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Air Force Plant No. 83, otherwise known as General Electric Aircraft Engine Business Group's Albuquerque Plant, is located in the southern portion of Albuquerque, New Mexico. The plant site is approximately one mile due west of Kirtland AFB. The facility is comprised of approximately 30 major buildings which cover 586,790 square feet within a 33-acre area. General Electric Company (GE) operates industrial facilities at Air Force Plant No. 83. GE has been at Plant No. 83 since 1967, when the Air Force assumed ownership of the plant from the Atomic Energy Commission. GE operations involve the manufacturing of aircraft engine parts, sub-assemblies, and spare parts for military and commercial jet engines. Conclusions have been developed based on the results of the project team's field inspection, review of base records and files, and interviews with base personnel. Each of the five sites were ranked using the HARM system and were determined to have a sufficient potential for environmental contamination to warrant some degree of follow-on investigation. These sites are: North parking lot; Hazardous waste storage Nos. 1, 3, and 4; and Underground cyanide vault.
In accordance with the procedures developed for the Department of Defense (DOD) Installation Restoration Program (IRP), and the EPA's April 1984 Scope of Work, a Phase II, Stage I site investigation has been performed at the Former USAF Plant No. 83 in Albuquerque, New Mexico. Investigations were conducted at identified hazardous waste storage sites and in other areas of the plant. A total of 12 monitoring wells were installed, seven (7) in the upper water-bearing zone and five (5) in the intermediate aquifer. Boreholes were continuously monitored during drilling with an OVA, with select samples being sent to the laboratory for priority pollutant analysis. Eight (8) samples of the sediment in the San Jose Drain were also obtained for analysis. Two deep wells (DWA-1 and DWA-2) were pumped for 24 hours and water levels measured in several nearby shallow wells in order to evaluate the in-situ permeability of the clay unit. Groundwater samples were obtained from all the wells during this investigation and three existing monitoring wells at the site. Keywords: Installation Restoration Program, Volatile Organic Compounds, Superfund Site, New Mexico, Metals, Soil Sample, hazardous materials.
In accordance with the procedures developed for the Department of Defense (DOD) Installation Restoration Program (IRP), and the EPA's April 1984 Scope of Work, a Phase II, Stage I site investigation has been performed at the Former USAF Plant No. 83 in Albuquerque, New Mexico. Investigations were conducted at identified hazardous waste storage sites and in other areas of the plant. A total of 12 monitoring wells were installed, seven (7) in the upper water-bearing zone and five (5) in the intermediate aquifer. Boreholes were continuously monitored during drilling with an OVA, with select samples being sent to the laboratory for priority pollutant analysis. Eight (8) samples of the sediment in the San Jose Drain were also obtained for analysis. Two deep wells (DWA-1 and DWA-2) were pumped for 24 hours and a.
In accordance with the procedures developed for the Department of Defense (DOD) Installation Restoration Program (IRP), and the EPA's April 1984 Scope of Work, a Phase II, Stage I site investigation has been performed at the Former USAF Plant No. 83 in Albuquerque, New Mexico. Investigations were conducted at identified hazardous waste storage sites and in other areas of the plant. A total of 12 monitoring wells were installed, seven (7) in the upper water-bearing zone and five (5) in the intermediate aquifer. Boreholes were continuously monitored during drilling with an OVA, with select samples being sent to the laboratory for priority pollutant analysis. Eight (8) samples of the sediment in the San Jose Drain were also obtained for analysis. Two deep wells (DWA-1 and DWA-2) were pumped for 24 hours and water levels measured in several nearby shallow wells in order to evaluate the in-situ permeability of the clay unit. Groundwater samples were obtained from all the wells during this investigation and three existing monitoring wells at the site. Keywords: Installation Restoration Program, Volatile Organic Compounds, Superfund site, New Mexico, Metals, Soil Sample, hazardous materials.
This report provides the Installation Restoration Program (IRP) Phase I-Records Search for Air Force Plant 78, Morton-Thiokol, Brigham City, Utah. This is a report of a study conducted to identify past potentially hazardous material disposal sites. Interviews and document searches were conducted to determine sites that were potentially contaminated. Keywords: Installation restoration program, Air Force plant 78, Hazardous waste.
This report provides the Installation Restoration Program (IRP) Phase I-Records Search for Air Force Plant 36, Evendale, Ohio. This is a report of a study conducted to identify past potentially hazardous material disposal sites. Interviews and document searches were conducted to determine sites that were potentially contaminated. Keywords: Installation Restoration Program (IRP), Hazardous waste.
Contents: Glossary of Terminology, Abbreviations, and Acronyms; Team Member Biographical Data; List of Interviewees; Master List of Shops; Water Quality Criteria; Water Quality Data; Hazard Assessment Rating Methodology; Hazard Assessment Rating Methodology Forms; Index of References to Potential Contamination Sources; Leases and Agreements. (fr).
This report provides an introduction, description, and environmental setting of Air Force Plant 44, Tucson, Arizona. It reviews past and present practices of wastewater treatment, landfills, waste oil pits, chrome and die yard pits, disposal and spill sites. A total of 11 sites were ranked using the HARM (Hazard Assessment Rating Methodology) rating system. (Author).
The goal of the IRP Phase I study is to identify sites where there is potential for environmental contamination resulting from past waste disposal practices and to assess the potential for contaminant migration from these sites. The conclusions are based on the evaluation of information collected from the project team's field inspection; review of records and files; examination of historical aerial photographs; and interviews with base personnel, past employees, and state and local government employees. Sixty-one potential contamination sources were identified on ANG, Camp Edwards/ARNG, USAF, and VA facilities at MMR. These sites are identified and their evaluation summarized in Table 5.0-1. Locations of these sites are shown in Figures 5.0-1 through 5.0-7. Forty-six of the 61 sites were determined to have a potential for contamination and contaminant migration. (fr).