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堆肥和生物炭对污染土壤中微生物群落及多环芳烃和含氮取代多环芳烃吸附/降解的影响。

Influence of compost and biochar on microbial communities and the sorption/degradation of PAHs and NSO-substituted PAHs in contaminated soils.

机构信息

University of Vienna, Department of Environmental Geosciences and Environmental Science Research Network, Althanstrasse 14, UZA2, 1090 Vienna, Austria.

VIBT EQ Extremophile Center, Department of Biotechnology, University of Natural Resources and Life Sciences, Muthgasse 18, 1190 Vienna, Austria.

出版信息

J Hazard Mater. 2018 Mar 5;345:107-113. doi: 10.1016/j.jhazmat.2017.11.010. Epub 2017 Nov 10.

DOI:10.1016/j.jhazmat.2017.11.010
PMID:29136576
Abstract

Diffusely contaminated soils often remain untreated as classical remediation approaches would be disproportionately expensive. Adding compost can accelerate the biodegradation of organic contaminants and adding biochar can immobilize contaminants through sorption. The combined use of compost and biochar to reduce polycyclic aromatic hydrocarbon (PAH) and NSO-substituted PAH contamination has, however, not previously been systematically investigated. We have therefore investigated the processes involved (i) through sorption batch experiments, (ii) by monitoring changes in bacterial, fungal and archaeal communities using denaturing gradient gel electrophoresis, and (iii) through degradation experiments with fluorene, phenanthrene, pyrene, carbazole, dibenzothiophene, and dibenzofuran. Sorption coefficients for organic contaminants in soils increased tenfold following 10% compost addition and up to a hundredfold with further addition of 5% biochar. The rate of PAH and NSO-PAH degradation increased up to twofold following compost addition despite increased sorption, probably due to the introduction of additional microbial species into the autochthonous soil communities. In contrast, degradation of PAHs and NSO-PAHs in soil-compost-biochar mixtures slowed down up to tenfold due to the additional sorption, although some degradation still occurred. The combined use of biochar and compost may therefore provide a strategy for immobilizing PAHs and NSO-PAHs and facilitating degradation of remaining accessible contaminant fractions.

摘要

受污染土壤通常未经处理,因为传统的修复方法代价过高。添加堆肥可以加速有机污染物的生物降解,而添加生物炭可以通过吸附作用固定污染物。然而,以前并没有系统地研究过同时使用堆肥和生物炭来减少多环芳烃(PAH)和取代的多环芳烃(NSO-PAH)污染的方法。因此,我们研究了以下过程:(i)通过吸附批实验,(ii)通过使用变性梯度凝胶电泳监测细菌、真菌和古菌群落的变化,以及(iii)通过对芴、菲、芘、咔唑、二苯并噻吩和二苯并呋喃的降解实验。在添加 10%堆肥后,土壤中有机污染物的吸附系数增加了十倍,而进一步添加 5%生物炭后则增加了一百倍。尽管吸附增加了,但在添加堆肥后,PAH 和 NSO-PAH 的降解速率增加了一倍,这可能是由于更多的微生物物种被引入到了土壤的土著群落中。相比之下,由于额外的吸附作用,PAHs 和 NSO-PAHs 在土壤-堆肥-生物炭混合物中的降解速度减慢了十倍,但仍有一些降解发生。因此,同时使用生物炭和堆肥可能是一种固定 PAH 和 NSO-PAH 并促进残留可及污染物降解的策略。

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