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首页> 外文期刊>Bulletin of University of Agricultural Sciences and Veterinary Medicine Cluj-Napoca: Agriculture >Estimation of Efficiency of Bio- and Phytoremediation for Pesticides Contaminated Soil
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Estimation of Efficiency of Bio- and Phytoremediation for Pesticides Contaminated Soil

机译:农药污染土壤的生物修复和植物修复效率估算

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Natural recovery of environmental pollution - natural attenuation, - is a long-term process. Development of a bioremediation technology for polluted soil is a multi-step process, which requires the integrated application of several methods: stimulation of the indigenous microflora in the contaminated site, and addition of microorganism-destructors to the soil. Recently at the final stages of soil remediation the method of phytoremediation is actively used. To estimate the efficiency of bioremediation of pesticides contaminated soil, using stimulation of anaerobic or facultative anaerobic microflora and phytoremediation applied afterwards. The soil was collected nearby the former destroyed storehouse of POPs. Pesticide residues in soil were evaluated using GC/MS multiresidue method, and the complex pollution of DDTs and trifluralin was found. With a view to remediate this complex contamination, the polluted soil was treated in combined aerobic and anaerobic conditions during 3.5 months, then the method of phytoremediation was used. The trifluralin content was reduced to 4-6% of the initial amount in all experimental variants as a result of bioremediation in anaerobic/aerobic conditions. Phytoremediation had not significant effect on trifluralin decomposition - only 2-3%. Before phytoremediation DDT was decomposed on 27.5-29.0%. After the phytoremediation, the degradation of pesticide amounted 56.3-72.5%. This study has shown, that in the case of complex pollution, phytoremediation, as a method of supplementary remediation, was important for the decomposition of DDT and DDE, and it was not essential for the mineralization of DDD and trifluralin.
机译:自然恢复环境污染-自然衰减-是一个长期过程。针对污染土壤的生物修复技术的发展是一个多步骤的过程,需要综合应用以下几种方法:在受污染的地点刺激本地微生物群落,并向土壤中添加微生物破坏因子。最近,在土壤修复的最后阶段,正在积极使用植物修复方法。为了评估农药污染土壤的生物修复效率,使用厌氧菌或兼性厌氧菌群进行刺激,然后进行植物修复。土壤是在以前被毁的持久性有机污染物仓库附近收集的。采用GC / MS多残留法对土壤中的农药残留进行了评估,发现了滴滴涕和氟乐灵的复杂污染。为了补救这种复杂的污染,在有氧和厌氧的条件下对污染的土壤进行了3.5个月的处理,然后采用了植物修复的方法。在厌氧/好氧条件下进行生物修复的结果是,在所有实验变体中,三氟拉林的含量降低至初始量的4-6%。植物修复对三氟拉林的分解没有显着影响-只有2-3%。在进行植物修复之前,DDT的分解率为27.5-29.0%。植物修复后,农药的降解率为56.3-72.5%。这项研究表明,在复杂污染的情况下,植物修复作为一种补充修复方法,对DDT和DDE的分解很重要,而对DDD和三氟拉林的矿化并不是必需的。

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