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首页> 外文期刊>Journal of Environmental Management >Effect of soil organic matter (SOM) on the degradation of polycyclic aromatic hydrocarbons using Pleurotus dryinus IBB 903-A microcosm study
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Effect of soil organic matter (SOM) on the degradation of polycyclic aromatic hydrocarbons using Pleurotus dryinus IBB 903-A microcosm study

机译:利用平菇IBB 903-A微观研究土壤有机质(SOM)对多环芳烃降解的影响

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摘要

Bioremediation of polycyclic aromatic hydrocarbons (PAHs) in soil matrix is often arbitrated by the presence of soil organic matter (SOM). The present study focuses on determining the effect of the soil organic content on the mycoremediation of two model PAHs, phenanthrene (Phe) and benzo(a) pyrene (BaP) through microcosm studies. On comparing various microcosm strategies, a maximum degradation of Phe (99%) and BaP (48.5%) in soil bioaugmented with Pleurotus dryinus IBB 903, followed by, biostimulation with the degradation of Phe (89.9%) and BaP (24.8%) were noted. On relating the degradation pattern with lignolytic enzyme cocktail production, a laccase activity of 108 U/Kg at day 21, aryl alcohol oxidase (411 U/Kg) and manganese peroxidase (52.2 U/Kg) at day 14 along with lignin peroxidase (481 U/Kg) at day 21 were noted in fungal augmented soils, which were comparatively higher than levels observed in the bio-stimulation. Investigating the impact of different concentration of SOM (3-12%), a maximum remediation of Phe by 100% at 9% SOM in days 28 and 58.19% for BaP at 12% SOM, respectively was exhibited. Further, the biosorption effect of PAHs in abiotic condition showed a positive correlation with the increase in SOM, with a maximum adsorption of 3.78% Phe, and 6.93% BaP. The results support that the nominal adsorption ability of SOM, and helps in enhancing the microbial growth, thereby improving their degradation potentials, when less than 6% of SOM was utilized. Overall, this work establishes the critical role of organic matter in the soil with reference by simultaneous stimulation and degradation capability in complete PAHs remediation.
机译:土壤基质中多环芳烃(PAHs)的生物修复通常因土壤有机质(SOM)的存在而受到争议。本研究的重点是通过微观研究确定土壤有机物含量对两种模型PAHs菲(Phe)和苯并(a)pyr(BaP)的mycoremediation的影响。在比较各种微观策略时,在以平菇IBB 903增强的生物强化土壤中,Phe(99%)和BaP(48.5%)的最大降解,其次是对Phe(89.9%)和BaP(24.8%)降解的生物刺激。注意。将降解模式与木质素酶混合物的产生联系起来,第21天的漆酶活性为108 U / Kg,第14天的芳基醇氧化酶(411 U / Kg)和锰过氧化物酶(52.2 U / Kg)以及木质素过氧化物酶(481) (U / Kg)在第21天在真菌增强土壤中被记录,相对高于生物刺激中观察到的水平。调查不同浓度的SOM(3-12%)的影响,分别显示28天和9%的BaP在12%SOM的情况下最大修复Phe在9%SOM时100%和58.19%。此外,在非生物条件下PAHs的生物吸附作用与SOM的增加呈正相关,最大吸附为3.78%Phe和6.93%BaP。当使用少于6%的SOM时,结果支持SOM的名义吸附能力,并有助于增强微生物的生长,从而提高其降解潜力。总的来说,这项工作通过同时刺激和降解PAHs的完全修复能力,确立了有机质在土壤中的关键作用。

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