经 KMnO4-hematite 改性的生物炭能减轻土壤中镉和锌的生物毒性,从而促进狐尾粟的生长。

Journal of hazardous materials Pub Date : 2024-09-15 Epub Date: 2024-07-29 DOI:10.1016/j.jhazmat.2024.135377
Xirui Kang, Na Geng, Yaping Li, Wei He, Hui Wang, Hong Pan, Quangang Yang, Zhongchen Yang, Yajie Sun, Yanhong Lou, Yuping Zhuge
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引用次数: 0

摘要

土壤中过量积累的镉和锌会毒害农作物,威胁食品安全。本研究开发并应用 KMnO4-hematite 改性生物炭(MnFeB)修复弱碱性镉锌污染土壤,研究了重金属固定效果、植物生长和狐尾粟对金属离子的吸收。施用锰铁硼能降低土壤重金属的植物毒性;生物可利用的酸溶性镉和锌分别减少了 57.79% 和 35.64%,而稳定的、不可生物利用的残留镉和锌分别增加了 96.44% 和 32.08%。叶绿素和总蛋白含量以及超氧化物歧化酶(SOD)活性提高,而脯氨酸、丙二醛、H2O2 含量、谷胱甘肽还原酶(GR)、抗坏血酸过氧化物酶(APX)和过氧化氢酶(CAT)活性降低。相应地,GR、APX 和 CAT 的表达下调,而 MnSOD 的表达上调。此外,锰铁硼能促进狐尾粟植株的净光合速率和生长。此外,MnFeB 还能降低茎、叶和籽粒中的镉和锌含量,降低芽中镉和锌的生物富集因子,并削弱镉和锌从根部向芽的转移。沉淀、络合、氧化还原、离子交换和π-π叠加作用是镉和锌的主要固定机制,MnFeB降低了土壤细菌群落的多样性以及变形菌和扁孢菌的相对丰度。这项研究为镉和锌污染土壤提供了一种可行而有效的修复材料。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Biochar with KMnO4-hematite modification promoted foxtail millet growth by alleviating soil Cd and Zn biotoxicity.

The excessive accumulation of Cd and Zn in soil poisons crops and threatens food safety. In this study, KMnO4-hematite modified biochar (MnFeB) was developed and applied to remediate weakly alkaline Cd-Zn contaminated soil, and the heavy metal immobilization effect, plant growth, and metal ion uptake of foxtail millet were studied. MnFeB application reduced the phytotoxicity of soil heavy metals; bioavailable acid-soluble Cd and Zn were reduced by 57.79% and 35.64%, respectively, whereas stable, non-bioavailable, residual Cd and Zn increased by 96.44% and 32.08%, respectively. The chlorophyll and total protein contents and the superoxide dismutase (SOD)activity were enhanced, whereas proline, malondialdehyde, the H2O2 content, glutathione reductase (GR), ascorbate peroxidase (APX) and catalase (CAT) activities were reduced. Accordingly, the expressions of GR, APX, and CAT were downregulated, whereas the expression of MnSOD was upregulated. In addition, MnFeB promoted the net photosynthetic rate and growth of foxtail millet plants. Furthermore, MnFeB reduced the levels of Cd and Zn in the stems, leaves, and grains, decreased the bioconcentration factor of Cd and Zn in shoots, and weakened the translocation of Cd and Zn from roots to shoots. Precipitation, complexation, oxidation-reduction, ion exchange, and π-π stacking interaction were the main Cd and Zn immobilization mechanisms, and MnFeB reduced the soil bacterial community diversity and the relative abundance of Proteobacteria and Planctomycetota. This study provides a feasible and effective remediation material for Cd- and Zn-contaminated soils.

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