Munitions
compounds (i.e., 2,4,6-trinitrotoluene (TNT), octahy-dro-1,3,5,7-tetranitro-1,3,5,7-tetrazocin
(HMX), and hexadydro-1,3,5-trinitro-1,3,5-triazin (RDX), also called
energetics) were originally believed to be recalcitrant to microbial
biodegradation based on historical groundwater chemical attenuation
data and laboratory culture work. More recently, it has been established
that natural bacterial assemblages in coastal waters and sediment
can rapidly metabolize these organic nitrogen sources and even incorporate
their carbon and nitrogen into bacterial biomass. Here, we report
on the capacity of natural microbial assemblages in three coastal
North Carolina (United States) estuaries to metabolize energetics
and phenanthrene (PHE), a proxy for terrestrial aromatic compounds.
Microbial assemblages generally had the highest ecosystem capacity
(mass of the compound mineralized per average estuarine residence
time) for HMX (21–5463 kg) > RDX (1.4–5821 kg) ≫
PHE (0.29–660 kg) > TNT (0.25–451 kg). Increasing
antecedent
precipitation tended to decrease the ecosystem capacity to mineralize
TNT in the Newport River Estuary, and PHE and TNT mineralization were
often highest with increasing salinity. There was some evidence from
the New River Estuary that increased N-demand (due to a phytoplankton
bloom) is associated with increased energetic mineralization rates.
Using this type of analysis to determine the ecosystem capacity to
metabolize energetics can explain why these compounds are rarely detected
in seawater and marine sediment, despite the known presence of unexploded
ordnance or recent use in military training exercises. Overall, measuring
the ecosystem capacity may help predict the effects of climate change
(warming and altered precipitation patterns) and other perturbations
on exotic compound fate and transport within ecosystems and provide
critical information for managers and decision-makers to develop management
strategies based on these changes.