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Plant diversity enhances the natural attenuation of polycyclic aromatic compounds (PAHs and oxygenated PAHs) in grassland soils

机译:植物多样性增强了草原土壤中多环芳烃(PAHS和含氧PAH)的自然衰减

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摘要

Increasing plant species richness stimulates microbial activity in soil, which might favor biodegradation of polycyclic aromatic compounds (PACs). To explore the relationship between plant community composition and PACs in grassland soils (Fluvisols exposed to an urban atmosphere), we determined the concentrations of 29 polycyclic aromatic hydrocarbons (PAHs) and 15 oxygenated PAHs (OPAHs) in topsoils of 80 plots of a grassland biodiversity experiment. The plots included different levels of plant species richness (1, 2, 4, 8, 16, 60 species) and 1-4 plant functional groups (grasses, small herbs, tall herbs, and legumes) in a randomized block design. The concentrations (ng g(-1)) of Sigma 29PAHs and Sigma 150PAHs in the soils were 271-2407 and 57-329, respectively. Concentrations of 16 (out of 44) PACs and Sigma 29PAHs decreased significantly with increasing plant species richness, after accounting for the effects of block and initial soil organic C concentration (ANCOVA, p & 0.05). Microbial turnover as the mechanism underlying this relationship was supported by the findings that (i) the regression of the concentrations of PAH with & 4 aromatic rings on plant species richness yielded slopes that were negatively correlated with their octanol-water partitioning coefficients, (ii) two OPAHs accumulated in soils with higher plant species richness, and (iii) higher plant species richness increased four OPAH/parent-PAH ratios. Accordingly, structural equation modeling indicated that the higher concentration of 1,2-acenaphthenequinone (a metabolite of acenaphthene) and the higher 1,2-acenaphthenequinone/acenaphthene and 1-indanone/fluorene ratios in plots with higher plant species richness were partly explained by higher soil microbial biomass on plots with higher plant species richness. We conclude that higher plant species richness can be used to enhance biodegradation of aged PACs in soil. We however caution that OPAHs (some of which are more toxic than their related PAHs) might accumulate in soils during such a plant-assisted remediation process.
机译:增加的植物物种富含性刺激土壤中的微生物活性,这可能有利于多环芳族化合物(PACS)的生物降解。探讨植物群落组成和草原土壤中PACS之间的关系(博尔沃斯苏尔暴露在城市大气中),我们确定了29种多环芳烃(PAH)和15个含氧PAHS(OPAHS)在草原生物多样性的80个曲线上的浓度实验。该地块包括随机块设计中的不同植物物种丰富度(1,2,4,8,16,60,60种)和1-4种植物官能团(草,小草草,高层草药和豆类)。土壤中Sigma 29Pahs和Sigma 150Pahs的浓度(Ng g(-1))分别为271-2407和57-329。在植物物种丰富性的情况下,植物物种的浓度显着减少了16个(44个)PACS和Sigma 29Pah的浓度随着植物物种的影响而显着下降。作为这种关系的机制的研究结果支持微生物营业额是(i)&amp的浓度的回归; 4植物物种的芳香环富含曲率与其辛醇 - 水分配系数呈负相关,(ii)在植物物种丰富的土壤中积累的两种蛋白石,(iii)高等植物物种丰富,增加了四个opah /父母pah比率。因此,结构方程模型表明,部分含量较高的1,2-亚苯二酚(亚苯甲酸根代谢物)和较高的1,2-丙基醌/亚丁烯和1-吲哚酮/芴r比的较高植物物种丰富度的较高浓度均解释高等植物物种丰富的地块上的较高土壤微生物测量。我们得出结论,较高的植物物种丰富性可用于增强土壤中老化的生物降解。然而,我们谨慎,奥普斯(其中一些比他们的相关PAH)在这种植物辅助修复过程中可能会积聚在土壤中。

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