Open AccessAnaerobic treatment of 2,4,6‐trichlorophenol in an expanded granular sludge bed‐anaerobic filter (EGSB‐AF) bioreactor at 15 °C
Author(s) -
Collins Gavin,
Foy Clare,
McHugh Sharon,
O’ Flaherty Vincent
Publication year - 2005
Publication title -
fems microbiology ecology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.377
H-Index - 155
eISSN - 1574-6941
pISSN - 0168-6496
DOI - 10.1016/j.femsec.2004.10.008
Subject(s) - bioreactor , anaerobic exercise , biology , anaerobic filter , microbial population biology , anaerobic digestion , biodegradation , pulp and paper industry , microbiology and biotechnology , food science , bacteria , botany , methane , ecology , physiology , genetics , engineering
Expanded granular sludge bed‐anaerobic filter (EGSB‐AF) bioreactors were operated at 15 °C for the treatment of 2,4,6‐trichlorophenol (TCP)‐containing volatile fatty acid (VFA)‐based wastewaters. The seed sludge used as inoculum for the control (no TCP) and test reactor was unexposed to chlorophenols (CPs) prior to the 425‐day trial. TCP supplementation to the feed at 50 mgCPl −1 partially inhibited the anaerobic degradation of the VFA feed measured as COD removal efficiency. However, the withdrawal and subsequent application of stepwise increments to the TCP loading resulted in steady COD removal. Terminal restriction fragment length polymorphism analysis showed Methanosaeta ‐like Archaea in the control reactor over the experimental period. Different methanogenic populations were detected in the test reactor and responded to the changes in feed composition. Bacterial community analyses indicated changes in the community structure over time and suggested the presence of Campylobacter ‐like, Acidimicrobium ‐like and Heliophilum ‐like organisms in the samples. TCP mineralisation was by a reductive dechlorination pathway through 2,4‐dichlorophenol (DCP) and 4‐chlorophenol (4‐CP) or 2‐chlorophenol (2‐CP). CP degradation rates in sludge granules from the lower chamber of the hybrid EGSB‐AF reactor was in the order TCP > DCP > 4‐CP > 2‐CP. However, a biodegradability order of lower CPs > TCP was observed in fixed‐film biomass taken from the upper reactor chamber, thus reflecting the role of this reactor section in the metabolism of residual lower CPs from the lower sludge‐bed stage of operation.