E-04 | 3.31E-04 | 3.13E-04 |
Total population populationdose = 148 person-rem. |
| ||||||
0-16 km (0-10 miles) | 7.49E-02 | 6.79E-02 | 7.98E-02 | 6.93E-02 | 7.22E-02 | 7.64E-02 |
0-32 km
(0-20 miles) | 3.60E-02 | 2.83E-02 | 4.96E-02 | 3.28E-02 | 3.42E-02 | 3.66E-02 |
0-48 km
(0-30 miles) | 1.93E-02 | 1.52E-02 | 2.36E-02 | 1.99E-02 | 2.06E-02 | 1.90E-02 |
0-64 km
(0-40 miles) | 1.58E-02 | 1.39E-02 | 1.82E-02 | 1.55E-02 | 1.69E-02 | 1.55E-02 |
0-80 km
(0-50 miles) | 1.47E-02 | 1.27E-02 | 1.62E-02 | 1.50E-02 | 1.54E-02 | 1.46E-02 |
Total population populationdose = 6,880 person-rem. |
| ||||||
0-16 km (0-10 miles) | 5.01E-04 | 4.54E-04 | 5.33E-04 | 4.64E-04 | 4.83E-04 | 5.11E-04 |
0-32 km
(0-20 miles) | 2.41E-04 | 1.89E-04 | 3.31E-04 | 2.19E-04 | 2.29E-04 | 2.45E-04 |
0-48 km
(0-30 miles) | 1.29E-04 | 1.01E-04 | 1.58E-04 | 1.33E-04 | 1.38E-04 | 1.27E-04 |
0-64 km
(0-40 miles) | 1.05E-04 | 9.28E-05 | 1.22E-04 | 1.04E-04 | 1.13E-04 | 1.03E-04 |
0-80 km
(0-50 miles) | 9.85E-05 | 8.52E-05 | 1.09E-04 | 1.00E-04 | 1.03E-04 | 9.73E-05 |
Total population populationdose = 46 person-rem. |
| ||||||
0-16 km (0-10 miles) | 3.27E-04 | 2.96E-04 | 3.48E-04 | 3.02E-04 | 3.15E-04 | 3.33E-04 |
0-32 km
(0-20 miles) | 1.57E-04 | 1.23E-04 | 2.16E-04 | 1.43E-04 | 1.49E-04 | 1.60E-04 |
0-48 km
(0-30 miles) | 8.43E-05 | 6.61E-05 | 1.03E-04 | 8.68E-05 | 8.98E-05 | 8.28E-05 |
0-64 km
(0-40 miles) | 6.87E-05 | 6.05E-05 | 7.95E-05 | 6.77E-05 | 7.36E-05 | 6.74E-05 |
0-80 km
(0-50 miles) | 6.43E-05 | 5.56E-05 | 7.09E-05 | 6.55E-05 | 6.72E-05 | 6.35E-05 |
Total population populationdose = 30 person-rem. |
| ||||||
0-16 km (0-10 miles) | 4.43E-03 | 4.02E-03 | 4.72E-03 | 4.10E-03 | 4.27E-03 | 4.52E-03 |
0-32 km
(0-20 miles) | 2.13E-03 | 1.67E-03 | 2.93E-03 | 1.94E-03 | 2.02E-03 | 2.16E-03 |
0-48 km
(0-30 miles) | 1.14E-03 | 8.97E-04 | 1.40E-03 | 1.18E-03 | 1.22E-03 | 1.12E-03 |
0-64 km
(0-40 miles) | 9.32E-04 | 8.21E-04 | 1.08E-03 | 9.18E-04 | 9.99E-04 | 9.15E-04 |
0-80 km
(0-50 miles) | 8.72E-04 | 7.54E-04 | 9.61E-04 | 8.89E-04 | 9.12E-04 | 8.61E-04 |
Total population populationdose = 407 person-rem. |
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