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环烷酸的选择性生物降解及混合物特征与水生毒性之间的可能关联

Selective biodegradation of naphthenic acids and a probable link between mixture profiles and aquatic toxicity.

机构信息

Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada.

出版信息

Environ Toxicol Chem. 2013 Oct;32(10):2207-16. doi: 10.1002/etc.2295. Epub 2013 Aug 8.

Abstract

The toxicity of oil sands process-affected waters (OSPW) from the Athabasca Oil Sands (AOS) in northern Alberta, Canada, is related to a relatively persistent group of dissolved organic acids known as naphthenic acids (NAs). Naphthenic acids are a complex mixture of carboxylic acids, with a general formula C(n)H(2n+Z)O2, where n indicates the carbon number and Z specifies the number of rings in the molecule. The present study is the first to evaluate the potential for the selective biodegradation of NAs and the associated reduction in aquatic toxicity of 2 OSPWs, maintained under 2 different hydraulic retention times and increased nutrient availability (nitrate and phosphate), using flow-through laboratory wetland microcosms over a 52-wk test period. High-performance liquid chromatography/quadrupole time of flight-mass spectrometry analysis was used to track the changes in NA mixture profiles, or "fingerprints," in each treatment over time. Based on first-order degradation kinetics, more rapid degradation was observed for NAs that had lower carbon numbers and fewer degrees of cyclization (NA congeners with carbon numbers 11-16 and Z series -2 to -4; half-lives between 19 and 28 wk). Within the NA mixture fingerprints, the 2 most persistent groups of homologues were also identified (NAs with carbon numbers 17-20 and Z series -6 to -12; half-lives between 37 and 52 wk). The persistence of this group of NAs may aid in explaining the residual chronic toxicological response as measured by the Microtox bioassay (effective concentration for 20%), after the degradation of the more labile fractions of NA mixtures in OSPW.

摘要

加拿大阿尔伯塔省北部阿萨巴斯卡油砂(AOS)的油砂加工影响水域(OSPW)的毒性与一组相对持久的溶解有机酸有关,这些酸被称为环烷酸(NAs)。环烷酸是羧酸的复杂混合物,其通式为 C(n)H(2n+Z)O2,其中 n 表示碳原子数,Z 表示分子中环的数量。本研究首次评估了在不同水力停留时间和增加养分供应(硝酸盐和磷酸盐)条件下,通过 52 周的试验期,使用流动实验室湿地微宇宙选择性生物降解 NAs 及其相关的水生毒性降低的潜力。使用高效液相色谱/四极杆飞行时间质谱分析来跟踪每个处理中随时间变化的 NA 混合物图谱或“指纹”的变化。根据一级降解动力学,碳数较低和环化程度较低的 NAs 表现出更快的降解(碳数为 11-16 的 NA 同系物和 Z 系列-2 到-4;半衰期为 19 到 28 周)。在 NA 混合物指纹中,还确定了 2 个最持久的同系物组(碳数为 17-20 的 NAs 和 Z 系列-6 到-12;半衰期为 37 到 52 周)。这组 NAs 的持久性可能有助于解释在 OSPW 中更不稳定的 NA 混合物部分降解后,通过 Microtox 生物测定(20%有效浓度)测量的慢性毒性残留的反应。

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