PUBLIC HEALTH ASSESSMENT
TRAVIS AIR FORCE BASE (AFB)
UNITED STATES AIR FORCE
SOLANO COUNTY, CALIFORNIA
APPENDIX A: ACRONYMS AND ABBREVIATIONS
| AFB | Air Force Base |
| ATSDR | Agency for Toxic Substances and Disease Registry |
|
CPT |
cone penetrometer testing |
| CREG | Cancer Risk Evaluation Guide |
| DCA | dichloroethane |
| DCE | dichloroethene |
| DOD | U.S. Department of Defense |
| EMEG | Environmental Media Evaluation Guides |
|
EPA |
U.S. Environmental Protection Agency |
| IROD | Interim Record of Decision |
| LLNL | Lawrence Livermore National Laboratory |
| MCL |
maximum contaminant level |
| µg/kg | microgram per kilogram |
| µg/L | microgram per liter |
| µg/m3 | microgram per cubic meter |
| MRL | Minimal Risk Level |
| MW | monitoring well |
| NEWIOU | North, East and West Industrial Operable Unit |
| ND | not detected |
|
NIOSH |
National Institute for Occupational Safety and Health |
| NPL | National Priorities List |
| OSHA | Occupational Safety and Health Administration |
| OU | operable unit |
| OVA | Organic Vapor Analyzer |
| PCB | polychlorinated biphenyl |
| pCi/g | picoCuries per gram |
| ppmv | parts per million per volume |
| ppb | parts per billion |
| ppbv | parts per billion per volume |
| PHA | Public Health Assessment |
| RDX | "Royal Dutch Explosive" ordnance compound, cyclotrimethylenetrinitramine |
| REL | recommended exposure limit |
| RfC | Reference Concentration |
| RI | Remedial Investigation |
| ROD | Record of Decision |
| TCE | trichlorethylene |
|
TPH |
total petroleum hydrocarbon |
| VOC | volatile organic compound |
| APPENDIX B: SOURCE SITE EVALUATION SUMMARY | |||
| Operable Unit | Site Included | Situations Evaluated in this Public Health Assessment | Evaluation |
| East Industrial Operable Unit | - Storm Sewer System - Fire Training Areas #,2,3,4 - STP Sludge Disposal Area - Solvent Spill Area - Oil Spill Area - STP Inactive - Oxidation Ponds - Tanks and Spill Area at AAFES NSGS - Facility 363/1201 - Aircraft Hardstand Area MW-329 - MW-269 - Facility 1205 - MW-246 |
- Storm Sewer System - Fire Training Area #4 - AAFES NSGS (Gasoline Station) - MW-269 (Bld. 1125) |
These are sites with surface soil, sub-surface
soil, soil gas, shallow groundwater and surface water contamination. Based
on the information and data currently available for these sites, ATSDR
concludes that there are no public health hazards associated with the areas
not specifically described and evaluated in this PHA.
For the sites listed, but not specifically evaluated in this PHA:
|
| West Industrial Operable Unit | - JP-4 Spill Area - TF33 Test Stand - Pipeline east of Facilities 810,818. 839, 842 - Aircraft Maintenance Hanger, North - Aircraft Maintenance Hangers - Facility 872 - Sanitary Sewer Line (between facilities 810, 919 and east of facilities 837, 838) |
- None | |
| West, Annexes, Base-wide Operable Unit | - Landfill #3 and Grazing Management Unit 2 - Grazing Management Units 7&8 - Landfill X - RB-1 Radioactive Waste Burial - RB-2 Radioactive Waste Burial |
- Grazing Management Units 7&8 - Landfill X |
|
| North Operable Unit | - Landfill #1 - Landfill #2 - Cyanide Disposal Pit |
- Landfill #1 - Landfill #2 |
|
| Others | - B-29 Crash Site - Union Creek south of base |
- B-29 Crash Site - Union Creek south of base |
|
APPENDIX C: ATSDR PUBLIC HEALTH CONCLUSION CATEGORIES
| Category | Definition | Criteria |
| A. Urgent public health hazard | This category is used for sites that pose an urgent public health hazard as the result of short-term exposures to hazardous substances. |
|
| B. Public health hazard | This category is used for sites that pose a public health hazard as the result of long-term exposures to hazardous substances. |
|
| C. Indeterminate public health hazard | This category is used for sites with incomplete information. |
|
| D. No apparent public health hazard | This category is used for sites where human exposure to contaminated media is occurring or has occurred in the past, but the exposure is below a level of health hazard. |
|
| E. No public health hazard | This category is used for sites that do not pose a public health hazard. |
|
APPENDIX D: SOIL GAS SAMPLES (TCE, DCE, AND TPH) FROM STORM
SEWER
B STUDY *
| Sample ID | Depth ( feet below ground surface) |
Contaminant | Concentration (ppbv) |
| 810-B01 | 15 | TCE | 3,618 |
| 810-B02 | 5 15 |
TPH-G TCE TPH-G |
25,000 840 15,000 |
| 810-B03 | 9 15 |
TCE DCE TCE DCE |
54,000 22,000 33,000 23,000 |
| 810-B04 | 8 14.33 |
TCE DCE DCE TCE |
9,400 18,000 106 570 |
| 810-B05 | 15 | TCE TPH-G |
101 73,000 |
| 810-B06 | 5 15 |
TPH-G TPH-G |
21,000 62,000 |
| 810-B07 | 6 10 |
TPH-G TPH-G |
16,000 10,000 |
| S3-C04 | 6 10 |
TCE TPH-G TCE |
772 18,000 128 |
| S3-C06 | 5.5 9 |
TPH-G TPH-G |
310,000 1,195,000 |
| SSSB-B01 | 4 9 |
TPH-G TPH-G |
2,700,00 4,000 |
| SSSB-B02 | 4 | TPH-G | 300 |
| SSSB-C01 | 6 10 |
TPH-G TPH-G |
23,000 23,000 |
| SSSB-C02 | 6 10 |
TPH-G TPH-G |
5,900 14,000 |
| SSSB-C03 | 10 | TPH-G | 2,800 |
| SSSB-C04 | 10 | TPH-G | 12,000 |
| SSSB-C05 | 4.5 | TPH-G | 3,500 |
| SSSB-C06 | 9 | TPH-G | 4,100 |
| SSSB-C12 | 4.5 9 |
TPH-G TPH-G |
180,000 2,800 |
| SSSB-M01 | 10 | TCE | 510 |
| 1917-B01 | 5.5 | TPH-G | 4,100 |

Figure 1: Location of Travis AFB

Figure 2: Travis AFB

Figure 3: Duck Pond

Figure 4: Buildings 810, 844, 845

Figure 5: Landfill 1

Figure 6: On-Base Gasoline Stations

Figure 7: Groundwater Plumes (Migrating Offsite): Fire Training Area 4, Landfill 2, Building 1125

Figure 8: Union Creek

Figure 9: B-29 Crash Site

Figure 10: Grazing Areas - Landfill X and Grazing Management Units 7 & 8
1. Abbreviations and acronyms are defined in Appendix A.
2. ATSDR and other agencies, such as the US EPA and California regulatory agencies have developed screening values or comparison values to provide guidelines for estimating minimum concentrations of a contaminant that may possibly cause adverse health effects, given a standard exposure rate and standard body weights. These values are used as screening mechanisms when evaluating contaminant levels detected in sample analyses to determine whether the levels found require more detailed examination.
3. Bioaccumulation is the term used to describe the increased concentration of a contaminant that occurs in a predator species as it consumes prey containing a contaminant.
4. The CREG is determined based on a 70 year lifetime exposure to this level. The benzene that might leak into this trailer would be at lower concentrations than the already low levels found in the crawlspace. And, because of the relatively short time for residents to be expected in these trailers, the exposure period is considerably less than the 70 years used in determining the CREG.
5. Screening values for the other chemicals are: acetone, 13,000 ppb (chronic EMEG/MRL); hexane 67.11 ppbv (RMEG/RfC); methanol, no threshold level, exposure to 250,000 ppb will cause temporary and reversible effects (headache) (18); xylene 100 ppb (MRL); pentane 120,000 ppb (NIOSH Recommended Exposure Limit (REL); propylene, no threshold limit for toxic effects, at high concentrations (part per hundred), propylene acts as an asphyxiant (19); and toluene, 1000 ppb (EMEG/MRL).
6. The study conducted by California was a large-scale study of the overall quality of fishery resources in the San Francisco Bay area.
7. CPT is a form of well installation that involves pushing a small diameter casing to a relatively shallow depth, rather than drilling a borehole and inserting casing in separate steps.


