Table 2.
Status of Investigation at ALAAP Study Areas Study Area No. | Site Name | Site Description | Media/ Contaminant | Status of Investigations |
AREA A |
11 | Magazine Area | Contained a series of buildings (igloos) for storage of explosives. Timbering activity. | Soil-Low level contamination. | Partially remediated in 1988. No further remedial action required. |
12 | Old Burning Ground | Served as burn area for failed batches of munitions compounds and contained a lead remelt area. | Soil-Low SVOCs and metal contamination. | This area was remediated in 1988 and 1994. |
13 | Small Arms Ballistics Range | Training range for small arms ballistics. Area used for controlled burning. | Soil-Metals and PAHs. | Metal-contaminated soil was removed in 1987. The FS proposes excavation and off-site disposal of PAH-contaminated soil. |
14 | Cannon Range | Test cannon firing area. Area is restricted by a fence. | Soil-Lead. | The FS proposes excavation and off-site disposal of lead- contaminated soil. |
15 | Old Well | An abandoned debris-filled well. | Groundwater-VOCs, SVOCs, nitroaromatic compounds, and metals. Soil-No sampling conducted. | Wells and contaminated soil were removed in 1987/1988. No further remedial action required. |
17 | Propellant Shipping Area (Eastern Portion) | Area consisted of buildings used for storage and shipping of propellants. | Soil-Low concentrations of nitroaromatic compounds and metals. | All buildings have been removed. No further remedial action required. |
29 | Rubble Pile | Area contained debris from an acid sump. | Soil-Lead and nitroaromatic compounds Groundwater - Nitroaromatic compounds. | Lead- and nitroaromatic- contaminated soil was removed in 1987/1988. No further remedial action required. |
30 | New Trench | A debris pile. | Soil-Low concentrations of metals and nitroaromatic compounds. | Soil was removed in 1987 and 1994. No further remedial action required. |
31 | Disposal Area | A small disposal area. | Soil-Low concentrations of metals. | Soil was removed in 1987. No further remedial action required. |
32 | No. 2 Rubble Area | Disposal area for general wastes and equipment. | Soil-Nitroaromatic compounds and metals | This area was remediated during 1987/1988. No further remedial action required. |
33 | Henningburg Area | A small disposal area. | Soil-SVOCs. | This area was remediated during 1987/1988. No further remedial action required. |
34 | 229 Area | A small disposal area. | Soil-Metals and SVOCs. | This area was remediated during 1987/1988. No further remedial action required. |
AREA B |
2 | Smokeless Powder Facility | Located on 74 acres in the leaseback area south of Area B. | Soil-Nitroaromatic compounds, PCBs. Groundwater - Nitroaromatic compounds and metals. | Buildings were decontaminated and burned. FS proposes remediation of explosive hot spots.a,b,c |
3 | Sanitary Landfill and Lead Facility | 7.5-acre landfill used between 1940s and 1970s for disposal of soil, domestic waste, and building rubble. | Soil - Low-level metal contamination. | No further action.d |
4 | Manhattan Project | Facility designed to produce heavy water. | Soil - Lead. | Facility buildings removed in 1945 and 1946. No further action.d |
5 | Red Water Storage Basin | Intended as a settling basin for TNT manufacturing process wastewaters. | No significant contamination. | No further action. |
6 | Southern TNT Manufacturing Area | New TNT production area. | Soil and Groundwater - Nitroaromatic compounds. Friable asbestos found along production pipelines. | TNT-contaminated soil removed to 100 mg/kg.e No further action. |
7 | Northern TNT Manufacturing Area | Old TNT production area. | Soil and Groundwater - Nitroaromatic compounds. Friable asbestos found along production pipelines. | TNT-contaminated soil removed to 100 mg/kg. e No further action. |
8 | Acid/Organic Manufacturing Area | An 104-acre area used to produce nitrobenzene, concentrated nitric acid, oleum, and sodium sulfite to form aniline and N-N-dimethylanimine. | Soil - Lead and nitrobenzene. Transite and friable asbestos mixed with soil over 12 acres. | No further action. d |
9 | Aniline Sludge Basin | An unlined basin used for storage of liquid waste and sludges from the production of the Acid/Organic Manufacturing Area. | Sediment-Arsenic and nitroaromatic compounds. | No further remedial action advised. d |
10 | Tetryl Manufacturing Area | Tetryl production area. | Soil - Tetryl and lead. Friable asbestos found in area. | Contaminated soil removed from western portion to 100 mg/kg. e No further remedial action required. |
16 | Flashing Ground | Consists of four trenches used for burning of combustible trash and explosives. | Soil - Nitroaromatic compounds and lead. | No further remedial action advised. b |
17 | Propellant Shipping Area (Western Portion) | Used for shipping of smokeless powder and high explosives. | Soil - Nitroaromatic compounds. Groundwater - Nitroaromatic compounds and metals. | FS proposes remediation of contaminated soil and groundwater. All buildings have been removed. a,c |
18 | Blending Tower Area | Blending area for smokeless powder. | Soil - Low concentrations of nitroaromatic compounds. Groundwater-Nitroaromatic compounds and metals. | FS proposes remediation of groundwater. c No further remedial action required for soil. |
19 | Lead Remelt Facility | Used for pouring of lead ingots. | Soil - High concentrations of lead. | FS proposes remediation of lead mounds. a |
20 | Rifle Powder Finishing Area | Area used for finishing of rifle powder and, perhaps, glazing. | Soil - Low concentrations of 2,4-DNT. Groundwater - Nitroaromatic compounds and metals. | FS proposes remediation of groundwater. c No further remedial action required for soil. |
21 | Red Water Ditch | Ditch running east to west through Area B. | Sediment - Lead, chromium, and nitroaromatic compounds. | TNT-contaminated soil removed to 100 mg/kg. e, d |
22 | Demolition Landfill | Landfill used for demolition debris, including lead and friable asbestos. | Soil - Lead, PAHs, and, nitroaromatic compounds | FS proposes removal of contaminated soil. a, b |
25 | Storage Battery/ Demolition Debris | Area for dumping old construction debris and lead acid battery casings. | No significant contamination. | FS proposes removal of batteries and debris from hillside. |
26 | Crossover Ditch | Ditch running from the central portion of Area B toward the Coosa River. | Sediment - Low concentrations of metals and nitroaromatic compounds. | No further remedial action required. d |
27 | Beaver Pond Drainage System | Two large beaver dams affected the original site drainage and accumulated contaminated surface runoff. | No significant contamination in surficial sediment. | No further remedial action required. b |
Building 6 | Coke Oven | Area received surface water drainage from the Smokeless Powder Facility. | No significant contamination. | No further remedial action required. |
| Transformer Storage Buildings | Buildings used to store transformers. Some have released contents to surrounding soil. | Soil - PCBs. | FS proposes remediation of PCB-contaminated soil. a |
| Downed Utility Poles with Transformers | A total of 27 downed utility poles, most within the southern section of the GSA. Some transformers may have released contents to surrounding soil. | Soil - PCBs. | FS proposes remediation of PCB-contaminated soil. a |
| Underground storage tanks (USTs) | Two 12,000-gallon USTs contained diesel fuels or gasoline. | No significant contamination. | USTs were removed in 1993. No further remedial action required. |
| Gas Station | A gas station may have been located in Area B. | No significant contamination. | All USTs had been removed. No further remedial action required. |
223B | Fertilizer and Pesticide Storage Building | Buildings used to store fertilizers and pesticides by a private company. | No significant contamination. | Storage buildings were cleaned out in 1991. No further remedial action required. |
Table 3.
Potential Exposure Pathways Table Pathway Name | Source of Contamination | Environmental Medium | Point of Exposure | Route of Exposure | Exposed Population | Comment |
On-site Soil | ALAAP-Area B | Soil: nitroaromatic compounds, lead | On-site soil | Dermal contact | Hunters and loggers (estimated 250 to 500 individuals) | Past, Current, and Future: - Hunters and loggers used areas that either contained low levels of contamination or were not used for industrial activities.
- Dermal contact with soil in these areas is not likely to result in adverse health effects.
|
Drinking Water | ALAAP-Area B | Groundwater: nitroaromatic compounds, lead | Future Area B wells | Ingestion, inhalation, and dermal contact | Future Area B users | Future: - No on-site drinking wells currently draw water from the groundwater beneath Area B.
- This pathway will not pose a health hazard if Area B groundwater use restrictions apply.
|
Coosa River | ALAAP-Area B | Surface water and sediment: nitroaromatic compounds, metals | Coosa River near ALAAP | Dermal contact | Boaters and Anglers (estimated 250 to 500 people) | Past, Current, and Future: - Only low levels of contaminants were detected in the Coosa River sediment; surface water concentrations are probably lower than sediment concentrations.
- Dermal contact with Coosa River surface water and sediment while boating or fishing is unlikely to result in adverse health effects.
|
Game | ALAAP-Areas A and B | Deer and small game: nitroaromatics, lead | Area A and abutting woodland | Ingestion | Hunters and their families (estimated 250 to 1,000) people) | Past, Current, and Future: - Deer and small game that graze on the site have not accumulated significant amounts of site-related compounds.
- Consumption of venison or small game hunted from is unlikely to result in adverse health effects.
|
Fish | ALAAP-Area B | Fish: mercury | Coosa River | Ingestion | Anglers and their families (estimated 250 to 1,000 people) | Past, Current, and Future: - Mercury was detected in fish from on-site ditches and drainages. The levels were below the FDA action level for mercury.
- Although Coosa River fish have not been analyzed for mercury, unfavorable fishing conditions most likely limit fishing and potential health hazard from consumption of fish.
|
Several exposure pathways have not been included in the table because past, current, orfuture exposure through the pathway is extremely unlikely. Site characterization suggeststhat the media or point of exposure has not been contaminated or that exposure was briefand intermittent. These pathways include groundwater exposure pathways through municipal,private wells, and Area B water supply (past and current exposure); and past trespassers'exposure to on-site soils and surface water pathways.