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[金发草对土壤中菲和芘的去除及修复机制]

[Mechanisms of the removal and remediation of phenanthrene and pyrene in soil by Pogonatherum paniceum].

作者信息

Pan Sheng-Wang, Wei Shi-Qiang, Yuan Xin, Cao Sheng-Xian

机构信息

Key Laboratory of Agricultural Resources and Environment in Chongqing, College of Resources and Environment, Southwest University, Chongqing 400716, China.

出版信息

Huan Jing Ke Xue. 2009 May 15;30(5):1273-9.

Abstract

The mechanisms of the removal and accumulation of phenanthrene (PHE) and pyrene (PYR) by rock plant Pogonatherum paniceum were studied by pot experiments. Results showed that P. paniceum might effectively remove PHE and PYR from soils at their initial concentrations of 20 to 322 mg x kg(-1). About 50.97%-86.77% of PHE or 46.45%-76.7% of PYR was removed from the soils respectively after 70-day plantation of P. paniceum; the average removal rates of PHE or PYR from the soils by P. paniceum were 63.56% and 58.6% higher than those of CK1 (with addition of 0.1% NaN3), and 46.09% and 42.92% higher than those of CK2 (without NaN3). P. paniceum did show ability to accumulate polycyclic aromatic hydrocarbons (PAHs) from the soils; the contents of PAHs in its root and shoot increased withthe increase of PAHs concentrations in the soils. The bioconcentration factors (BCFs) for PAHs tended to decrease with increasing concentrations of these contaminants in soil. BCFs for PYR were higher than those for PHE, and BCFs for PHE (0.12-1.63) and PYR (1.03-5.61) in shoots were much lower than those in roots (0.21-3.08 and 1.31-10.11) at the same treatment. The mechanisms of phytoremediation processes by P. paniceum involve both biotic and abiotic factors. Contributions of each factor to the phytoremediation processes were estimated, which indicated that abiotic loss, plant accumulation, phytodegredation and microbial degradation accounted for 5.1%, 0.32%, 4.22% and 17.47% of the total removal of PHE, and 2.56%, 4.27%, 2.01% and 15.68% of PYR from soils, respectively. In contrast, 41.56% removal of PHE and 36.64% of PYR were attributed to plant-microbial interactions. Thus plant-microbial interactions are the main mechanisms for the remediation of soil PAHs pollution.

摘要

通过盆栽试验研究了岩生植物李氏禾去除和积累菲(PHE)和芘(PYR)的机制。结果表明,李氏禾能够有效去除初始浓度为20至322mg·kg⁻¹土壤中的PHE和PYR。李氏禾种植70天后,土壤中分别去除了约50.97% - 86.77%的PHE或46.45% - 76.7%的PYR;李氏禾对土壤中PHE或PYR的平均去除率分别比添加0.1%NaN₃的CK1高63.56%和58.6%,比不添加NaN₃的CK2高46.09%和42.92%。李氏禾确实表现出从土壤中积累多环芳烃(PAHs)的能力;其根和地上部分中PAHs的含量随着土壤中PAHs浓度的增加而增加。PAHs的生物富集系数(BCFs)倾向于随着土壤中这些污染物浓度的增加而降低。在相同处理下,PYR的BCFs高于PHE的BCFs,且地上部分中PHE(0.12 - 1.63)和PYR(1.03 - 5.61)的BCFs远低于根中(0.21 - 3.08和1.31 - 10.11)的BCFs。李氏禾植物修复过程的机制涉及生物和非生物因素。估算了各因素对植物修复过程的贡献,结果表明,非生物损失、植物积累、植物降解和微生物降解分别占土壤中PHE总去除量的5.1%、0.32%、4.22%和17.47%,以及PYR总去除量的2.56%、4.27%、2.01%和15.68%。相比之下,41.56%的PHE去除量和36.64%的PYR去除量归因于植物 -微生物相互作用。因此,植物 - 微生物相互作用是修复土壤PAHs污染的主要机制。

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