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Enzyme activities and glyphosate biodegradation in a riparian soil affected by simulated saltwater incursion

机译:模拟咸水入侵对河岸土壤酶活性和草甘膦生物降解的影响

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摘要

Soil salinization due to saltwater incursion, is a major threat to biochemical activities and thus strongly alters biogeochemical processes in a freshwater riparian of coastal estuary region. A pot incubation experiment was conducted to investigate the effects of simulated saltwater incursion on some key enzymatic activities and biodegradation dynamics of herbicide glyphosate in a riparian soil in Chongming Island located in the Yangtze River estuary, China. The results showed that saltwater addition with 10% artificial seawater significantly increased the biodegradation efficiency of glyphosate with the lowest residual concentration among all the treatments. However, glyphosate degradation was markedly decreased in the riparian soil with high levels of saltwater treatment. As compared with no saltwater treatment, the half-lives for 20% and 50% seawater treatments were prolonged by 4.9% and 21.1%, respectively. Throughout the incubation period, saltwater addition with 10% seawater stimulated the enzymatic activities in the glyphosate-spiked riparian soil, as compared to the treatment with 0% seawater. Flourescein diacetate (FDA) hydrolysis rate, dehydrogenase activity (DHA), catalase activity, and alkaline phosphatase activity in the glyphosate-spiked riparian soil treated with 10% seawater were 68.5%, 49.2%, 38.7%, and 28.6% higher than those for no saltwater treatment, respectively. The effect of 20% seawater treatment on the glyphosate-spiked riparian soil enzymatic activities fluctuated between promotion and inhibition depending on the type of enzymes. Soil enzymatic activities were severely depressed by increasing salinity level with 50% seawater treatment significantly inhibited, relative to no saltwater treatment. Especially, FDA hydrolysis rate and DHA were decreased by 73.8% and 64.8%, respectively, as compared to no saltwater treatment. Glyphosate degradation percentages were strongly positively correlated to the FDA hydrolysis rate and DHA, indicating that as compared to the other enzymes, the two enzymes contributed more to the herbicide biodegradation in the salt-affected riparian soil.
机译:盐水入侵造成的土壤盐碱化是对生物化学活动的主要威胁,因此强烈改变了沿海河口地区淡水河岸带的生物地球化学过程。通过盆栽试验研究了模拟海水入侵对长江口崇明岛河岸土壤中某些关键酶活性和除草剂草甘膦生物降解动力学的影响。结果表明,在所有处理中,添加10%人造海水的盐水显着提高了草甘膦的生物降解效率,残留浓度最低。然而,在高水平盐水处理下,河岸土壤中草甘膦的降解显着降低。与不进行盐水处理相比,海水处理的20%和50%的半衰期分别延长了4.9%和21.1%。在整个潜伏期中,与0%海水处理相比,添加10%海水的盐水刺激了草甘膦加喷的河岸土壤中的酶活性。用10%海水处理的草甘膦加水河岸土壤中的氟乙酸甘油酯(FDA)水解率,脱氢酶活性(DHA),过氧化氢酶活性和碱性磷酸酶活性分别比分别高68.5%,49.2%,38.7%和28.6%。分别不进行盐水处理。 20%的海水处理对草甘膦加水的河岸土壤酶活性的影响在促进和抑制之间波动,具体取决于酶的类型。盐度水平的提高严重地抑制了土壤酶的活性,相对于未进行盐水处理而言,50%的海水处理受到了显着抑制。特别是,与未进行盐水处理相比,FDA的水解率和DHA分别降低了73.8%和64.8%。草甘膦的降解百分率与FDA水解速率和DHA呈极强的正相关,表明与其他酶相比,这两种酶在受盐影响的河岸土壤中对除草剂生物降解的贡献更大。

著录项

  • 作者

    Changming Yang; Mengmeng Wang;

  • 作者单位
  • 年度 2011
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  • 原文格式 PDF
  • 正文语种 {"code":"en","name":"English","id":9}
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