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anaerobic dehalogenation of halogenated organic compounds

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516 Max M. Häggblom et al.<br />

HO<br />

Br<br />

CH 3<br />

Br<br />

OH<br />

HO<br />

CH 3<br />

OH<br />

Br<br />

CH 3<br />

Br<br />

CH 3<br />

Methanogenic<br />

4 Br - Time (Days)<br />

Sulfidogenic<br />

300<br />

300<br />

250<br />

200<br />

200<br />

150<br />

TBBPA<br />

TBBPA<br />

TBBPA (Sterile)<br />

Conc. (µM)<br />

100<br />

50<br />

TBBPA (sterile)<br />

BPA<br />

Conc. (uM)<br />

100<br />

BPA (TBBPA)<br />

0<br />

0 20 40 60 80 100 120<br />

Time (Days)<br />

0<br />

0 20 40 60 80 100 120<br />

Figure 6. Dehalogenation <strong>of</strong> tetrabromobisphenol A in estuarine microcosms under<br />

methanogenic and sulfidogenic conditions (from Voordeckers et al., 2002).<br />

6. CONCLUSIONS<br />

Reductive <strong>dehalogenation</strong> is a promising mechanism for the removal <strong>of</strong><br />

toxic organohalides from estuarine and marine sediments. Anaerobic<br />

<strong>dehalogenation</strong> <strong>of</strong> <strong>halogenated</strong> aromatic contaminants, such as PCDD/Fs and<br />

tetrabromobipshenol A, was readily promoted in estuarine and marine<br />

sediments from several sites. Co-amendment with more soluble <strong>halogenated</strong><br />

<strong>compounds</strong> as “priming” agents greatly speeds PCDD/F dechlorination in<br />

<strong>anaerobic</strong> sediments. This stimulation was brought about in the presence <strong>of</strong><br />

added electron donors lactate and propionate ensuring reduced conditions<br />

and adequate reducing equivalents to stimulate dechlorination. In highly<br />

<strong>organic</strong> sediments with adequate reducing power, it is possible that these<br />

<strong>halogenated</strong> additives may be just as effective without additional electron<br />

donors. While the process has much potential, a key aspect <strong>of</strong> the technology<br />

– the nature and capability <strong>of</strong> the intrinsic microbial community – is <strong>of</strong>ten<br />

unknown. The use <strong>of</strong> molecular tools for monitoring microbial activity<br />

coupled with the understanding <strong>of</strong> how redox processes affect<br />

<strong>dehalogenation</strong> may be used as a rapid screening method for determining<br />

whether a site is a good candidate for bioremediation and to tailor a<br />

bioremediation strategy for that site.

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