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小球藻和斜生栅藻处理系统中磺胺甲噁唑和恩诺沙星的降解及代谢途径。

Degradation and metabolic pathways of sulfamethazine and enrofloxacin in Chlorella vulgaris and Scenedesmus obliquus treatment systems.

机构信息

Key laboratory of Hubei Province for the Protection and Utilization of Special Plant Germplasm in Wuling Mountain Area, College of Life Science, South-Central University for Nationalities, Wuhan, 430074, Hubei, China.

Crean Lutheran High School, Irvine, CA, 92618, USA.

出版信息

Environ Sci Pollut Res Int. 2020 Aug;27(22):28198-28208. doi: 10.1007/s11356-020-09008-4. Epub 2020 May 15.

Abstract

The degradation and metabolic pathways of sulfamethazine (SMZ) and enrofloxacin (ENR) via microalgal treatment systems were investigated in this study. SMZ and ENR applied at 1-25 mg L did not significantly inhibit the growth of Chlorella vulgaris or Scenedesmus obliquus. SMZ and ENR exposure did not significantly alter the maximum quantum efficiencies of C. vulgaris and S. obliquus. When cultured at light intensities of 45-50 μmol photon m s, the C. vulgaris and S. obliquus treatment systems achieved 24% and 11% degradation, respectively. The greatest removal of ENR was 52% and 43.3%, for C. vulgaris and S. obliquus treatment systems, respectively, after 15 days. The results indicated that the degradation of SMZ and ENR occurred by a combination of biodegradation and photolysis. Kinetic investigations revealed that the removal of SMZ and ENR (5 mg L) followed a first-order model, with apparent rate constants (k) ranging from 0.0141 to 0.0048 day and 0.0132 to 0.0086 day, respectively. Fifteen metabolites of SMZ and five intermediates of ENR were identified by UPLC-MS, and degradation pathways for SMZ and ENR were proposed. SMZ transformation reactions included ring cleavage, hydroxylation, methylation, and oxidation, whereas ENR was degraded by dealkylation, decarboxylation, and defluorination. Graphical abstract.

摘要

本研究考察了微藻处理系统中磺胺嘧啶(SMZ)和恩诺沙星(ENR)的降解和代谢途径。1-25 mg/L 的 SMZ 和 ENR 应用并未显著抑制小球藻或斜生栅藻的生长。SMZ 和 ENR 暴露并未显著改变小球藻和斜生栅藻的最大量子效率。当在 45-50 μmol 光子 m s 的光强下培养时,小球藻和斜生栅藻处理系统分别实现了 24%和 11%的降解。在 15 天内,小球藻和斜生栅藻处理系统对 ENR 的最大去除率分别为 52%和 43.3%。结果表明,SMZ 和 ENR 的降解是生物降解和光解的结合。动力学研究表明,SMZ 和 ENR(5 mg/L)的去除遵循一级模型,表观速率常数(k)范围分别为 0.0141 至 0.0048 天和 0.0132 至 0.0086 天。通过 UPLC-MS 鉴定了 15 种 SMZ 代谢物和 5 种 ENR 中间体,并提出了 SMZ 和 ENR 的降解途径。SMZ 的转化反应包括环裂解、羟化、甲基化和氧化,而 ENR 则通过脱烷基、脱羧基和脱氟降解。

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