posted on 2016-11-04, 00:00authored byKai Ding, Wenqing Xu
1,1-trichloro-2,2-di(4-chlorophenyl)ethane
(DDT) and its metabolites
1,1-dichloro-2,2-bis(4-chlorophenyl)ethane (DDD) and 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene
(DDE), are often detected in soils and sediments containing high concentrations
of black carbon. Sulfide (∼5 mM) from biological sulfate reduction
often coexists with black carbon and serves as both a strong reductant
and a nucleophile for the abiotic transformation of contaminants.
In this study, we found that the abiotic transformation of DDT, DDD,
and DDE (collectively referred to as DDX) require both sulfide and
black carbon. 89.3 ± 1.8% of DDT, 63.2 ± 1.9% of DDD, and
50.9 ± 1.6% of DDE were degraded by sulfide (5 mM) in the presence
of graphite powder (21 g/L) after 28 days at pH 7. Chloride was a
product of DDX degradation. To better understand the reaction pathways,
electrochemical cells and batch reactor experiments with sulfide-pretreated
graphite powder were used to differentiate the involvement of black
carbon materials in DDX transformation by sulfide. Our results suggest
that DDT and DDD are transformed by surface intermediates formed from
the reaction between sulfide and black carbon, while DDE degradation
involves reductive dechlorination. This research lays the groundwork
for developing an alternative in situ remediation technique for rapidly
decontaminating soils and sediments to lower toxic products under
environmentally relevant conditions.