麻疯树种植土壤重金属污染的植物修复研究

A. Sani, S.A. Danturai,, M. Mohamed, M. B. Abubakar, M.H Kafinga, R. Aliyu, A. Haruna, I. Adam, J. Aliyu, M. Garba, N. Abdullahi
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引用次数: 1

摘要

本研究旨在评价麻疯树对重金属污染土壤的修复潜力。将麻风树的成熟插枝种植在塑料盆中,塑料盆中填满3种不同浓度的HMs污染土壤;采用完全随机设计(CRD),分别为250mg/kg、500mg/kg和1000mg/kg。目的是评估麻疯树是否可以用来治疗重金属;检测污染土壤中的Zn、Ni、Cd、Pb和Cu,确定处理后的金属是否符合尼日利亚等相关国际标准所倡导的农业土壤土壤允许限量浓度。结果表明,不同土壤污染程度对各重金属含量的影响差异均有统计学意义(P<0.05)。然而,尽管它们的浓度在初始土壤污染时达到了标准,但在麻风树种植前后,Cu、Zn和Ni金属均未达到尼日利亚标准,但它们被麻风树植物高度去除。在500mg/kg烃燃料土壤污染条件下,金属的去除率最高,为57% ~ 95%。除1000mg/kg烃燃料污染达到美国标准,脱除效率在8% ~ 42%之间外,麻疯树种植前后Cd金属浓度均低于达标标准。然而,无论是污染初始浓度还是种植后的浓度,Pb金属浓度都较高且变化较大,在麻疯树植物修复后达到或不达到某些国家规定的一定浓度标准。总体而言,本研究结果表明,尽管麻疯树植物修复过程在两个月的时间内,但在500mg/kg污染水平下,植物对污染土壤中的金属具有有效的净化作用,特别是Cu、Zn和Ni。因此,需要继续进行实验,以充分确定最佳金属植物修复所需的实际周期和适当的土壤污染水平,以及麻疯树在修复方面比其他植物更喜欢的金属类型。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Phytoremediation of Heavy Metals Contaminated Agricultural Soil Planted to Jatropha curcas
This study was conducted to assess the potential of Jatropha curcas in remediating soils contaminated with heavy metals from hydrocarbon fuel. Matured cuttings of Jatropha plant were planted in the plastic pots filled with soils contaminated with three different level of HMs concentration; 250mg/kg, 500mg/kg and 1000mg/kg respectively arranged in a Completely Randomized Design (CRD). The aim was to appraise if Jatropha curcas can be used to treat the heavy metals; Zn, Ni, Cd, Pb and Cu in the contaminated soils and determine whether the treated metals complied to soil permissible limit concentration of agricultural soils advocated by Nigerian and other related international standards. Findings indicated that all the analysed metals recorded a significant statistical difference with different level of soil contamination (P<0.05). However, despite their concentration achieved compliance at their initial soil contamination, Cu, Zn and Ni were highly removed by Jatropha plant though the latter metal failed compliance to Nigerian standard at both pre and post Jatropha planting period. Moreover, the metals showed highest removal efficiency in the range of 57%-95% at 500mg/kg hydrocarbon fuel soil contamination. In contrast, Cd metal concentration was low and above compliance limit at pre and post Jatropha planting period except at 1000mg/kg hydrocarbon fuel contamination that achieved compliance of United States (US) with removal efficiency in the range of 8%-42%. However, Pb metal concentration was high and variable at both initial contamination and concentration after Jatropha planting, with the metal achieving and failing compliance of some countries at certain level of concentration after the Jatropha phytoremediation. Overall, the outcome of this research indicates that the Jatropha plant has depurated the metals effectively from the contaminated soils particularly Cu, Zn and Ni at 500mg/kg level of contamination despite the fact that the phytoremediation process was within the period of two months. Hence, the continuation of the experiment is needed in order to fully determine the actual period and appropriate level of soil contamination required for the optimum metal phytoremediation and type of metals the Jatropha plant prefers most in terms of the remediation compared to others.
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