MOE Key Laboratory on Pollution Processes and Environmental Criteria, College of Environmental Science and Engineering, Nankai University, Tianjin, 300350, China.
MOE Key Laboratory on Pollution Processes and Environmental Criteria, College of Environmental Science and Engineering, Nankai University, Tianjin, 300350, China.
Environ Pollut. 2018 May;236:158-167. doi: 10.1016/j.envpol.2018.01.030.
One interest of using biochar as soil amendment is to reduce pesticide adverse effects. In this paper, the sorption and degradation of thiacloprid (THI) in a black soil amended by various biochars were systematically investigated, and the mechanisms therein were explored by analyzing the changes in soil physicochemical properties, degrading enzymes and genes and microorganism community. Biochar amendment increased THI sorption in soil, which was associated with an increase in organic carbon and surface area and a decrease in H/C. Amendments of 300-PT (pyrolyzing temperature) biochar promoted the biodegradation of THI by increasing the microbe abundance and improving nitrile hydratase (NHase) activity. In contrast, 500- and 700-PT biochar amendments inhibited biodegradation by reducing THI availability and changing NHase activity and THI-degradative nth gene abundance, and instead promoted chemical degradation mainly through elevated pH, active groups on mineral surface and generation of •OH and other free radicals. Furthermore, THI shifted the soil microbial community, stimulated the NHase activity and elevated nth gene abundance. Biochar amendments also changed soil bacterial community by modulating soil pH, dissolved organic matter and nitrogen and phosphorus levels, which further influenced THI biodegradation. Therefore, the impact of biochars on the fate of a pesticide in soil depends greatly on their type and properties, which should be comprehensively examined when applying biochar to soil.
将生物炭作为土壤改良剂的一个目的是减少农药的不良影响。本文系统地研究了不同生物炭改良的黑土中噻虫啉(THI)的吸附和降解情况,并通过分析土壤理化性质、降解酶和基因以及微生物群落的变化,探讨了其中的机制。生物炭的添加增加了土壤中 THI 的吸附,这与有机碳和比表面积的增加以及 H/C 的降低有关。300-PT(热解温度)生物炭的添加促进了 THI 的生物降解,增加了微生物丰度并提高了腈水合酶(NHase)活性。相比之下,500-和 700-PT 生物炭的添加通过降低 THI 的可用性以及改变 NHase 活性和 THI 降解 nth 基因丰度来抑制生物降解,而是通过提高 pH 值、矿物表面的活性基团以及生成 •OH 和其他自由基来促进化学降解。此外,THI 改变了土壤微生物群落,刺激了 NHase 活性并提高了 nth 基因丰度。生物炭的添加还通过调节土壤 pH 值、溶解有机质和氮磷水平来改变土壤细菌群落,这进一步影响了 THI 的生物降解。因此,生物炭对土壤中农药命运的影响在很大程度上取决于其类型和特性,在将生物炭应用于土壤时应综合考虑这些特性。