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Municipal solid wastes as a resource for environmental recovery: Impact of water treatment residuals and compost on the microbial and biochemical features of As and trace metal-polluted soils

机译:市政固体废物作为环境恢复资源:水处理残留物和堆肥对砷和微量金属污染土壤的微生物和生化特性的影响

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In this study we evaluated the microbiological and biochemical impact of iron-based water treatment residuals (Fe-WTRs) and municipal solid waste compost (MSWC), alone and combined, on three different soils co-contaminated with arsenic (As) and trace-metals (TM), i.e. Pb, Cu and Zn. Overall, all the amendments considered significantly increased the abundance of culturable heterotrophic bacteria, with MSWC showing the greatest impact across all soils (up to a 24% increase). In most of treated soils this was accompanied by a significant reduction of both the (culturable) fungal/bacterial ratio, and the proportion of culturable As(V)- and As(III)-resistant bacteria with respect to total bacterial population. The catabolic potential and versatility of the resident microbial communities (assessed by community level physiological profile) was highly soil-dependent and substantial increases of both parameters were observed in the amended soils with the higher total As concentration (from approx. 749 to 22,600 mg kg(-1)). Moreover, both carbon source utilisation profile and 16S rRNA soil metagenome sequencing indicated a significant impact of MSWC and Fe-WTRs on the structure and diversity of soil microbial communities, with Proteobacteria, Actinobacteria and Firmicutes being the most affected taxa. The assessment of selected soil enzyme activities (dehydrogenase, urease and beta-glucosidase) indicated an increase of metabolic functioning especially in soils treated with MSWC (e.g. dehydrogenase activity increased up to 19.5-fold in the most contaminated soil treated with MSWC). Finally, the microbial and biochemical features of treated (and untreated) contaminated soils (i.e. total bacterial counts, catabolic potential and versatility and soil enzyme activities) were highly correlated with the concentrations of labile As and TM in these latter soils and supported a clear role of the tested amendments (especially MSWC) as As- and TM-immobilising agents.
机译:在这项研究中,我们评估了铁基水处理残留物(Fe-WTRs)和城市固体废物堆肥(MSWC)单独和组合对三种被砷(As)和痕量污染物共同污染的土壤的微生物学和生化影响。金属(TM),即Pb,Cu和Zn。总体而言,所有考虑到的修正案均显着增加了可培养异养细菌的丰度,其中MSWC对所有土壤的影响最大(增加了24%)。在大多数处理过的土壤中,这伴随着(可培养的)真菌/细菌比率以及可培养的抗As(V)和抗As(III)细菌相对于总细菌种群的比例显着降低。驻留微生物群落的分解代谢潜力和多功能性(通过群落水平的生理特征评估)高度依赖土壤,并且在总砷浓度较高(从约749到22,600 mg kg)的改良土壤中,观察到两个参数均显着增加。 (-1))。此外,碳源利用概况和16S rRNA土壤基因组测序均表明MSWC和Fe-WTRs对土壤微生物群落的结构和多样性具有重大影响,其中变形杆菌,放线菌和Firmicutes是受影响最大的分类单元。对选定的土壤酶活性(脱氢酶,脲酶和β-葡萄糖苷酶)的评估表明,代谢功能增强,尤其是在用MSWC处理的土壤中(例如,在最污染的MSWC处理的土壤中,脱氢酶活性提高了19.5倍)。最后,已处理(和未处理)污染土壤的微生物和生化特征(即细菌总数,分解代谢潜能,多功能性和土壤酶活性)与这些土壤中不稳定的As和TM的浓度高度相关,并支持明确的作用被测试的修正剂(特别是MSWC)作为As和TM固定剂。

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