Methyl tertiary-butyl ether (MTBE) biodegradation in batch and continuous upflow fixed biofilm reactors

被引:25
作者
Acuna-Askar, K
Englande, AJ
Hu, C
Jin, G
机构
[1] Univ Autonoma Nuevo Leon, Fac Med, Dept Quim Analit, Monterrey, Nuevo Leon, Mexico
[2] Tulane Univ, Med Ctr, Sch Publ Hlth & Trop Med, Dept Environm Hlth Sci, New Orleans, LA 70112 USA
[3] Illinois State Univ, Coll Appl Sci & Technol, Dept Hlth Sci, Normal, IL 61790 USA
关键词
biodegradation; methyl tert-butyl ether; petrochemical activated sludge; kinetic rate constant; fixed film bioreactor;
D O I
10.2166/wst.2000.0509
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
MTBE was effectively biodegraded under oxidizing environmental conditions in the presence of an acclimated mixed culture isolated from a petrochemical biotreater. MC-1 (Gram-positive coccus), MC-2 (Acinetobacter Iwoffii) and MC-3 (Bacillus sp.) were present in the culture medium, with MC-1 being the predominant organism. The presence of other easily assimilated carbon sources in the culture medium influenced MTBE biodegradation. In batch studies, 62-73% MTBE was biodegraded in 144-192 hours at an initial concentration of 100 ppm as the sole carbon source, with the ORP ranging from 191-274 my, and at a temperature of 29 degreesC. The overall K rate constants and the specific k rate constants were evaluated using a first or der rate equation. Mean values determined were 1.79x10(-1) day(-1) and 1.66x10(-2) day(-1)/(mg/L cell mass), respectively. Continuous upflow fixed biofilm reactor studies were performed at retention times of 0.25, 0.5, and 1 day at an initial MTBE concentration of 150 ppm. Results indicated that approximately 53% MTBE was biodegraded for the 0.25 day retention time and 70% for both the 0.5 and 1.0 day retention times. Three kinetic models were evaluated for all experimental retention times. These included: Model I (Eckenfelder); Model II (Arvin) and Model III (first-order biphasic). Results indicated that model III yielded the highest and most consistent correlation coefficients for all retention times evaluated.
引用
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页码:153 / 161
页数:9
相关论文
共 19 条
[1]  
[Anonymous], 1998, STAND METH EX WAT WA, V20th
[2]   BIODEGRADATION KINETICS OF CHLORINATED ALIPHATIC-HYDROCARBONS WITH METHANE OXIDIZING BACTERIA IN AN AEROBIC FIXED BIOFILM REACTOR [J].
ARVIN, E .
WATER RESEARCH, 1991, 25 (07) :873-881
[3]  
*ATSDR, 1995, TOX PROF METH ETH
[4]   UTILIZATION RATES OF TRACE HALOGENATED ORGANIC-COMPOUNDS IN ACETATE-GROWN BIOFILMS [J].
BOUWER, EJ ;
MCCARTY, PL .
BIOTECHNOLOGY AND BIOENGINEERING, 1985, 27 (11) :1564-1571
[5]   SUBSTRATE DIVERSITY AND EXPRESSION OF THE 2,4,5-TRICHLOROPHENOXYACETIC ACID OXYGENASE FROM BURKHOLDERIA CEPACIN AC1100 [J].
DANGANAN, CE ;
SHANKAR, S ;
YE, RW ;
CHAKRABARTY, AM .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1995, 61 (12) :4500-4504
[6]   THE EFFECT OF OXIDATION-REDUCTION POTENTIAL ON THE BIOTRANSFORMATIONS OF CHLORINATED HYDROCARBONS [J].
DOONG, RA ;
WU, SC .
WATER SCIENCE AND TECHNOLOGY, 1992, 26 (1-2) :159-168
[7]  
Eckenfelder W., 1989, IND WATER POLLUTION
[8]   Studies on the dechlorination of tetrachloroethene to cis-1,2-dichloroethene by Dehalospirillum multivorans in biofilms [J].
Eisenbeis, M ;
BauerKreisel, P ;
ScholzMuramatsu, H .
WATER SCIENCE AND TECHNOLOGY, 1997, 36 (01) :191-198
[9]   Health risk assessment of groundwater contaminated with methyl tertiary butyl ether (MTBE) [J].
Hartley, WR ;
Englande, AJ ;
Harrington, DJ .
WATER SCIENCE AND TECHNOLOGY, 1999, 39 (10-11) :305-310
[10]   Redox potential as a controlling factor in enhancing carbon tetrachloride biodegradation [J].
Jin, G ;
Englande, AJ .
WATER SCIENCE AND TECHNOLOGY, 1996, 34 (10) :59-66