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Site-Related ContaminationSolid Waste Management Units (SWMU) and Areas of Concern (AOC) Surface water, sediment, groundwater, and soil samples were collected during several environmental investigations of the western and eastern sides of the island (Table 2). Metals have been detected in groundwater samples from all of the AOCs and SWMUs; pesticides at a few of the AOCs and SWMUs; and polychlorinated biphenyls (PCBs) at one of the SWMUs. Metals have been detected in sediment and surface water samples from the AOCs and SWMUs where samples have been collected. Metals have been detected in most of the soil samples collected from the AOCs and SWMUs. Pesticides and polycyclic aromatic hydrocarbons (PAHs) have been detected in soil collected from several of the AOCs and SWMUs. At this time, metals are the primary contaminants of concern to NOAA at the AFWTA site.
The maximum contaminant concentrations detected during the preliminary assessment/site investigations of the western side of
Site-specific or regionally specific screening guidelines are always used when available. In the absence of such guidance, the screening guidelines for groundwater and surface water are the ambient water quality criteria (AWQC) (USEPA 2002); the screening guidelines for sediment in a saltwater environment are the effects range-low (ERL) concentrations (Long et al. 1998); and the screening guidelines for soil are the Oak Ridge National Laboratory final preliminary remediation goals (ORNL-PRGs) (Efroymson et al. 1997) and the USEPA's ecological soil screening guidelines (USEPA 2004b). Maximum concentrations that exceeded relevant screening guidelines are discussed below. When known, the general sampling location of a sample that exceeded screening guidelines is also provided. SoilMetals and the pesticide dieldrin were detected in soil samples collected from the site at maximum concentrations that exceeded screening guidelines (Table 3). PAHs and the pesticides chlordane, 4,4'-DDE, 4,4'-DDD, and 4,4'-DDT were also detected in soil samples, but no ORNL-PRGs or ecological soil screening guidelines are available for comparison to the maximum concentrations of these contaminants. The maximum concentrations of arsenic, cadmium, and zinc were detected in samples collected from the main operations area on the western side of the island. The maximum concentrations of copper were detected in samples collected from SWMU 7 on the western side of
Except for 2-methylnaphthalene, naphthalene, and phenanthrene, the maximum concentrations of the PAHs were detected in soil samples collected from AOC R on the western side of the island. The maximum concentrations of 2-methylnaphthalene and naphthalene were detected in samples collected from AOC I. The maximum concentration of phenanthrene was detected at SWMU 6. ORNL-PRGs are not available for comparison to the maximum concentrations of detected PAHs (other than acenaphthene, which did not exceed the ORNL-PRG). The maximum concentrations of chlordane and 4,4'-DDD were detected in samples collected from SWMU 6 and AOC R, respectively. The maximum concentrations of 4,4'-DDE, 4,4'-DDT, and dieldrin were detected in samples collected from the main operations area. The maximum concentration of dieldrin exceeded the ecological soil screening guideline by a factor of approximately two. Surface Water
GroundwaterMetals and pesticides were detected in groundwater samples collected from the site at maximum concentrations that exceeded screening guidelines (Table 4). The maximum concentrations of cadmium, chromium, copper, lead, mercury, nickel, selenium, silver, vanadium, and zinc were detected in a sample collected from a monitoring well at SWMU 4 on the western side of
The pesticides 4,4'-DDT and dieldrin were detected in samples from the main operations area on the western side of
SedimentAll metals except for mercury were detected in sediment samples collected from SWMU 6 on the western side of the island (Table 5). The maximum concentration of mercury was detected in a sample collected from SWMU 7. The maximum concentrations of mercury, selenium, and silver exceeded the ERL by two orders of magnitude. Arsenic and cadmium concentrations exceeded the ERLs by one order of magnitude. The maximum concentration of nickel exceeded the ERL by a factor of seven. The maximum concentrations of copper, lead, and vanadium exceeded the ERLs by a factor of three. The maximum concentrations of zinc exceeded the ERLs by a factor of approximately 1.5. No ERL is available for comparison to the maximum concentration of thallium. |
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