Gj. Wilson et al., Anaerobic/aerobic biodegradation of pentachlorophenol using GAC fluidized bed reactors: Optimization of the empty bed contact time, WATER SCI T, 38(7), 1998, pp. 9-17
An integrated reactor system has been developed to remediate pentachlorophe
nol (PCP) containing wastes using sequential anaerobic and aerobic biodegra
dation. Anaerobically, PCP was degraded to approximately equimolar concentr
ations (>99%) of chlorophenol (CP) in a granular activated carbon (GAC) flu
idized bed reactor (FBR) at empty bed contact times (EBCTs) ranging from 18
.6 to 2.3 hr. However, at lower EBCTs, chlorophenol concentrations decrease
d to less than 10% of the influent PCP concentration. The optimal EBCT was
determined to be 2.3 hr based on PCP conversion to CPs and stable reactor o
peration. Decreasing the EBCT fourfold did not inhibit degradation of PCP a
nd its intermediates, and thus, removal of PCP is possible at lower detenti
on times providing a significant cost advantage.
Analytical grade PCP was fed via syringe pumps into a GAC FBR at an influen
t concentration of 200 mg/L. Acting as the primary substrate, ethanol was a
lso fed at a concentration of 1388 mg/L. Effluent PCP and chlorinated pheno
lic compounds were analyzed weekly to evaluate reactor performance. Biodegr
adation pathways were also identified. 3-chlorophenol (3-CP) was the predom
inant CP. Concentrations of 3-CP follow the same trends as 3,5-dichlorophen
ol (DCP) concentrations. In a similar manner, 4-chlorophenol concentrations
correlate with 3,4-DCP concentrations.
A second stage aerobic GAC FBR was added after the anaerobic bioreactor whi
ch removed the remaining CP and phenols. No phenol or CP has been observed
in the effluent or on the GAG. Overall, the influent chemical oxygen demand
(COD) loading was reduced from 34 g/L*d to less than 1.36 g/L*d. (C) 1998
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