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Lumbricid macrofauna alter atrazine mineralization and sorption in a silt loam soil

机译:大型软体动物改变粉质壤土中阿特拉津的矿化和吸附

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摘要

Atrazine is a widely used herbicide and is often a contaminant in terrestrial and freshwater ecosystems. It is uncertain, however, how the activity of soil macrofauna affects atrazine fate and transport. Therefore, we investigated whether earthworms enhance atrazine biodegradation by stimulating herbicide degrading soil microflora, or if they increase atrazine persistence by facilitating herbicide sorption. Short (43 d) and medium term (86 d) effects of the earthworms and on mineralization, distribution, and sorption of U-ring-C atrazine and on soil C mineralization was quantified in packed-soil microcosms using silt loam soil. A priming effect (stimulation of soil C mineralization) caused by atrazine supply was shown that likely lowered the earthworm net effect on soil C mineralization in atrazine-treated soil microcosms. Although earthworms significantly increased soil microbial activity, they reduced atrazine mineralization to CO–C from15.2 to 11.7% at 86 d. Earthworms facilitated formation of non-extractable atrazine residues within C-rich soil microsites that they created by burrowing and ingesting soil and organic matter. Atrazine sorption was highest in their gut contents and higher in casts than in burrow linings. Also, gut contents exhibited the highest formation of bound atrazine residues (non-extractable atrazine). Earthworms also promoted a deeper and patchier distribution of atrazine in the soil. This contributed to greater leaching losses of atrazine in microcosms amended with earthworms (3%) than in earthworm-free microcosms (0.003%), although these differences were not significant due to high variability in transport from earthworm-amended microcosms. Our results indicated that earthworms, mainly by casting activity, facilitated atrazine sorption, which increased atrazine persistence. As a consequence, this effect overrode any increase in atrazine biodegradation due to stimulation of microbial activity by earthworms. It is concluded that the affect of earthworms of atrazine mineralization is time-dependent, mineralization being slightly enhanced in the short term and subsequently reduced in the medium term.
机译:阿特拉津是一种广泛使用的除草剂,通常是陆地和淡水生态系统中的污染物。然而,尚不确定土壤中大型动物的活动如何影响阿特拉津的命运和运输。因此,我们调查了whether是否通过刺激除草剂降解土壤微生物区系来增强at去津的生物降解性,还是通过促进除草剂的吸附来提高at去津的持久性。在淤泥质壤土中,定量研究了micro的短期(43 d)和中期(86 d)以及and对U型环-C r去津的矿化,分布和吸附以及对土壤C矿化的影响。研究显示,由at去津供应引起的启动效应(刺激土壤C矿化)可能降低了net净处理过的土壤微观世界中net对土壤C矿化的净效应。尽管earth显着提高了土壤微生物活性,但它们在86 d时将阿特拉津的成矿作用从CO降低到15.2到11.7%。通过挖土和摄取土壤和有机质而促进了富含C的土壤微地点中不可提取的at去津残留物的形成。阿特拉津在肠道中的吸附量最高,在铸模中的吸附量高于洞穴壁。而且,肠内容物表现出结合的at去津残基(不可提取的at去津)的最高形成。 also还促进了阿特拉津在土壤中更深和更分散的分布。这比用无azine的缩微胶膜(0.003%)导致at去津的micro失损失更大(3%),尽管这些差异并不明显,因为from修饰的微胶膜的转运具有很大的可变性。我们的结果表明,mainly主要通过铸造活动促进d去津的吸附,从而增加at去津的持久性。结果,由于effect刺激微生物活性,这种作用抵消了over去津生物降解的任何增加。结论是at对阿特拉津矿化的影响是随时间变化的,短期内矿化作用略有增强,而在中期则降低。

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