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Acute toxicity and relationship between metabolites and ecotoxicity during the biodegradation process of non-ionic surfactants: fatty-alcohol ethoxylates, nonylphenol polyethoxylate and alkylpolyglucosides

机译:非离子表面活性剂生物降解过程中的急性毒性以及代谢产物与生态毒性之间的关系:脂肪醇乙氧基化物,壬基酚聚乙氧基化物和烷基多糖苷

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The toxicity values of fatty-alcohol ethoxylates, nonylphenol polyethoxylate, and alkylpolyglucosides have been determined by applying assays with luminescent bacteria. Also, the relation between metabolites and ecotoxicity during the biodegradation process has been determined. The biodegradation tests were carried out according to the OECD 301 E test for ready biodegradability. In these tests a solution of the surfactant, representing the sole carbon source for the microorganisms, was tested in a mineral medium, inoculated and incubated under aerobic conditions in the dark. The toxicity of surfactants is related to their molecular structure (Quantitative Structure Activity Relationships, QSAR). For the alkylpolyglucosides, toxicity expressed as EC50 is related with the critical micelle concentration (CMC), the hydrophiliclipophilic balance (HLB) of the surfactant, and the hydrophobic alkyl chain (R). The results indicate that toxicity increased as the CMC decreased and as the hydrophobicity increased and R rose. For fatty-alcohol ethoxylates, parameters characteristic studied have been HLB, number of units of ethylene oxide and the alkyl chain length. Relationships found are in agreement with the fact that increasing the alkyl chain length leads to a lower EC50, whereas increasing ethoxylation leads to a lower toxicity. An analysis of the behaviour of the toxicity and HLB again indicates that the toxicity was greater for surfactants with a smaller HLB. The evolution of the toxicity was studied over the biodegradation process, expressed as a percentage of inhibition. For all the nonionic surfactants assayed, except for the nonylphenol polyethoxylate, a major decline was found in toxicity during the first days of the biodegradation assay and at all the concentrations tested.
机译:脂肪醇乙氧基化物,壬基酚聚乙氧基化物和烷基聚葡萄糖苷的毒性值已通过使用发光细菌进行测定来确定。此外,已经确定了生物降解过程中代谢物与生态毒性之间的关系。根据OECD 301 E测试进行了生物降解测试,以确保具有良好的生物降解能力。在这些测试中,代表矿物唯一碳源的表面活性剂溶液在矿物培养基中进行测试,接种后在黑暗中于有氧条件下孵育。表面活性剂的毒性与它们的分子结构(定量结构活性关系,QSAR)有关。对于烷基多糖苷,以EC50表示的毒性与临界胶束浓度(CMC),表面活性剂的亲水亲脂平衡(HLB)和疏水性烷基链(R)有关。结果表明,毒性随着CMC的降低,疏水性的增加和R的增加而增加。对于脂肪醇乙氧基化物,研究的参数特征是HLB,环氧乙烷的单元数和烷基链长。发现的关系与增加烷基链长度导致较低的EC 50,而增加乙氧基化导致较低的毒性这一事实是一致的。毒性和HLB行为的分析再次表明,HLB较小的表面活性剂的毒性更大。研究了在生物降解过程中毒性的演变,用抑制百分比表示。对于所有测定的非离子表面活性剂,除了壬基酚聚乙氧基化物以外,在生物降解测定的第一天和所有测试浓度下,毒性均出现了大幅下降。

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