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

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
TABLE 1
Contaminants of Concern in On-Site Surface Soils, Phase I and II
| 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 |
TABLE 2
Contaminants of Concern in On-Site Subsurface Soils, Phase I
| 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 |
TABLE 3
Contaminants of Concern in On-Site Subsurface Soils, Phase II
| 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 Carcinogenic PAHs | 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 |
TABLE 4
Contaminants of Concern in On-Site Groundwater
| 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 |
TABLE 5
Contaminants of Concern in On-Site Surface Water
| 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 |
TABLE 6
Contaminants of Concern in On-Site Sediments
| 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 |
TABLE 7
Contaminants of Concern in Off-Site Groundwater
Upgradient and Background Wells
| 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 |
TABLE 8
Completed and Potential Exposure Pathways
| 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, and Dermal Contact | Recreationalists/trespassers | Past Present Future |
| Sediments | STF | Sediments | Dismantling Yard Swamp Airport |
Ingestion, and Dermal Contact | Recreationalists/trespassers | Past Present Future |
| Potential Exposure Pathways | ||||||
| Groundwater | STF | On-site and Off- site Groundwater | Public and Private (Industrial and Residential) Supply Wells | Ingestion, Inhalation, and Dermal 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 Subsurface Soils and Soil Dust | Dismantling Yard
Railyard Amsted Airport Swamp |
Ingestion, Inhalation, and Dermal Contact | On-site Workers and Recreationalists/trespassers | Future |
Surface Soil and Sediment 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 for both 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 (365
days per year x 70 years)
Response to Public Comments
The South Tacoma Field Public Health Assessment was made available for public review and comment from April 17, 1995, through July 7, 1995. During the public comment period, written comments were submitted from one party, Tacoma Industrial Properties. The following responses address the comments specific to Tacoma Industrial Properties and pertinent to the public health assessment.
| 1. | Comment: Second page of the Summary, last paragraph. Reference is made to "restricting
public access and maintaining site security at ..., Tacoma Industrial Properties..." In response, the
TIP site is surrounded by a chain-link fence with a gate at the South Proctor Street entrance. This
gate is locked after normal business hours. This is the only physical restriction planned for the
TIP 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 unit is fenced. In response to the comment concerning the vagueness of the public health assessment recommendations, ATSDR acts as an advisory agency providing recommendations for actions needed to protect public health. These recommendations are primarily directed at regulatory agencies, such as EPA. ATSDR intentionally makes recommendations so that response options are not specific, thus allowing regulatory agencies flexibility in developing risk management decisions for appropriate remedial actions in effort to satisfy CERCLIS requirements, as well as ATSDR recommendations. |
| 2. | Comment: Page 5, Paragraph 7, Line 9: The building occupied by Savage Industries is on the
former 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 no
way used as a recreational park.
Response: See response to comment 1. |
| 4. | Comment: Page 48, Conclusions: "The South Tacoma Field site poses a public health
hazard..." should read "[Prior to remediation,] [t]he South Tacoma Field site poses a public
health 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 hazardous waste 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 proposed remedial actions to be conducted at the site. However, should monitoring data from site remediation become available, ATSDR could assess whether remedial actions are indeed effective in protecting public health. |
| 5. | Comment: Page 50, paragraph 2: Inclusion of TIP in this paragraph is erroneous per the RI/FS
and 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 only contaminant of health concern found in surface soils at the TIP sampling unit. In the Recommendations section, contaminants of concern and sampling units were grouped by specific recommendation. However for clarity, the layout of recommendations will be changed so that recommendations are organized by specific sampling units. |
| 6. | Comment: Page 52, Action Undertaken, paragraph 2: As previously stated, the TIP site is
surround by a chain-link fence. There have been some cases of trespass and vandalism, but
security for the most part has been maintained.
Response: See response to comment 1. |