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首页> 外文期刊>Environmental Toxicology and Chemistry >EFFECT OF ETHOXYLATE NUMBER AND ALKYL CHAIN LENGTH ON THE PATHWAY AND KINETICS OF LINEAR ALCOHOL ETHOXYLATE BIODEGRADATION IN ACTIVATED SLUDGE
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EFFECT OF ETHOXYLATE NUMBER AND ALKYL CHAIN LENGTH ON THE PATHWAY AND KINETICS OF LINEAR ALCOHOL ETHOXYLATE BIODEGRADATION IN ACTIVATED SLUDGE

机译:活性污泥中乙醇酸乙酯数目和烷基链长对线性乙醇乙醇酸乙酯生物合成途径和动力学的影响

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摘要

Batch activated-sludge die-away studies were conducted with various pure homologs to determine the effect of ethoxylate number and alkyl chain length on the kinetics of primary and ultimate biodegradation of linear alcohol ethoxylates. The 14C-(ethoxylate) homologs C14E1, C14E3, C14E6, and C14E9 were used to investigate the effect of ethoxylate number, and 14C-(ethoxylate) homologs C12E6, C14E6, and C16E6 were used to examine the effect of chain length. Activated sludge was dosed with a trace concentration (0.2 μM) of each homolog, and the disappearance of parent, formation of metabolites, production of 14CO2, and uptake into solids were monitored with time. Ethoxylate number had little effect on the first-order decay rates for primary biodegradation, which ranged from 61 to 78 h−1. However, alkyl chain length had a larger effect, with the C16 chain-length homolog exhibiting a slower rate of parent decay (18 h−1) compared to its corresponding C12 and C14 homologs (61–69 h−1). Ethoxylate number affected the mechanism of biodegradation, with fission of the central ether bond to yield the corresponding fatty alcohol and (poly)ethylene glycol group increasing in dominance with increasing ethoxylate number. Based upon the measured rates of primary biodegradation, removal of parent during activated-sludge treatment was predicted to range between 99.7 and 99.8% for all homologs except C16E6, which had a predicted removal of 98.9%. Based upon the measured rates of ultimate biodegradation, removal of ethoxylate-containing metabolites was predicted to exceed 83% for all homologs. These predictions corresponded closely with previously published removal measurements in laboratory continuous activated-sludge systems and actual treatment plants.
机译:用各种纯同系物进行了批量活性污泥死去研究,以确定乙氧基化物数量和烷基链长对线性醇乙氧基化物的初次和最终生物降解动力学的影响。使用14C-(乙氧基化物)同系物C14E1,C14E3,C14E6和C14E9来研究乙氧基化物数的影响,并使用14C-(乙氧基化物)同系物C12E6,C14E6和C16E6来检查链长的影响。向活性污泥中加入痕量浓度的每种同系物(0.2μM),并随时间监测母体的消失,代谢产物的形成,14CO2的产生以及对固体的吸收。乙氧基化数对一级生物降解的一级衰减率影响很小,范围从61到78 h-1。但是,烷基链长的影响更大,与相应的C12和C14同系物(61–69 h-1)相比,C16链长同系物的母体衰变速率(18 h-1)慢。乙氧基化物数目影响生物降解的机理,中心醚键的裂变产生相应的脂肪醇和(聚)乙二醇基团,随着乙氧基化物数目的增加而占主导地位。根据测得的主要生物降解速率,除C16E6预计清除率为98.9%以外,所有同系物在活性污泥处理过程中的亲本清除率预计在99.7%至99.8%之间。根据测得的最终生物降解速率,所有同系物的含乙氧基化物代谢物的去除率预计超过83%。这些预测与实验室连续活性污泥系统和实际处理厂中先前发表的去除量测量结果非常一致。

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