posted on 2021-04-26, 18:39authored byYiran Tong, Matthew J. Berens, Bridget A. Ulrich, Jakov Bolotin, Jennifer H. Strehlau, Thomas B. Hofstetter, William A. Arnold
Subsurface contamination with the
explosive hexahydro-1,3,5-trinitro-1,3,5-triazine
(RDX) at ordnance production and testing sites is a problem because
of the persistence, mobility, and toxicity of RDX and the formation
of toxic products under anoxic conditions. While the utility of compound-specific
isotope analysis for inferring natural attenuation pathways from stable
isotope ratios has been demonstrated, the stable isotope fractionation
for RDX reduction by iron-bearing minerals remains unknown. Here,
we evaluated N and C isotope fractionation of RDX during reduction
by Fe(II) associated with Fe minerals and natural sediments and applied
N isotope ratios to the assessment of mineral-catalyzed RDX reduction
in a contaminant plume and in sediment columns treated by in situ chemical reduction. Laboratory studies revealed
that RDX was reduced to nitroso compounds without denitration and
the concomitant ring cleavage. Fe(II)/iron oxide mineral-catalyzed
reactions exhibited N isotope enrichment factors, εN, between −6.3±0.3‰ and −8.2±0.2‰,
corresponding to an apparent 15N kinetic isotope effect
of 1.04–1.05. The observed variations of the δ15N of ∼15‰ in RDX from groundwater samples suggested
an extent of reductive transformation of 85% at an ammunition plant.
Conversely, we observed masking of N isotope fractionation after RDX
reduction in laboratory flow-through systems, which was presumably
due to limited accessibility to reactive Fe(II).