Department of Soil Science and Agricultural Chemistry, Institute of Agricultural Sciences, Banaras Hindu University, Varanasi, Uttar Pradesh, India.
Department of Soil Science and Agricultural Chemistry, College of Agriculture, Odisha University of Agriculture and Technology, Bhubaneswar, Odisha, India.
Int J Phytoremediation. 2022;24(9):945-954. doi: 10.1080/15226514.2021.1985960. Epub 2021 Oct 11.
The pot experiment was conducted to explore the phytoremediation potential of two different marigold species grown in heavy metals contaminated red, black, alluvial, recent river clay, sewage irrigated, sewage sludge, and garden soil. Different soil types were treated uniformly with lead (20 mg Pb kg soil), cadmium (5 mg Cd kg soil), chromium (30 mg Cr kg soil) and nickel (10 mg Ni kg soil). Completely randomized design (CRD) was used with three replications. African marigold () recorded ∼89.4% more dry matter yield over French marigold () when grown under metals treated soils. Both the marigold species were highly effective for removing Cd and Ni from contaminated soils (TF >1) however, Ni (TF ∼14.9) was more efficiently accumulated by and Cd (TF ∼12.1) by . Higher biomass yield in resulted higher accumulation of heavy metals (except Cr) compared to . Assessment of contamination factor (CF) and geo-accumulation index (I) of heavy metals indicates that post-harvest soils had moderate to high degree of contamination by different metals, Cr being the highest. It may be concluded that was more efficient in extracting heavy metals from different heavy metals contaminated soils. Contamination of land with heavy metals poses severe environmental threats. Physical and chemical remediation techniques are generally used for remediating metals contaminated sites. These methods are cost-intensive and therefore, commercially non-viable, besides being disruptive in nature and causing deterioration of soil. Alternatively, bio-remediation techniques are cost-effective and environment friendly. Among the various phytoremediation techniques, hyperaccumulator plants are most commonly used for the remediation of the contaminated sites. It has been found that different species of the same plant (marigold) differ in their ability to accumulate metals under various contaminated soils having different properties. Thus, this experiment provided an unique opportunity to investigate the effect of various soil properties on metal accumulation efficacy of marigold under metal-spiked soils. Marigold plants can grow rapidly by developing a robust root system which helps them to survive under contaminated soil environment. Thus, marigold being ornamental plant could be used to decontaminate polluted sites while providing ornamental value and may serve as a source of commercially valuable products extracting metals from biomass by way of incineration. However, meager information is available about the usage of various marigold species for phytoremediation of heavy metals under different metal-polluted soils. In the current experiment, we intend to evaluate the potential use of two different marigold species ( and ) in remediating heavy metals under nine soils of different nature spiked with metals and assessing heavy metals pollution load indexes in these polluted soils.
该盆栽实验旨在探索两种不同的万寿菊物种在受重金属污染的红壤、黑土、冲积土、新近河流黏土、污水灌溉、污泥和园林土壤中的植物修复潜力。不同的土壤类型用铅(20mg Pb kg 土壤)、镉(5mg Cd kg 土壤)、铬(30mg Cr kg 土壤)和镍(10mg Ni kg 土壤)均匀处理。采用完全随机设计(CRD),设 3 次重复。在受金属处理的土壤中生长时,非洲万寿菊()的干物质产量比法国万寿菊()高约 89.4%。两种万寿菊物种对受污染土壤中的 Cd 和 Ni 都具有较高的去除效率(TF>1),但镍(TF≈14.9)由 积累效率更高,而镉(TF≈12.1)由 积累效率更高。 较高的生物量产量导致其对不同重金属(除铬外)的积累量高于 。对重金属污染因子(CF)和地积累指数(I)的评估表明,收获后土壤受到不同金属的中度至高度污染,其中铬的污染程度最高。可以得出结论, 从不同重金属污染土壤中提取重金属的效率更高。重金属对土地的污染会带来严重的环境威胁。物理和化学修复技术通常用于修复受污染的场地。这些方法成本高,因此在商业上不可行,而且性质上具有破坏性,会导致土壤恶化。相比之下,生物修复技术具有成本效益,对环境友好。在各种植物修复技术中,超积累植物最常用于污染场地的修复。已经发现,同一种植物(万寿菊)的不同物种在不同性质的受污染土壤中积累金属的能力不同。因此,这项实验为研究不同土壤性质对金属在受金属污染土壤中积累效率的影响提供了一个独特的机会。万寿菊植物可以通过发展强大的根系快速生长,这有助于它们在污染土壤环境中生存。因此,万寿菊作为观赏植物可以用来净化污染的场地,同时提供观赏价值,并可以通过焚烧从生物质中提取金属来作为商业价值高的产品的来源。然而,关于不同万寿菊物种在不同金属污染土壤中用于植物修复重金属的用途,信息很少。在本实验中,我们旨在评估两种不同的万寿菊物种(和)在修复九种不同性质的受金属污染土壤中的重金属的潜力,并评估这些污染土壤中的重金属污染负荷指数。