posted on 2016-01-19, 00:00authored byJames R. Degnan, J. K. Böhlke, Krystle Pelham, David M. Langlais, Gregory J. Walsh
Explosives
used in construction have been implicated as sources
of NO3– contamination in groundwater,
but direct forensic evidence is limited. Identification of blasting-related
NO3– can be complicated by other NO3– sources, including agriculture and wastewater
disposal, and by hydrogeologic factors affecting NO3– transport and stability. Here we describe a study
that used hydrogeology, chemistry, stable isotopes, and mass balance
calculations to evaluate groundwater NO3– sources and transport in areas surrounding a highway construction
site with documented blasting in New Hampshire. Results indicate various
groundwater responses to contamination: (1) rapid breakthrough and
flushing of synthetic NO3– (low δ15N, high δ18O) from dissolution of unexploded
NH4NO3 blasting agents in oxic groundwater;
(2) delayed and reduced breakthrough of synthetic NO3– subjected to partial denitrification (high δ15N, high δ18O); (3) relatively persistent
concentrations of blasting-related biogenic NO3– derived from nitrification of NH4+ (low δ15N, low δ18O); and (4) stable but spatially
variable biogenic NO3– concentrations,
consistent with recharge from septic systems (high δ15N, low δ18O), variably affected by denitrification.
Source characteristics of denitrified samples were reconstructed from
dissolved-gas data (Ar, N2) and isotopic fractionation
trends associated with denitrification (Δδ15N/Δδ18O ≈ 1.31). Methods and data from
this study are expected to be applicable in studies of other aquifers
affected by explosives used in construction.