ABSTRACT:
Landfill-stimulated iron reduction and arsenic release
at the Coakley superfund site (NH)
Arsenic is a contaminant
at more than one-third of all Superfund Sites in the United
States. Frequently this contamination appears to result from
geochemical processes rather than the
presence of a well-defined arsenic source. Here we examine
the geochemical processes that regulate arsenic
levels at the Coakley Landfill Superfund Site
(NH), a site contaminated with As, Cr, Pb, Ni, Zn, and aromatic
hydrocarbons. Long-term field observations indicate
that the concentrations of most of these contaminants have
diminished as a result of treatment by monitored natural
attenuation begun in 1998; however, dissolved arsenic levels
increased modestly over the same interval. We attribute this
increase to the reductive release of arsenic associated
with poorly crystalline iron hydroxides within a glaciomarine
clay layer within the overburden underlying
the former landfill. Anaerobic batch incubations that stimulated
iron reduction in the glaciomarine clay released appreciable
dissolved arsenic and iron. Field observations
also suggest that iron reduction associated with biodegradation
of organic waste are partly responsible for arsenic release;
over the five-year study period since a cap was emplaced
to prevent water flow through the site, decreases in groundwater
dissolved benzene concentrations at the landfill are correlated
with increases in dissolved arsenic concentrations, consistent
with the microbial decomposition of both benzene and other
organics, and reduction of arsenic-bearing iron oxides. Treatment
of contaminated groundwater increasingly is based on stimulating
natural biogeochemical processes to degrade the contaminants.
These results indicate that reducing environments created
within organic contaminant plumes may release arsenic. In
fact, the strong correlation (>80%) between elevated arsenic levels and organic contamination
in groundwater systems at Superfund Sites across the United
States suggests that arsenic contamination caused by natural
degradation of organic contaminants may be widespread.