Lin Qi, Wang Zhaowei, Ma Song, Chen Yingxu
Department of Environmental Engineering, Zhejiang University, Huajiachi 268 Kaixuan Road, Hangzhou, Zhejiang 310029, People's Republic of China.
Sci Total Environ. 2006 Sep 15;368(2-3):814-22. doi: 10.1016/j.scitotenv.2006.03.024. Epub 2006 Apr 27.
Though phytoremediation is widely studied in remediation of metal contaminated soils or organic contaminated soils, little information is available regarding the effectiveness and processes of phytoremediation of sites co-contaminated with organic and metal pollutants. Sites co-contaminated with organic and metal pollutants are common and considered to be a more complex problem as the two components often cause a synergistic effect on cytotoxicity as measured both by growth inhibition and colony-forming ability. In this paper, the dissipation mechanisms for pentachlorophenol (PCP) in copper co-contaminated soil by Lolium perenne L, and Raphanus sativus was investigated in a greenhouse experiment by monitoring the growth response of plants, evaluating the removal efficiency of extractable PCP, differentiating PCP residuals in strongly and loosely adhering rhizosphere soils, and analyzing the microbial activity in the rhizosphere. In copper co-contaminated soil with the initial PCP concentration of 50 mg/kg, plants grew better with the increment of soil Cu level (0, 150, 300 mg/kg), which implied that combinations of inorganic and organic pollutants sometimes exerted antagonistic effects on plant cytotoxicity. The observed higher PCP dissipation in soil spiked with 50 mg/kg PCP in the presence of Cu and the less difference of PCP residual between strongly and loosely adhering soils further suggests the occurrence of Cu-PCP interaction and the enhanced degradation and mass flow are two possible explanations. In copper co-contaminated soil with the initial PCP concentration of 100 mg/kg, however, both plant growth and microbial activity were inhibited with the increment of soil Cu level. The lowered degrading activity of microorganisms and the reduced mass flow were probably responsible for the significantly lower levels of PCP dissipation in copper co-contaminated soil. These results showed that remediation of sites co-contaminated with organic and metal pollutants is a complex problem and a more thorough understanding of the extent and mechanisms by which metals inhibit organic degradation is needed to develop phytoremediation of co-contaminated sites.
尽管植物修复在金属污染土壤或有机污染土壤的修复方面得到了广泛研究,但关于有机和金属污染物共同污染场地的植物修复效果及过程的信息却很少。有机和金属污染物共同污染的场地很常见,并且被认为是一个更复杂的问题,因为这两种成分通常会对细胞毒性产生协同效应,这可以通过生长抑制和集落形成能力来衡量。在本文中,通过监测植物的生长反应、评估可提取五氯苯酚(PCP)的去除效率、区分紧密和松散附着根际土壤中的PCP残留量以及分析根际微生物活性,在温室实验中研究了黑麦草和萝卜对铜共同污染土壤中PCP的消散机制。在初始PCP浓度为50mg/kg的铜共同污染土壤中,随着土壤铜水平(0、150、300mg/kg)的增加,植物生长得更好,这意味着无机和有机污染物的组合有时会对植物细胞毒性产生拮抗作用。在有铜存在的情况下,在添加了50mg/kg PCP的土壤中观察到更高的PCP消散,并且紧密和松散附着土壤之间的PCP残留差异较小,这进一步表明铜-PCP相互作用的发生,增强的降解和质量流是两种可能的解释。然而,在初始PCP浓度为100mg/kg的铜共同污染土壤中,随着土壤铜水平的增加,植物生长和微生物活性均受到抑制。微生物降解活性的降低和质量流的减少可能是铜共同污染土壤中PCP消散水平显著降低的原因。这些结果表明,有机和金属污染物共同污染场地的修复是一个复杂的问题,需要更深入地了解金属抑制有机降解的程度和机制,以开发共同污染场地的植物修复方法。