McRae Bethany M, LaPara Timothy M, Hozalski Raymond M
Department of Civil Engineering, University of Minnesota, 122 Civil Engineering Building, 500 Pillsbury Drive SE, Minneapolis, MN 55455, USA.
Chemosphere. 2004 May;55(6):915-25. doi: 10.1016/j.chemosphere.2003.11.048.
Haloacetic acids (HAAs) are toxic organic chemicals that are frequently detected in surface waters and in drinking water distribution systems. The aerobic biodegradation of HAAs was investigated in serum bottles containing a single HAA and inoculated with washed microorganisms obtained from enrichment cultures maintained on either monochloroacetic acid (MCAA) or trichloroacetic acid (TCAA) as the sole carbon and energy source. Biodegradation was observed for each of the HAAs tested at concentrations similar to those found in surface waters and in drinking water distribution systems. The MCAA culture was able to degrade both MCAA and monobromoacetic acid (MBAA) with pseudo-first order rate constants of 1.06 x 10(-2) and 1.13 x 10(-2) l(mg protein)(-1) d(-1), respectively, for concentrations ranging from 10(-5) to 2 mM. The pseudo-first order rate constant for TCAA degradation by the TCAA culture was 6.52 x 10(-3) l(mg protein)(-1) d(-1) for concentrations ranging from 5.33 x 10(-5) to 0.72 mM. The TCAA culture was also able to degrade MCAA with the rate accelerating as incubation time increased. Experiments with radiolabeled HAAs indicated that the 14C was primarily converted to 14CO2 with minor incorporation into cell biomass. The community structure of the enrichment cultures was analyzed by both cultivation-dependent and cultivation-independent approaches. Denaturing gradient gel electrophoresis (DGGE) of the PCR-amplified 16S rRNA gene fragments showed that each of the two enrichment cultures had multiple bacterial populations, none of which corresponded to HAA-degrading bacteria cultivated on HAA-supplemented agar plates. This research indicates that biodegradation is a potential loss mechanism for HAAs in surface waters and in drinking water distribution systems.
卤乙酸(HAAs)是有毒有机化学品,常在地表水和饮用水分配系统中被检测到。在含有单一卤乙酸的血清瓶中研究了卤乙酸的好氧生物降解,接种的是从以一氯乙酸(MCAA)或三氯乙酸(TCAA)作为唯一碳源和能源维持的富集培养物中获得的经洗涤的微生物。在与地表水和饮用水分配系统中发现的浓度相似的情况下,对所测试的每种卤乙酸都观察到了生物降解。MCAA培养物能够降解MCAA和一溴乙酸(MBAA),对于浓度范围为10^(-5)至2 mM的情况,其假一级速率常数分别为1.06×10^(-2)和1.13×10^(-2) l(mg蛋白质)^(-1) d^(-1)。对于浓度范围为5.33×10^(-5)至0.72 mM的情况,TCAA培养物对TCAA降解的假一级速率常数为6.52×10^(-3) l(mg蛋白质)^(-1) d^(-1)。TCAA培养物也能够降解MCAA,且随着培养时间增加速率加快。用放射性标记的卤乙酸进行的实验表明,^14C主要转化为^14CO2,少量掺入细胞生物质中。通过依赖培养和不依赖培养的方法分析了富集培养物的群落结构。对PCR扩增的16S rRNA基因片段进行变性梯度凝胶电泳(DGGE)表明,两种富集培养物中的每一种都有多个细菌种群,其中没有一个与在添加卤乙酸的琼脂平板上培养的卤乙酸降解细菌相对应。这项研究表明,生物降解是地表水和饮用水分配系统中卤乙酸潜在的损失机制。