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过渡金属螯合剂乙二胺二琥珀酸(EDDS)的[S,S]、[R,R]和混合立体异构体的生物降解作用

Biodegradation of [S,S], [R,R] and mixed stereoisomers of ethylene diamine disuccinic acid (EDDS), a transition metal chelator.

作者信息

Schowanek D, Feijtel T C, Perkins C M, Hartman F A, Federle T W, Larson R J

机构信息

Procter & Gamble European Technical Center, Strombeek-Bever, Belgium.

出版信息

Chemosphere. 1997 Jun;34(11):2375-91. doi: 10.1016/s0045-6535(97)00082-9.

Abstract

An in-depth biodegradation test program was executed on the hexadentate ligand Ethylene Diamine Di Succinate (EDDS). The EDDS structure contains two chiral carbon atoms, and has three stereoisomers ([R,R], [R,S]/[S,R], [S,S]). Our research has focused on the isomer mixture (i.e. 25%[S,S]; 25%[R,R]; 50%[S,R]/[R,S], as produced from the reaction of ethylene diamine with maleic anhydride) and on the single [S,S]- and [R,R]-isomers. Biodegradation screening of the 14C-labelled EDDS isomer mixture in a Batch Activated Sludge (BAS) test with various inocula revealed incomplete mineralization, up to ca. 65% after 28 days. N-(2-aminoethyl) aspartic acid (AEAA), probably the d-isomer, was identified as the major portion of the 14C-material remaining in solution. Further testing revealed that the [S,S]-isomer is rapidly and completely mineralized in all test systems. By contrast, [R,R]-EDDS remained undegraded in a Sturm (OECD 301B) test, but was very slowly biotransformed into the recalcitrant metabolite AEAA in a BAS test. The [S,R]/[R,S] form undergoes biotransformation to AEAA in both high and low biomass systems. In a sewage treatment simulation test (OECD 303) the steady state DOC removal of mixture-EDDS in a CAS test was limited to 25-35%, even after extensive pre-acclimation, while the [S,S]-isomer achieved nearly complete removal (96%). This study illustrates the importance stereospecificity may have on the biodegradation and metabolite formation of a chemical. A biodegradation scheme for the different EDDS stereoisomers is proposed.

摘要

针对六齿配体乙二胺二琥珀酸(EDDS)开展了一项深入的生物降解测试项目。EDDS结构包含两个手性碳原子,有三种立体异构体([R,R]、[R,S]/[S,R]、[S,S])。我们的研究聚焦于异构体混合物(即由乙二胺与马来酸酐反应生成的,含25%[S,S];25%[R,R];50%[S,R]/[R,S])以及单一的[S,S]-和[R,R]-异构体。在批次活性污泥(BAS)测试中,使用各种接种物对14C标记的EDDS异构体混合物进行生物降解筛选,结果显示矿化不完全,28天后最高可达约65%。N-(2-氨基乙基)天冬氨酸(AEAA),可能是d-异构体,被确定为溶液中剩余14C物质的主要成分。进一步测试表明,[S,S]-异构体在所有测试系统中都能快速且完全矿化。相比之下,[R,R]-EDDS在斯特姆(经合组织301B)测试中未降解,但在BAS测试中非常缓慢地生物转化为难降解代谢物AEAA。[S,R]/[R,S]形式在高生物量和低生物量系统中都会生物转化为AEAA。在污水处理模拟测试(经合组织303)中,即使经过广泛的预驯化,在连续流活性污泥(CAS)测试中混合物-EDDS的稳态溶解性有机碳去除率也限制在25-35%,而[S,S]-异构体几乎实现了完全去除(96%)。本研究说明了立体特异性对化学品生物降解和代谢物形成可能具有的重要性。提出了不同EDDS立体异构体的生物降解方案。

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