A successful anaerobic bioaugmentation was carried out
on a trichloroethene (TCE)-contaminated aquifer at
Dover Air Force Base, DE, using a microbial enrichment
culture capable of dechlorinating TCE to ethene. A
hydraulically controlled pilot system 12 × 18 m was
constructed 15 m below ground surface in an alluvial
aquifer to introduce nutrients and substrate into the
groundwater. Ambient TCE and cis-1,2-dichloroethene
(cDCE) concentrations in groundwater averaged 4800 and
1200 μg/L. The pilot operated for 568 days. Results by
day 269 confirmed previous laboratory work showing that
dechlorination did not proceed past cDCE. By this time,
most of the TCE was dechlorinated to cDCE, and cDCE was
the predominant contaminant. An ethene-forming microbial
enrichment culture from the Department of Energy's
Pinellas site in Largo, FL, was injected into the pilot area.
After a lag period of about 90 days, vinyl chloride and
ethene began to appear in wells. The injected culture
survived and was transported through the pilot area. By day
509, TCE and cDCE were fully converted to ethene.
A variety of microbial dechlorination mechanisms have been demonstrated in laboratory microcosms, pure cultures, and in situ sedimentary environments. New perspectives on in situ processes from these efforts allow the design of more realistic bioremediation strategies that complement natural processes regardless of whether the strategy used is one of engineered accelerated bioremediation or natural attenuation. Since 1994 the scientific community has acquired considerable knowledge regarding natural attenuation of organochlorine compounds. Natural attenuation of chlorinated solvents has been documented at a number of field sites. Reductive dechlorination driven by co-contaminants or naturally occurring organics as substrates in combination with aerobic or co-metabolic degradation contains certain chlorinated solvent plumes. Although natural attenuation is not a panacea, at sites where it is applicable, it offers a scientifically sound, cost-effective method to remediate groundwater contaminated with chlorinated solvents.
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