Academy of Scientific and Innovative Research (AcSIR), Ghaziabad, Uttar Pradesh, India.
CSIR-National Environmental Engineering Research Institute (NEERI), Nagpur, Maharashtra, India.
Int J Phytoremediation. 2024;26(9):1518-1525. doi: 10.1080/15226514.2024.2331708. Epub 2024 Apr 2.
Heavy metal-enriched fly ash (FA) deposits are recognized as hazardous contaminated sites on the earth, which pollute our ecosystems. Consequently, the present investigation was carried out to explore the phytoremediation potential of naturally growing medicinal plants in the FA dumpsite. This present study chose two native medicinal plants and found to be naturally colonizing abundantly on FA dumpsite to assess heavy metal accumulation. FA sample of thriving sites found to have metal content in order Mn (216.6)> Cr (39.27)> Zn (20.8)> Ni (16.1)> Cu (15.03)> Co (6.7)> Pb (5.43) whereas for FA dumpsites, the order of metal availability was Mn (750.3)> B (54.5)>Cr (37.2)>Zn (31.33)> Cu (18.7)> Ni (16.93)> Co (7.7)>Pb (4.23). In , higher concentrations of Cr and Mn were observed in the shoot in comparison to the root, indicative of its potential as a hyperaccumulator plant. Conversely, in , greater amounts of Pb were detected in the shoot relative to the root. Hence, it is recommended that and grow on such heavy metal-enriched substrates should be avoided for medicinal purposes; however, these plants can be used for phytoremediation purposes.
重金属富集的粉煤灰(FA)矿床被认为是地球上的危险污染场地,它们污染了我们的生态系统。因此,本研究旨在探索自然生长在 FA 堆放场的药用植物的植物修复潜力。本研究选择了两种本地药用植物,发现它们在 FA 堆放场大量自然定殖,以评估重金属积累情况。在 FA 生长旺盛的地点发现的 FA 样本中,金属含量顺序为 Mn(216.6)>Cr(39.27)>Zn(20.8)>Ni(16.1)>Cu(15.03)>Co(6.7)>Pb(5.43),而对于 FA 堆放场,金属可利用性顺序为 Mn(750.3)>B(54.5)>Cr(37.2)>Zn(31.33)>Cu(18.7)>Ni(16.93)>Co(7.7)>Pb(4.23)。在 中,与根相比,茎叶中 Cr 和 Mn 的浓度更高,表明其具有作为超积累植物的潜力。相反,在 中,茎叶中 Pb 的含量相对较高。因此,建议避免将 和 等生长在富含重金属的基质上用于药用目的;然而,这些植物可以用于植物修复目的。