Chlorinated electron acceptor availability selects for specificDehalococcoidespopulations in dechlorinating enrichment cultures and in groundwater
AbstractIndividualDehalococcoides mccartyi (Dhc)strains differ primarily from one another by the number and identity of the reductive dehalogenase homologous catalytic subunit A (rdhA) genes contained within their respective genomes. While thousands ofrdhAgenes have been sequenced, the activity of the corresponding proteins have been identified in only a handful of cases. Most effort has focused on identifying the enzymes that dechlorinate substrates including trichloroethene (TCE), cis-dichloroethene (cDCE) and vinyl chloride (VC) relevant to groundwater remediation. The associatedrdhAgenes, namelytceA, bvcA,andvcrA, along with theD. mccartyi16S rRNA gene are often used to track growth and dechlorinating activity in DNA extracted from field samples. In this study, we augmented the typical suite of three characterizedrdhAgenes to include an additional 12 uncharacterizedrdhAsequences identified in the metagenome in the mixedDhc-containing culture KB-1 to track population shifts within the culture and at two bioaugmented field sites. Quantitative PCR assays were developed for the 15 selectedD. mccartyi rdhAgenes and evaluated using 11 different sub-cultures of KB-1, each enriched on different chlorinated ethenes and ethanes. The proportion ofrdhAgene copies relative toDhc16S gene copies indicated the presence of multiple distinctDhcpopulations in each culture. The specific electron acceptor amended to each culture had a major influence on the distribution ofD. mccartyipopulations and their associatedrdhAgenes. We also surveyed the abundance ofrdhAgenes in samples obtained from two bioaugmented field sites. Growth of the dominantD. mccartyipopulation in the KB-1 inoculum was detected in the UK site samples. At both field sites, the measurement of relativerdhAabundances revaled significantD. mccartyipopulation shifts over time as dechlorination progressed from TCE through cDCE to VC and ethene, indicating that the selective pressure of the most abundant chlorinated electron acceptor that was observed in lab cultures was also occurring in the populations in the field. Understanding driving forces behindD. mccartyipopulation selection and activity is improving predictability of remediation performance at chlorinated solvent contaminated sites.