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老化土壤中同时存在镉和芘时,有效苯并[a]芘的消散。

Dissipation of available benzo[a]pyrene in aging soil co-contaminated with cadmium and pyrene.

机构信息

Ministry of Education Key Laboratory of Environment Remediation and Ecosystem Health, College of Environmental and Resources Science, Zhejiang University, Hangzhou, 310058, China.

出版信息

Environ Sci Pollut Res Int. 2014 Jan;21(2):962-71. doi: 10.1007/s11356-013-1960-y. Epub 2013 Jul 11.

Abstract

A microcosm experiment was conducted to investigate the dissipation of available benzo[a]pyrene (BaP) in soils co-contaminated with cadmium (Cd) and pyrene (PYR) during aging process. The available residue of BaP in soil was separated into desorbing and non-desorbing fractions. The desorbing fraction contributed more to the dissipation of available BaP than the non-desorbing fraction did. The concentration of bound-residue fraction of BaP was quite low across all treatments. Within the duration of this study (250 days), transformation of BaP from available fractions to bound-residue fraction was not observed. Microbial degradation was the dominant mechanism of the dissipation of available BaP in the soil. The dissipation of available BaP was significantly inhibited with the increment in Cd level in the soil. The addition of PYR (250 mg kg(-1)) remarkably promoted the dissipation of available BaP without reducing Cd availability in the soil. The calculated half-life of available BaP in the soil prolonged with the increment in Cd level; however, the addition of PYR shortened the half-life of available BaP by 13.1, 12.7, and 32.8% in 0.44, 2.56, and 22 mg Cd kg(-1) soils, respectively. These results demonstrated that the inhibiting effect of Cd and the promoting effect of PYR on the dissipation of available BaP were competitive. Therefore, this study shows that the bioremediation process of BaP can be more complicated in co-contaminated soils.

摘要

采用微宇宙实验研究了共存镉(Cd)和芘(PYR)污染条件下土壤中可利用苯并[a]芘(BaP)的老化过程中消解规律。将土壤中可利用态 BaP 分为解吸态和非解吸态两部分。解吸态对可利用态 BaP 的消解贡献大于非解吸态。各处理下土壤中结合残留态 BaP 的浓度均较低。在本研究的时间范围内(250 天),未观察到可利用态 BaP 向结合残留态转化。微生物降解是土壤中可利用态 BaP 消解的主要机制。随着土壤中 Cd 水平的增加,可利用态 BaP 的消解受到显著抑制。添加 PYR(250 mg kg(-1))可显著促进可利用态 BaP 的消解,而不会降低土壤中 Cd 的有效性。可利用态 BaP 在土壤中的半衰期随 Cd 水平的增加而延长;然而,在 0.44、2.56 和 22 mg Cd kg(-1)的土壤中,添加 PYR 分别将可利用态 BaP 的半衰期缩短了 13.1%、12.7%和 32.8%。这些结果表明,Cd 的抑制作用和 PYR 对可利用态 BaP 消解的促进作用是相互竞争的。因此,本研究表明,在共存污染土壤中,BaP 的生物修复过程可能更加复杂。

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