PRELIMINARY CONCEPTUAL MODEL FOR ARSENIC OCCURRENCE AND TRANSPORT IN GROUND WATER, SURFACE WATER AND POND-BOTTOM SEDIMENTS, RED COVE, PLOW SHOP POND, CENTRAL MASSACHUSETTS
Arsenic is naturally occurring in local soils and bedrock and is associated with iron in oxide and sulfide minerals. Previous work (Stein, et al., 2004) indicates that ground water oxidation-reduction potential (ORP) exerts considerable control on arsenic mobility, primarily through 1) precipitation of hydrous ferric oxides (HFO) and sorption of arsenic, 2) reductive dissolution of HFO and arsenic release, and 3) formation of iron and/or arsenic sulfide phases. Low ORP in the vicinity of SHL gives rise to elevated dissolved iron and arsenic concentrations. Ground water flow data from monitoring wells indicate consistent head-field gradients focused toward Red Cove. Reducing ground water, discharging to the cove from the direction of the landfill, encounters a redox boundary below the sediment-water interface, where arsenic is precipitated along with HFO and possibly sulfides in the sediments. However, arsenic is generally nondetect in surface water. A redox interface was observed at several locations at or near the cove at 1 to 2 m below the sediment surface. Preliminary estimates suggest that several Kg of arsenic are transported to Red Cove annually by these processes, and toxicity data indicate impairment. Remedial measures, if needed, must consider the geochemical and hydrologic dynamics of ground water-surface water interactions.