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Soil microbial community toxic response to atrazine and its residues under atrazine and lead contamination

机译:土壤微生物群落对阿特拉津的毒性反应及其残留在尿嘧啶和铅污染下

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Intensive use of atrazine and extensive dispersal of lead (Pb) have occurred in farmland with chemical agriculture development. However, the toxicological effect of their presence on soil microorganism remains unknown. The objective of this study was to investigate the impacts of atrazine or Pb on the soil microbiota, soil net nitrogen mineralization, and atrazine residues over a 28-day microcosm incubation. The Shannon-Wiener diversity index, typical microbe species, and a Neighbor-joining tree of typical species from sequencing denaturing gradient gel electrophoresis (DGGE) bands were determined across periodical sampling times. The results showed that the existence of atrazine or Pb (especially high concentration) in soils reduced microbial diversity (the lowest H value is 2.23) compared to the control (H = 2.59) after a 28-day incubation. The species richness reduced little (from 17 similar to 19 species to 16 similar to 17 species) over the research time. But soil microbial community was significantly affected by the incubation time after the exposure to atrazine or Pb. The combination of atrazine and Pb had a significant inhibition effect on soil net nitrogen nitrification. Atrazine and Pb significantly stimulated soil cumulative net nitrogen mineralization and nitrification. Pb (300 and 600 mg kg(-1)) accelerated the level of atrazine dissipation. The exposure might stimulate the significant growth of the autochthonous soil degraders which may use atrazine as C source and accelerate the dissipation of atrazine in soils.
机译:在农田中发生了亚唑嗪和广泛的铅(PB)的密集使用,具有化学农业发展。然而,它们在土壤微生物上存在的毒理学效应仍然未知。本研究的目的是探讨阿特拉嗪或Pb对土壤微生物的影响,在28天的微观孵育中对土壤微生物群,土壤氮矿化和阿特拉津残留物的影响。在周期性取样时间确定Shannon-Wener分集指数,典型的微生物物质和典型物种的典型物种的邻接树木曲线测定曲线电泳(DGGE)带。结果表明,与对照(H = 2.59)在孵育后的对照(H = 2.59)相比,土壤中的阿特拉嗪或Pb(特别是高浓度)降低了微生物多样性(最低H值为2.23)。物种丰富性在研究时间上减少了几乎没有(从类似于19种相似的17种相似的16种)。但是土壤微生物群落受到尿嘧啶或Pb的潜伏时间的显着影响。阿特拉嗪和Pb的组合对土壤氮硝化氮化具有显着的抑制作用。阿特拉津和PB显着刺激土壤累积净氮矿化和硝化。 PB(300和600mg kg(-1))加速了甲卓嗪散热水平。曝光可能刺激可使用阿特拉汀作为C来源的自身加热性土壤降解的显着生长,并加速土壤中尿嘧啶的耗散。

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