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Microbes Influence The Fractionation Of Arsenic In Paddy Soils With Different Fertilization Regimes

机译:微生物影响不同施肥方式下水稻土中砷的分离

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Sequential extraction procedures were used to investigate the influence of the microbes on the distribution of arsenic in a Chinese paddy soil under different long-term fertilization treatments. The paddy soil with four long-term fertilization treatments (CK, M, NPK and NPK+M) and three levels of arsenate addition (0,50,100 mg As kg~(-1) dry soil), were selected to construct microcosms for laboratory incubation. After the incubation, soil samples were sequentially extracted to determine As in various fractions, i.e. water soluble (F0), exchangeable (F1), bound to carbonates (F2), bound to Fe and Mn oxides (F3), bound to organic matter and sulfides (F4), and residual (F5, mineral matrix). Results showed that most of the As was fixed by mineral matrix (F5, ratios ranging from 46.22% to 96.37%), followed by As bound to Fe and Mn oxides (F3, ratios ranging from 3.14% to 28.18%), and the ratios of the other four fractions (F0, F1, F2 and F4) were mostly less than 10%. The microbes in the paddy soil could make As transform from inactive fraction (F5) to relatively active fractions (F0, F1, F2 and F3) and thus increase its environmental risk. With the increase of the As addition levels and with the application of manure or chemical NPK fertilizers, As was distributed more in the relatively active fractions (F0, F1, F2, F3 and F4) in the paddy soil mediated by the microbes. In addition, Fe and Mn oxides could play an important role in decreasing the As leaching potential from the mineral matrix to soil solution and thus abate the As risk to human health.
机译:采用连续提取方法研究了不同长期施肥条件下微生物对中国稻田土壤砷分布的影响。选择4种长期施肥的水稻土(CK,M,NPK和NPK + M)和3种砷的添加水平(0,50,100 mg As kg〜(-1)旱土),构建实验室的缩影。孵化。孵育后,依次提取土壤样品,以测定各个部分的As,即水溶性(F0),可交换(F1),与碳酸盐(F2)结合,与Fe和Mn氧化物(F3)结合,与有机物和硫化物(F4)和残留物(F5,矿物基质)。结果表明,大多数As被矿物基质固定(F5,比例为46.22%至96.37%),其次是As与Fe和Mn氧化物结合(F3,比例为3.14%至28.18%),且比例固定其他四个部分(F0,F1,F2和F4)中的大多数都小于10%。稻田土壤中的微生物可能使砷从非活性组分(F5)转变为相对活性组分(F0,F1,F2和F3),从而增加其环境风险。随着砷添加量的增加以及粪肥或化学氮磷钾肥料的施用,砷在微生物介导的水稻土中相对活跃的部分(F0,F1,F2,F3和F4)中分布更多。此外,铁和锰的氧化物可能在降低砷从矿物基质到土壤溶液中的浸出潜力中扮演重要角色,从而减轻砷对人体健康的危害。

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