Akademik Veri Yönetim Sistemi
JOURNAL OF ENVIRONMENTAL MANAGEMENT, cilt.83, sa.4, ss.427-436, 2007 (SCI-Expanded)
This paper investigated the biodegradation kinetics of 4-chlorophenol (4-CP) and 2,4-dichlorophenol (2,4-DCP) separately in batch reactors and mixed in sequencing batch reactors (SBRs). Batch reactor experiments showed that both 4-CP and 2,4-DCP began to inhibit their own degradation at 53 and 25 mgl(-1), respectively, and that the Haldane equation gave a good fit to the experimental data because r(2) values were higher than 0.98. The maximum specific degradation rates (q(m)) were 130.3 and 112.4 mg g(-1) h for 4-CP and 2,4-DCP, respectively. The values of the half saturation (K-s) and self-inhibition constants (K-i) were 34.98 and 79.74 mgl(-1) for 4-CP, and 13.77 and 44.46 mgl(-1) for 2,4-DCP, respectively. The SBR was fed with a mixture of 220 mgl(-1) of 4-CP, 110 mgl(-1) of 2,4-DCP, and 300 mgl(-1) of peptone as biogenic substrate at varying feeding periods (0-8 h) to evaluate the effect of feeding time on the performance of the SBR. During SBR operation, in addition to self-inhibition, 4-CP degradation was strongly and competitively inhibited by 2,4-DCP. The inhibitory effects were particularly pronounced during short feeding periods because of higher chlorophenol peak concentrations in the reactor. The competitive inhibition constant (K-ii) of 2,4-DCP on 4-CP degradation was 0.17 mgl(-1) when the reactor was fed instantaneously (0 h feeding). During longer feedings, increased removal/loading rates led to lower chlorophenol peak concentrations at the end of feeding. Therefore, in multi-substrate systems feeding time plus reaction time should be determined based on both degradation kinetics and substrate interaction. During degradation, the meta cleavage of 4-chlorocatechol resulted in accumulation of a yellowish color because of the formation of 5-chloro-2-hydroxymuconic semialdehyde (CHMS), which was further metabolized. Isolation and enrichment of the chlorophenols-degrading culture suggested Pseudomonas sp. and Pseudomonas stutzeri to be the dominant species. (C) 2006 Elsevier Ltd. All rights reserved.