PUBLIC HEALTH ASSESSMENT
COMMENCEMENT BAY, SOUTH TACOMA FIELD
(a/k/a COMMENCEMENT BAY, SOUTH TACOMA CHANNEL)
TACOMA, PIERCE COUNTY, WASHINGTON
A. Maps for South Tacoma Field Site
B. Contaminants of Concern Tables
D. Response to Public Comments
APPENDIX - A
Maps for South Tacoma Field Site

Figure 1. Site Location Map for South Tacoma Field Superfund Site

Figure 2. Sampling Unit Designations and Businesses Map

Figure 3. Upgradient and On-Site Monitoring Well Locations Map
APPENDIX - B
Contaminants of Concern Tables
| CONTAMINANT | SWAMP | AIRPORT | DISMANTLING YARD | RAILYARD | TIP | AMSTED | COMPARISON VALUE | |
|---|---|---|---|---|---|---|---|---|
| Range of Detection (mg/kg) | mg/kg | Source | ||||||
| Inorganic Compounds | ||||||||
| Aluminum | 1,560 -24,000 | 8,770 - 26,600 | 1,350 -104,000 | 3,550 - 28,400 | 8,260 - 62,300 | 8,910 -27,500 | None | None |
| Antimony | 2.1 - 23.2 | 4.7 - 24.4 | 2.1 - 46.6 | 2.1 - 491 | 2.1 - 58 | 2.5 - 1,150 | 20 | RMEG |
| Arsenic | 0.70 - 54.4 | 2.9 - 50.1 | 2.5 - 696 | 1.8 - 395 | 0.24 - 52.32 | 6.1 - 389 | 20 | EMEG |
| Barium | 33.5 - 974 | 46.1 - 565 | 10.8 - 2,600 | 9.9 - 2,290 | 55.1 - 850 | 52.3 - 675 | 4,000 | RMEG |
| Beryllium | 0.11 - 1 | 0.10 - 0.98 | 0.09 - 14.4 | 0.1 - 2.7 | 0.11 - 2.9 | 0.13 - 2.2 | 0.2 | CREG |
| Boron | 0.75 - 44 | 2.0 - 26.2 | 0.85 - 1,300 | 0.85 - 229 | 2.0 - 5.5 | 0.85 - 2.4 | 500 | EMEG* |
| Cadmium | 0.11 - 12.1 | 0.21 - 4.0 | 0.21 - 29.9 | 0.11 - 22.6 | 0.21 - 2.0 | 0.12 - 13.4 | 40 | EMEG |
| Chromium (Total) | 14.3 - 501 | 10.2 - 94.1 | 2.9 - 707 | 2.9 - 282 | 12.7 - 107 | 21.0 - 130 | 300 | RMEG+ |
| Cobalt | 1.4 - 21.1 | 5.2 - 17.7 | 2.4 - 135 | 0.7 - 37.4 | 7.0 - 19.0 | 5.5 - 20.7 | None | None |
| Copper | 7.2 - 287 | 11.2 - 418 | 7.2 - 11,200 | 11.7 - 13,000 | 14.7 - 334 | 42.2 -163,000 | None | None |
| Lead | 4.7 - 1,510 | 6.8 - 1,160 | 18.1 - 24,000 | 11.2 - 27,100 | 6.6 - 1,820 | 16.4 -118,000 | None | None |
| Manganese | 74.6 - 6,090 | 180 - 763 | 42.2 - 5,850 | 22.7 - 2,270 | 293 - 27,000 | 202 - 21,800 | 300 | RMEG |
| Nickel | 6 - 472 | 16.5 - 70.9 | 2.8 - 173 | 7.6 - 121 | 13.3 - 41.5 | 20.8 - 865 | None | None |
| Thallium | 0.11 - 3.0 | 0.1 - 0.32 | 0.06 - 6.7 | 0.10 - 1.2 | 0.11 - 0.25 | 0.12 - 5.9 | None | None |
| Vanadium | 2.5 - 321 | 25.6 - 154 | 0.34 - 170 | 13.5 - 170 | 28.8 - 106 | 19.4 - 105 | 200 | EMEG* |
| Zinc | 13.4 - 781 | 30.2 - 972 | 35.3 - 24,200 | 25.8 - 7,530 | 43.6 - 242 | 49.5 - 61,600 | 20,000 | RMEG |
| Volatile Organic Compounds | ||||||||
| Benzene | ND | ND | 0.008 - 0.012 | ND | ND | ND | 20 | CREG |
| Bromodichloromethane | ND | ND | ND | ND | ND | ND | 10 | CREG |
| Chloroform | ND | ND | 0.012 - 0.036 | ND | ND | ND | 100 | CREG |
| 1,2-Dichloroethane | ND | ND | ND | ND | ND | ND | 8 | CREG |
| Ethylbenzene | ND | ND | ND | ND | ND | ND | 5,000 | RMEG |
| Methylene Chloride | 0.031 - 0.480 | 0.110 - 0.930 | 0.150 - 0.90 | 0.073 - 1.40 | 0.310 | 0.140 - 0.160 | 90 | CREG |
| Tetrachloroethylene | ND | ND | 0.005 | 0.003 | ND | ND | 10 | CREG |
| 1,1,2-Trichloroethane | ND | ND | ND | ND | ND | ND | 10 | CREG |
| Trichloroethylene | ND | ND | 0.009 | ND | ND | ND | 60 | CREG |
| Vinyl Chloride | ND | ND | ND | ND | ND | ND | 1 | EMEG |
| Semi-Volatile Organic Compounds | ||||||||
| Bis(2-ethylhexyl)phthalate | 0.120 - 0.58 | 0.044 - 0.430 | 0.048 - 1.3 | 0.05 - 4.2 | 0.032 | ND | 50 | CREG |
| 3,3-Dichlorobenzidine | ND | ND | ND | 0.043 - 9.7 | ND | ND | 2 | CREG |
| Pentachlorophenol | ND | ND | ND | 0.078 - 0.096 | ND | ND | 6 | CREG |
| Poylnuclear Aromatic Hydrocarbon Compounds | ||||||||
| Benzo(a)anthracene | 0.01 - 4.1 | 0.019 - 2.6 | 0.01 - 9.4 | 0.02 - 4.3 | 0.044 - 1.5 | 0.01 - 1.7 | None | None |
| Benzo(a)pyrene | 0.009 - 8.9 | 0.032 - 0.01 | 0.01 - 6.3 | 0.02 - 3.8 | 0.032 - 2.2 | 0.01 - 2.1 | 0.1 | CREG |
| Benzo(b)fluoranthene | 0.01 - 6 | 0.02 - 3.1 | 0.01 - 6.5 | 0.014 - 6.8 | 0.061 - 2.9 | 0.01 - 2.2 | None | None |
| Benzo(g,h,i)perylene | 0.022 - 7.6 | 0.016 - 1.8 | 0.014 - 7.4 | 0.02 - 3.2 | 1.8 - 1.9 | 0.02 - 1.5 | None | None |
| Benzo(k)fluoranthene | 0.007 - 3.9 | 0.015 - 1.5 | 0.01 - 3.4 | 0.013 - 3.6 | 0.022 - 1.1 | 0.01 - 1.2 | None | None |
| Chrysene | 0.01 - 4.6 | 0.013 - 2.6 | 0.011 - 9.9 | 0.014 - 4.1 | 0.065 - 1.9 | 0.01 - 2.2 | None | None |
| Dibenzo(a,h)anthracene | 0.086 | 1 | 0.02 - 0.87 | 0.02 - 0.16 | ND | 0.01 - 0.25 | None | None |
| Indeno(1,2,3-cd)pyrene | 0.01 - 6.7 | 0.012 - 2 | 0.01 - 5.8 | 0.01 - 2.9 | 0.038 - 1.7 | 0.01 - 1.3 | None | None |
| Naphthalene | 0.13 - 0.21 | 0.44 | 0.01 - 2.9 | 0.11 - 4.8 | ND | ND | None | None |
| Phenanthrene | 0.12 - 1.7 | 0.012 - 2.1 | 0.01 - 15 | 0.012 - 6.1 | 0.048 - 1 | 0.02 - 4.5 | None | None |
| Total PAHs | 0.28 - 46.7 | 0.28 - 25.0 | 0.28 - 105.3 | 0.018 - 70.4 | 0.28 - 37.0 | 0.38 - 30.3 | 0.1 | CREG |
| Total Probable Carcinogenic PAHs | 0.04 - 34.2 | 0.04 - 12.6 | 0 - 38.5 | 0.04 - 24.5 | 0.04 - 10.6 | 0.06 - 10.2 | 0.1 | CREG |
| Pesticides | ||||||||
| Aldrin | ND | ND | ND | 0.012 | ND | ND | 0.04 | CREG |
| Polychlorinated Biphenyl Compounds | ||||||||
| Aroclor 1242 | ND | ND | ND | ND | ND | ND | 0.09 | CREG |
| Aroclor 1248 | ND | ND | ND | ND | ND | ND | 0.09 | CREG |
| Aroclor 1254 | ND | ND | 0.2 - 9.0 | 0.17 - 56 | ND | ND | 0.09 | CREG |
| Aroclor 1260 | ND | ND | 0.35 - 0.44 | 1.0 | ND | ND | 0.09 | CREG |
- Child EMEG and RMEG values used.
* Intermediate EMEG
+ RMEG for Chromium VI
ND Not Detected at laboratory detection levels.
References - 25, 26
| CONTAMINANT | PIONEER BUILDERS | TACOMA PUBLIC UTILITIES | COMPARISON VALUE | |
|---|---|---|---|---|
| Maximum Detection (mg/kg) | mg/kg | Source | ||
| Inorganic Compounds | ||||
| Aluminum | 10,300 | 20,800 | None | None |
| Antimony | ND | 15.6 | 20 | RMEG |
| Arsenic | 1.8 | 133 | 20 | EMEG |
| Barium | 57.7 | 125 | 4,000 | RMEG |
| Beryllium | 0.52 | 0.42 | 0.2 | CREG |
| Boron | ND | ND | 500 | EMEG* |
| Cadium | ND | 2.4 | 40 | EMEG |
| Chromium (Total) | 19.3 | 2,300 | 300 | RMEG+ |
| Cobalt | 8.0 | 10.2 | None | None |
| Copper | 16.4 | 856 | None | None |
| Lead | 1.2 | 838 | None | None |
| Manganese | 275 | 836 | 300 | RMEG |
| Nickel | 25.5 | 48.8 | None | None |
| Thallium | ND | 1.24 | None | None |
| Vanadium | 29.8 | 44.5 | 200 | EMEG* |
| Zinc | 28.0 | 542 | 20,000 | RMEG |
| Volatile Organic Compounds | ||||
| Benzene | ND | 0.95 | 20 | CREG |
| Bromodichloromethane | ND | ND | 10 | CREG |
| Chloroform | ND | ND | 100 | CREG |
| 1,2-Dichloroethane | ND | ND | 8 | CREG |
| Ethylbenzene | 0.055 | ND | 5,000 | RMEG |
| Methylene Chloride | 1.0 | 0.11 | 90 | CREG |
| Tetrachloroethylene | ND | 0.017 | 10 | CREG |
| 1,1,2-Trichloroethane | ND | ND | 10 | CREG |
| Trichloroethylene | ND | 0.31 | 60 | CREG |
| Vinyl Chloride | ND | ND | 1 | EMEG |
| Semi-Volatile Organic Compounds | ||||
| Bis(2-ethylhexyl)phthalate | 0.89 | 3.7 | 50 | CREG |
| 3,3-Dichlorobenzidine | ND | 22.0 | 2 | CREG |
| Pentachlorophenol | ND | 150.0 | 6 | CREG |
| Polynuclear Aromatic Hydrocarbon Compounds | ||||
| Benzo(a)anthracene | 0.056 | 30.0 | None | None |
| Benzo(a)pyrene | 0.031 | 16.0 | 0.1 | CREG |
| Benzo(b)fluoranthene | 0.085 | 22.0 | None | None |
| Benzo(g,h,i)perylene | 0.043 | 8.0 | None | None |
| Benzo(k)fluoranthene | 0.043 | 14.0 | None | None |
| Chrysene | 0.2 | 51.0 | None | None |
| Dibenzo(a,h)anthracene | ND | 1.7 | None | None |
| Indeno(1,2,3-cd)pyrene | 0.058 | 6.2 | None | None |
| Phenanthrene | 0.076 | 150.0 | None | None |
| Pesticides | ||||
| Aldrin | ND | 2.0 | 0.04 | CREG |
| Polychlorinated Biphenyl Compounds | ||||
| Aroclor 1242 | ND | 71.0 | 0.09 | CREG |
| Aroclor 1248 | ND | 0.51 | 0.09 | CREG |
| Aroclor 1254 | ND | 0.27 | 0.09 | CREG |
| Aroclor 1260 | ND | 840.0 | 0.09 | CREG |
- Child EMEG and RMEG values used.
* Intermediate EMEG
+ RMEG for Chromium VI
NA Not Analyzed for.
ND Not Detected at laboratory detection levels.
References - 25, 26
| CONTAMINANT | SWAMP | AIRPORT | DISMANTLING YARD | RAILYARD | TIP | AMSTED | COMPARISON VALUE | |
|---|---|---|---|---|---|---|---|---|
| Maximum Detection (mg/kg) | mg/kg | Source | ||||||
| Inorganic Compounds | ||||||||
| Aluminum | 18,000 | 17,600 | 24,100 | 32,400 | 27,100 | 178,000 | None | None |
| Antimony | ND | 13 | 276 | 762 | 90 | 877 | 20 | RMEG |
| Arsenic | 67.6 | 19.6 | 57.7 | 360 | 126 | 95.6 | 20 | EMEG |
| Barium | NA | NA | NA | NA | NA | NA | 4,000 | RMEG |
| Beryllium | ND | 0.58 | 0.68 | 2.4 | 1.7 | 9.4 | 0.2 | CREG |
| Boron | NA | NA | NA | NA | NA | NA | 500 | EMEG* |
| Cadmium | ND | 0.80 | 11.7 | 4.0 | 1.5 | 10.3 | 40 | EMEG |
| Chromium (Total) | 523 | 89 | 80.4 | 143 | 153 | 896 | 300 | RMEG+ |
| Cobalt | 37.4 | 19.1 | 20.1 | 19.3 | 53.3 | 290 | None | None |
| Copper | 428 | 383 | 881 | 27,300 | 455 | 24,400 | None | None |
| Lead | 1,110 | 1,970 | 9,890 | 17,000 | 2,360 | 31,200 | None | None |
| Manganese | 2,880 | 522 | 1,520 | 1,760 | 15,600 | 13,800 | 300 | RMEG |
| Nickel | 472 | 437 | 173 | 114 | 75.9 | 582 | None | None |
| Thallium | NA | NA | NA | NA | NA | NA | None | None |
| Vanadium | 134 | 51.2 | 59.8 | 189 | 109 | 529 | 200 | EMEG* |
| Zinc | 1,580 | 1,730 | 9,760 | 958 | 517 | 13,200 | 20,000 | RMEG |
| Volatile Organic Compounds | ||||||||
| Benzene | 5.0 | ND | ND | 3.0 | ND | 21.0 | 20 | CREG |
| Bromodichloromethane | ND | ND | ND | ND | ND | ND | 10 | CREG |
| Chloroform | ND | ND | ND | ND | ND | ND | 100 | CREG |
| 1,2-Dichloroethane | ND | ND | ND | ND | ND | ND | 8 | CREG |
| Ethylbenzene | 9.0 | ND | ND | ND | ND | 0.01 | 5,000 | RMEG |
| Methylene Chloride | 48.0 | 54.0 | ND | 48.0 | 13.0 | ND | 90 | CREG |
| Tetrachloroethylene | 14.0 | ND | 81.0 | ND | ND | ND | 10 | CREG |
| 1,1,2-Trichloroethane | ND | ND | ND | ND | ND | ND | 10 | CREG |
| Trichloroethylene | ND | ND | ND | ND | ND | ND | 10 | CREG |
| Vinyl Chloride | ND | ND | ND | ND | ND | ND | 1 | EMEG |
| Semi-Volatiles Organic Compounds | ||||||||
| Bis(2-ethylhexyl)phthalate | 1.8 | 0.16 | 2.0 | 2.2 | 0.36 | 9.6 | 50 | CREG |
| 3,3-Dichlorobenzidine | ND | ND | ND | 0.33 | ND | ND | 2 | CREG |
| Pentachlorophenol | ND | ND | ND | ND | ND | ND | 6 | CREG |
| Polynuclear Aromatic Hydrocarbon Compounds | ||||||||
| Total Probable CarcinogenicPAHs | 18.0 | 17.1 | 8.3 | 8.03 | 0.535 | 3.7 | 0.1 | CREG |
| Pesticides | ||||||||
| Aldrin | ND | ND | ND | 0.037 | ND | ND | 0.04 | CREG |
| Polychlorinated Biphenyl Compounds | ||||||||
| PCBs | ND | ND | 0.44 | 40.0 | ND | ND | 0.09 | CREG |
- Child EMEG and RMEG values used.
* Intermediate EMEG
+ RMEG for Chromium VI
NA Not Analyzed for.
ND Not Detected at laboratory detection levels.
References - 25, 26
| CONTAMINANT | Range of Detection (µg/L) | COMPARISON VALUE | |
|---|---|---|---|
| µg/L | Source | ||
| Inorganic Compounds | |||
| Aluminum | 16.0 - 5,940 | None | None |
| Antimony | 11.0 - 50.7 | 4 | RMEG |
| Arsenic | 1.0 - 50.9 | 0.02 | CREG |
| Barium | 2.2 - 56.5 | 700 | RMEG |
| Beryllium | 1.0 - 2.6 | 0.008 | CREG |
| Boron | 20.2 - 1,940 | 100 | EMEG* |
| Cadmium | <1.0 - <3.0 | 7 | EMEG |
| Chromium (Total) | 3.3 - 21.5 | 50 | RMEG+ |
| Cobalt | 3.2 - 218 | None | None |
| Copper | 1.0 - 21.0 | None | None |
| Lead | 0.7 - 58.9 | None | None |
| Manganese | 1.0 - 5,200 | 50 | RMEG |
| Nickel | 6.7 - 1,950 | 100 | LTHA |
| Thallium | 1.0 - 7.5 | 0.4 | LTHA |
| Vanadium | 3.3 - 30.5 | 30 | EMEG* |
| Zinc | 2.0 - 726 | 3,000 | RMEG |
| Volatile Organic Compounds | |||
| Benzene | 86 - 480 | 1 | CREG |
| Bromodichloromethane | 2.0 | 0.6 | CREG |
| Chloroform | 1.0 - 20 | 6 | CREG |
| 1,2-Dichloroethane | 5.0 - 7.0 | 0.4 | CREG |
| Ethylbenzene | 150 - 1,000 | 1,000 | EMEG |
| Methylene Chloride | 3.0 - 6.0 | 5 | CREG |
| Tetrachloroethylene | 3.0 - 4.0 | 0.7 | CREG |
| 1,1,2-Trichloroethane | 51.0 | 0.6 | CREG |
| Trichloroethylene | 1.0 - 6.0 | 3 | CREG |
| Vinyl Chloride | 2.0 | 0.2 | EMEG |
| Semi-Volatile Organic Compounds | |||
| Bis(2-ethylhexyl)phthalate | 0.7 - 7.0 | 3 | CREG |
| 3,3-Dichlorobenzidine | ND | 0.08 | CREG |
| Pentachlorophenol | ND | 0.3 | CREG |
| Polynuclear Aromatic Hydrocarbons Compounds | |||
| Benzo(a)anthracene | ND | None | None |
| Benzo(a)pyrene | ND | 0.005 | CREG |
| Benzo(b)fluoranthene | ND | None | None |
| Benzo(g,h,i)perylene | ND | None | None |
| Benzo(k)fluoranthene | ND | None | None |
| Chrysene | ND | None | None |
| Dibenzo(a,h)anthracene | ND | None | None |
| Indeno(1,2,3-cd)pyrene | ND | None | None |
| Naphthalene | 2.3 - 190 | 20 | LTHA |
| Phenanthrene | 0.14 - 1.1 | None | |
| Pesticides | |||
| Aldrin | ND | 0.002 | CREG |
| Poylchlorinated Biphenyl Compounds | |||
| PCBs | ND | 0.005 | CREG |
- Child EMEG and RMEG values used.
* Intermediate EMEG
+ RMEG for Chromium VI
LTHA Life Time Health Advisory
ND Not Detected at laboratory detection levels.
References - 25, 26
| CONTAMINANT | RUNON | ON-SITE | RUNOFF | COMPARISON VALUE | |
|---|---|---|---|---|---|
| Maximum Concentration (µg/L) | µg/L | Source | |||
| Inorganic Compounds | |||||
| Aluminum | 38,500 | 80,900 | 4,040 | None | None |
| Antimony | 15.9 | ND | ND | 4 | RMEG |
| Arsenic | 25.5 | 24.8 | 4.0 | 0.02 | CREG |
| Barium | 252.0 | 773 | 31.2 | 700 | RMEG |
| Beryllium | ND | 1.9 | ND | 0.008 | CREG |
| Boron | 174.4 | 47.4 | 39.8 | 100 | EMEG* |
| Cadmium | 2.4 | 18.3 | ND | 7 | EMEG |
| Chromium (Total) | 50.4 | 193 | 8.0 | 50 | RMEG+ |
| Cobalt | 997.0 | 24.1 | ND | None | None |
| Copper | 52.2 | 2,980 | 9.2 | None | None |
| Lead | 124 | 219 | 9.5 | None | None |
| Manganese | 659 | 865 | 52.6 | 50 | RMEG |
| Nickel | 52.6 | 18.4 | 15.3 | 100 | LTHA |
| Thallium | 19.5 | ND | ND | 0.4 | LTHA |
| Vanadium | 66.9 | 146 | 4.2 | 30 | EMEG* |
| Zinc | 325 | 3,160 | 40.4 | 3,000 | RMEG |
| Volatile Organic Compounds | |||||
| Benzene | NA | ND | ND | 1 | CREG |
| Bromodichloromethane | NA | ND | ND | 0.6 | CREG |
| Chloroform | NA | 5.0 | ND | 6 | CREG |
| 1,2-Dichloroethane | NA | ND | ND | 0.4 | CREG |
| Ethylbenzene | NA | ND | ND | 1,000 | EMEG |
| Methylene Chloride | NA | 8.0 | ND | 5 | CREG |
| Tetrachloroethylene | NA | ND | ND | 0.7 | CREG |
| 1,1,2-Trichloroethane | NA | ND | ND | 0.6 | CREG |
| Trichloroethylene | NA | ND | ND | 3 | CREG |
| Vinyl Chloride | NA | ND | ND | 0.2 | EMEG |
| Semi-Volatile Organic Compounds | |||||
| Bis(2-ethylhexyl)phthalate | ND | 55.0 | 75.0 | 3 | CREG |
| 3,3-Dichlorobenzidine | ND | ND | ND | 0.08 | CREG |
| Pentachlorophenol | ND | 6.0 | 0.7 | 0.3 | CREG |
| Polynuclear Aromatic Hydrocarbon Compounds | |||||
| Benzo(a)anthracene | 0.90 | 1.5 | ND | None | None |
| Benzo(a)pyrene | 1.0 | 3.8 | ND | 0.005 | CREG |
| Benzo(b)fluoranthene | 2.0 | 3.9 | ND | None | None |
| Benzo(g,h,i)perylene | 1.0 | 3.7 | ND | None | None |
| Benzo(k)fluoranthene | 0.9 | 2.1 | ND | None | None |
| Chrysene | 2.2 | 4.4 | ND | None | None |
| Dibenzo(a,h)anthracene | 0.2 | 1.0 | ND | None | None |
| Indeno(1,2,3-cd)pyrene | 1.4 | 2.0 | ND | None | None |
| Naphthalene | 0.35 | ND | ND | 20 | LTHA |
| Phenanthrene | 2.5 | 3.9 | 0.087 | None | None |
| Pesticides | |||||
| Aldrin | ND | ND | ND | 0.002 | CREG |
| Polychlorinated Biphenyl Compounds | |||||
| PCBs | ND | ND | ND | 0.005 | CREG |
- Child EMEG and RMEG values used.
NA Not Analyzed
ND Not Detected at laboratory detection levels.
LTHA Life Time Health Advisory
* Intermediate EMEG
+ RMEG for Chromium VI
References - 25, 26
| CONTAMINANT | Maximum Concentration (mg/kg) | COMPARISON VALUE | |
|---|---|---|---|
| mg/kg | Source | ||
| Inorganic Compounds | |||
| Aluminum | 38,700 | None | None |
| Antimony | 33.9 | 20 | RMEG |
| Arsenic | 93.8 | 20 | EMEG |
| Barium | 2,550 | 4,000 | RMEG |
| Beryllium | 1.1 | 0.2 | CREG |
| Boron | 47.6 | 500 | EMEG* |
| Cadmium | 18 | 40 | EMEG |
| Chromium (Total) | 614 | 300 | RMEG+ |
| Cobalt | 20 | None | None |
| Copper | 979 | None | None |
| Lead | 2,050 | None | None |
| Manganese | 814 | 300 | RMEG |
| Nickel | 408 | None | None |
| Thallium | ND | None | None |
| Vanadium | 93 | 200 | EMEG* |
| Zinc | 2,460 | 20,000 | RMEG |
| Volatile Organic Compounds | |||
| Benzene | 0.024 | 20 | CREG |
| Bromodichloromethane | ND | 10 | CREG |
| Chloroform | 0.14 | 500 | EMEG |
| 1,2-Dichloroethane | ND | 8 | CREG |
| Ethylbenzene | 0.17 | 5,000 | RMEG |
| Methylene Chloride | 2.0 | None | None |
| 1,1,2-Trichloroethane | ND | 10 | CREG |
| Trichloroethylene | ND | 60 | CREG |
| Tetrachloroethylene | ND | 10 | CREG |
| Vinyl Chloride | ND | 1.0 | EMEG |
| Semi-Volatile Organic Compounds | |||
| Bis(2-ethylhexyl)phthalate | 160 | 50 | CREG |
| 3,3-Dichlorobenzidine | ND | 2 | CREG |
| Pentachlorophenol | ND | 6 | CREG |
| Polynuclear Aromatic Hydrocarbon Compounds | |||
| Benzo(a)anthracene | 32 | None | None |
| Benzo(a)pyrene | 35 | 0.1 | CREG |
| Benzo(b)fluoranthene | 36 | None | None |
| Benzo(g,h,i)perylene | 29 | None | None |
| Benzo(k)fluoranthene | 22 | None | None |
| Chrysene | 44 | None | None |
| Dibenzo(a,h)anthracene | 5.5 | None | None |
| Indeno(1,2,3-cd)pyrene | 29 | None | None |
| Naphthalene | ND | None | None |
| Phenanthrene | 64 | None | None |
| Total PAHs | 560 | None | None |
| Total Probable Carcinogenic PAHs | 200 | 0.1 | CREG |
| Pesticides | |||
| Aldrin | ND | 0.04 | CREG |
| Polychlorinated Biphenyl Compounds | |||
| Aroclor 1242 | ND | 0.09 | CREG |
| Aroclor 1248 | ND | 0.09 | CREG |
| Aroclor 1254 | 1.8 | 0.09 | CREG |
| Aroclor 1260 | 4 | 0.09 | CREG |
- Child EMEG and RMEG values used.
NA Not Analyzed
ND Not Detected at laboratory detection levels.
LTHA Life Time Health Advisory
* Intermediate EMEG
+ RMEG for Chromium VI
References - 25, 26
| CONTAMINANT | Range of Detection (µg/L) | COMPARISON VALUE | |
|---|---|---|---|
| µg/L | Source | ||
| Inorganic Compounds | |||
| Aluminum | <16.0 - 28,800 | None | None |
| Antimony | <11.0 - 24.2 | 4 | RMEG |
| Arsenic | <1.0 - 16.7 | 0.02 | CREG |
| Barium | <20.0 - 282 | 700 | RMEG |
| Beryllium | <1.0 | 0.008 | CREG |
| Boron | <19.0 - 184 | 100 | EMEG* |
| Cadmium | <1.0 - <4.6 | 7 | EMEG |
| Chromium (Total) | <5.0 - 48.5 | 50 | RMEG+ |
| Cobalt | <3.0 - 46.2 | None | None |
| Copper | <1.0 - 112 | None | None |
| Lead | <1.0 - 42.0 | None | None |
| Manganese | <1.0 - 3,160 | 50 | RMEG |
| Nickel | <8.0 - 152 | 100 | LTHA |
| Thallium | <1.0 - 3.0 | 0.4 | LTHA |
| Vanadium | <4.0 - 78.0 | 30 | EMEG* |
| Zinc | <2.0 - 429 | 3,000 | RMEG |
| Volatile Organic Compounds | |||
| Benzene | ND | 1 | CREG |
| Bromodichloromethane | ND | 0.6 | CREG |
| Chloroform | ND | 6 | CREG |
| 1,2-Dichloroethane | 12.0 - 13.0 | 0.4 | CREG |
| 1,1-Dichloroethylene | 3.0 - 28.0 | 0.6 | CREG |
| Ethylbenzene | ND | 1,000 | EMEG |
| Methylene Chloride | ND | 5 | CREG |
| Tetrachloroethylene | 1.0 | 0.7 | CREG |
| 1,1,2-Trichloroethane | ND | 0.6 | CREG |
| Trichloroethylene | 7.0 | 3 | CREG |
| Vinyl Chloride | 2.0 | 0.2 | EMEG |
| Semi-Volatile Organic Compounds | |||
| Bis(2-ethylhexyl)phthalate | 5.0 - 20.0 | 3 | CREG |
| 3,3-Dichlorobenzidine | ND | 0.08 | CREG |
| Pentachlorophenol | ND | 0.3 | CREG |
| Polynuclear Aromatic Hydrocarbons Compounds | |||
| Benzo(a)anthracene | ND | None | None |
| Benzo(a)pyrene | ND | 0.005 | CREG |
| Benzo(b)fluoranthene | ND | None | None |
| Benzo(g,h,i)perylene | ND | None | None |
| Benzo(k)fluoranthene | ND | None | None |
| Chrysene | ND | None | None |
| Dibenzo(a,h)anthracene | ND | None | None |
| Indeno(1,2,3-cd)pyrene | ND | None | None |
| Naphthalene | 0.12 | 20 | LTHA |
| Phenanthrene | ND | None | |
| Pesticides | |||
| Aldrin | ND | 0.002 | CREG |
| Poylchlorinated Biphenyl Compounds | |||
| PCBs | ND | 0.005 | CREG |
- Upgradient wells are TL-12A, TL-13A, TL-14A, TL-23A, and CBS-10A.
Background wells are CBS-5A, CBS-9A, WWC-2, TL-16, and 89.7-P1.
Child EMEG and RMEG values used.
LTHA Life Time Health Advisory
* Intermediate EMEG
+ RMEG for Chromium VI
NA Not Analyzed for.
ND Not Detected at laboratory detection levels.
References - 26
| Pathway Name | Exposure Pathway Elements | Time | ||||
|---|---|---|---|---|---|---|
| Source | Media | Point of Exposure | Route of Exposure | Exposed Population | ||
| Completed Exposure Pathways | ||||||
| Surface Soils | STF | Surface Soils and Soil Dust | Dismantling Yard Railyard Airport Swamp | Ingestion, Inhalation, and Dermal Contact | Recreationalists/trespassers | Past Present Future |
| Surface Water | STF | Surface Water | Dismantling Yard Swamp Airport | Ingestion,Inhalation, andDermal Contact | Recreationalists/trespassers | Past Present Future |
| Sediments | STF | Sediments | Dismantling Yard Swamp Airport | Ingestion, andDermal Contact | Recreationalists/trespassers | Past Present Future |
| Potential Exposure Pathways | ||||||
| Groundwater | STF | On-site andOff- siteGroundwater | Public andPrivate(Industrial andResidential)Supply Wells | Ingestion,Inhalation, andDermal Contact | Workers and Residents | Past Present Future |
| Surface Soils | STF | Surface Soils and Soil Dust | Amsted TIP | Ingestion, Inhalation, and Dermal Contact | Recreationalists/trespassers | Past Future |
| Subsurface Soils | STF | Exposed SubsurfaceSoils andSoil Dust | Dismantling Yard Railyard Amsted Airport Swamp | Ingestion,Inhalation, andDermal Contact | On-site Workers andRecreationalists/trespassers | Future |
APPENDIX - C
Exposure Assumptions
| Child | ||
|---|---|---|
| Exposure Frequency | 2 days per week 52 weeks per year | |
| Exposure Duration | 6 years | |
| Exposure Time | 365 days per year 6 years | |
| Body Weight | 16 kg | |
| Ingestion Rate | 200 mg per day | |
| Adult | ||
| Exposure Frequency | 1 day per week 52 weeks per year | |
| Noncarcinogenic Evaluation | ||
| Exposure Duration | 30 years (6 years as child and 24 years as adult) | |
| Exposure Time | 365 days per year 30 years | |
| Carcinogenic Evaluation | ||
| Exposure Duration | 30 years | |
| Exposure Time | 365 days per year 70 years | |
| Body Weight | 70 kg | |
| Ingestion Rate | 100 mg per day | |
Exposure Factor (EF) = exposure frequency x exposure duration ÷ exposure time
| C | = | contaminant concentration (mg/kg) |
|---|---|---|
| IR | = | soil ingestion rate (mg/day) |
| EF | = | exposure factor (unitless) |
| BW | = | body weight (kg) |
A conversion factor of 10-6 kg/mg is required to convert the soil contaminant concentration (C)from mg/kg to mg/mg soil.
Surface Water Exposure Assumptions
| Child | ||
|---|---|---|
| Exposure Frequency | 2 days per week 12 weeks per year (3 months of summer) | |
| Exposure Duration | 6 years | |
| Exposure Time | 365 days per year 6 years | |
| Body Weight | 16 kg | |
| Ingestion Rate | 0.05 liters per day | |
| Adult | ||
| Exposure Frequency | 1 day per week 12 weeks per year (3 months of summer) | |
| Noncarcinogenic Evaluation | ||
| Exposure Duration | 30 years (6 years as child and 24 years as adult) | |
| Exposure Time | 365 days per year 30 years | |
| Carcinogenic Evaluation | ||
| Exposure Duration | 30 years | |
| Exposure Time | 365 days per year 70 years | |
| Body Weight | 70 kg | |
| Ingestion Rate | 0.05 liters per day | |
Based on EPA recommended intake value for intensive water activities, (e.g., swimming),accidental ingestion of surface water during water activities is assumed to be 50 ml per hour forboth children and adults, assuming that water activity occurs 1 hour per visit.
Exposure Factor (EF) = exposure frequency x exposure duration ÷ exposure time
| C | = | contaminant concentration (µg/L) |
|---|---|---|
| IR | = | water ingestion rate (L/day) |
| EF | = | exposure factor (unitless) |
| BW | = | body weight (kg) |
A conversion factor of 10-3 mg/µg is required to convert the water contaminant concentration (C) from µg/L to mg/L water.
Equations for Surface Soil and Sediment Ingestion
Noncarcinogenic Evaluation
Child Estimated Daily Exposure Dose = (C x IR x EF X 10-6)/BW
Adult Estimated Daily Exposure Dose =
C x 10-6 x [{(child IR x child exposure frequency x child exposure duration)/(child BW x 365 days/year)} + {(adult IR x adult exposure frequency x adult exposure duration )/30 years}/(adult BW x 365 days/year)]
Equations for Surface Water Ingestion
Noncarcinogenic Evaluation
Child Estimated Daily Exposure Dose = (C x IR x EF X 10-3)/BW
Adult Estimated Daily Exposure Dose =
C x 10-3 x [{(child IR x child exposure frequency x child exposure duration)/(child BW x 365 days/year)} + {(adult IR x adult exposure frequency x adult exposure duration )/30 years}/(adult BW x 365 days/year)]
Carcinogenic Evaluation
Cancer Risk = Estimated Daily Exposure Dose x Cancer Slope Factor
Exposure Factor used in the estimated daily exposure dose for the cancer risk equation is:
EF = adult exposure frequency x adult exposure duration (30 years) ÷ adult exposure time (365days per year x 70 years)
Response to Public Comments
The South Tacoma Field Public Health Assessment was made available for public review andcomment from April 17, 1995, through July 7, 1995. During the public comment period, writtencomments were submitted from one party, Tacoma Industrial Properties. The followingresponses address the comments specific to Tacoma Industrial Properties and pertinent to thepublic health assessment.
| 1. | Comment: Second page of the Summary, last paragraph. Reference is made to "restrictingpublic access and maintaining site security at ..., Tacoma Industrial Properties..." In response, theTIP site is surrounded by a chain-link fence with a gate at the South Proctor Street entrance. Thisgate is locked after normal business hours. This is the only physical restriction planned for theTIP site. No remedial action is required for this site. In general, this paragraph is too broad,burdensome, and misleading as to the actions required of a specific property owner. Response: The public health assessment has been revised to indicate that the TIP sampling unitis fenced. In response to the comment concerning the vagueness of the public health assessmentrecommendations, ATSDR acts as an advisory agency providing recommendations for actionsneeded to protect public health. These recommendations are primarily directed at regulatoryagencies, such as EPA. ATSDR intentionally makes recommendations so that response optionsare not specific, thus allowing regulatory agencies flexibility in developing risk managementdecisions for appropriate remedial actions in effort to satisfy CERCLIS requirements, as well asATSDR recommendations. |
|---|---|
| 2. | Comment: Page 5, Paragraph 7, Line 9: The building occupied by Savage Industries is on theformer Griffin Wheel site, not BNR as written. Griffin Wheel is a division of Amsted Industries,owner of the property adjacent to TIP. Response: For clarification the sentence has been changed from "...in old BNR building..." to"...in a former wood patterns and vaults building." |
| 3. | Comment: Page 22, A. Surface Soils Pathway, Last paragraph: TIP site is fenced and is noway used as a recreational park. Response: See response to comment 1. |
| 4. | Comment: Page 48, Conclusions: "The South Tacoma Field site poses a public healthhazard..." should read "[Prior to remediation,] [t]he South Tacoma Field site poses a publichealth hazard..." It should be made clear the remedial actions will alleviate any health threats. Otherwise, the RI/FS and cleanup are for naught. Response: ATSDR Public Health Assessment is an evaluation of relevant environmental data,health outcome data, and community concerns associated with current conditions of a hazardouswaste site. From this evaluation, public health implications posed by the site are determined. The health assessment does not attempt to predict public health implications based on proposedremedial actions to be conducted at the site. However, should monitoring data from siteremediation become available, ATSDR could assess whether remedial actions are indeedeffective in protecting public health. |
| 5. | Comment: Page 50, paragraph 2: Inclusion of TIP in this paragraph is erroneous per the RI/FSand ROD. Concentrations of lead and arsenic are not elevated in comparison to other sites. PCBs were not detected on the TIP site. Response: As stated in the Conclusions section of the health assessment, manganese is the onlycontaminant of health concern found in surface soils at the TIP sampling unit. In theRecommendations section, contaminants of concern and sampling units were grouped by specificrecommendation. However for clarity, the layout of recommendations will be changed so thatrecommendations are organized by specific sampling units. |
| 6. | Comment: Page 52, Action Undertaken, paragraph 2: As previously stated, the TIP site issurround by a chain-link fence. There have been some cases of trespass and vandalism, butsecurity for the most part has been maintained. Response: See response to comment 1. |


