Attenuation mechanisms of N-nitrosodimethylamine at an operating intercept and treat groundwater remediation system.
The North Boundary Containment System (NBCS), an intercept-and-treat system, was established at Rocky Mountain Arsenal (RMA), Commerce City, CO, to remove low-level organic contaminants from a groundwater plume exiting RMA to the north and northwest. N-nitrosodimethylamine (NDMA) was detected in groundwater collected from the dewatering and recharge zones of the NBCS system. Concern over the fate of NDMA, in terms of potentially exiting the boundaries of the arsenal, prompted an investigation to evaluate potential attenuation mechanisms for NDMA within the alluvial aquifer system and within the NBCS itself. Groundwater, soil, and granular activated carbon (GAC) samples were taken from key locations in the NBCS system. Soil and GAC samples were assayed for sorption kinetics and for adsorption and desorption properties using 14C-labeled NDMA. NDMA biodegradation experiments were conducted by following 14CO(2) evolution from 14C-labeled NDMA in soils and GAC samples under aerobic and anaerobic conditions. The sorptive capacity of the site soils for NDMA was insignificant. Furthermore, the adsorption of the NDMA by the soil was almost completely reversible. Evaluation of the degradation potential of the native microbial consortia indicated a high level of NDMA mineralization when measured using bench-scale microcosms. The native consortia had capability to mineralize the NDMA under both aerobic and anaerobic incubations, indicating facultative characteristics. Testing of the local groundwater chemistry revealed that the area of the aquifer of interest was microaerobic and neutral in pH. These conditions were optimal for NDMA removal. While sorption was insignificant, degradation was a significant attenuation mechanism, which may be the reason that no NDMA has migrated off-site. This gives rise to the potential of a long-term sink for attenuating NDMA within the recharge zone of the treatment system.
Gunnison
D
D
Environmental Laboratory, US Army Environmental Research and Development Center at Waterways Experiment Station, Vicksburg, MS, USA.
Zappi
M E
ME
Teeter
C
C
Pennington
J C
JC
Bajpai
R
R
D000327:Adsorption; D000332:Aerobiosis; D000693:Anaerobiosis; D001673:Biodegradation, Environmental; D002245:Carbon Dioxide / Q000737:chemistry; D002250:Carbon Radioisotopes / Q000737:chemistry; D002606:Charcoal; D003120:Colorado; D004128:Dimethylnitrosamine / Q000032:analysis* / Q000737:chemistry; D004787:Environmental Pollution / Q000517:prevention & control*; D015386:Hazardous Substances / Q000032:analysis*; D006801:Humans; D006863:Hydrogen-Ion Concentration; D007220:Industrial Waste / Q000517:prevention & control; D019275:Radiopharmaceuticals / Q000737:chemistry; D012987:Soil / Q000032:analysis; D012988:Soil Microbiology; D012989:Soil Pollutants / Q000032:analysis*; D014867:Water / Q000032:analysis; D014874:Water Pollutants, Chemical / Q000032:analysis*; D014877:Water Pollution, Chemical / Q000517:prevention & control*
D002250:Carbon Radioisotopes; D015386:Hazardous Substances; D007220:Industrial Waste; D019275:Radiopharmaceuticals; D012987:Soil; D012989:Soil Pollutants; D014874:Water Pollutants, Chemical; D014867:Water; D002245:Carbon Dioxide; D002606:Charcoal; D004128:Dimethylnitrosamine