塑料镉共污染土壤的生物炭修复及其对山竹苋生长的影响[j]。

Q2 Environmental Science
Yan-Xiao Cao, Jiang-Xiu Yang, Nuo Chen, Xin-Yu Xu, Jun-Feng Wu, Hong-Hu Li, Jing-Tao Hou, Jing-Dong Zhang
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引用次数: 0

摘要

通过盆栽试验,研究了在聚丙烯(PP)塑料和Cd共污染土壤中,不同浓度(0.1%和1%)和不同粒径的生物炭对土壤性质、镉(Cd)生物有效性和苋菜(Amaranthus mangostanus L.)生长的影响。结果表明,在低剂量(0.1%)塑料镉共污染土壤中,生物炭显著提高了土壤阳离子交换量、铵态氮和有效磷,分别提高了4.14% ~ 22.75%、92.82% ~ 130.57%和2.86% ~ 18.91%。相比之下,在高剂量(1%)塑料- cd共污染土壤中,土壤pH值和溶解有机碳含量增加幅度更大。生物炭主要通过物理吸附和化学钝化作用,使低剂量塑料-Cd共污染土壤中有效Cd含量、苋菜Cd含量和苋菜Cd富集因子分别降低10.29% ~ 23.35%、4.40% ~ 39.06%和10.92% ~ 34.45%。然而,在高剂量塑料-Cd共污染土壤中,生物炭出乎意料地促进了苋菜对Cd的吸收,并且在较小的塑料粒径下观察到更多的Cd积累。此外,生物炭显著提高了苋菜生物量和抗氧化酶活性,且在低剂量和大尺寸塑料污染条件下效果更为显著。冗余分析和偏最小二乘路径模型表明,生物炭通过吸附和固定Cd、改善土壤理化性质和养分有效性、抑制塑料-重金属协同效应、激活植物抗氧化防御系统等途径缓解共污染胁迫。综上所述,在低剂量塑料-Cd共污染土壤中,稻壳生物炭显著改善了土壤理化性质,降低了Cd的生物有效性,促进了植物生长。对于高剂量塑料镉污染,需要生物炭与植物修复相结合的策略来增强镉的固定化。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
[Biochar Remediation of Plastic-cadmium Co-contaminated Soil and Its Effect on Amaranthus mangostanus L. Growth].

A pot experiment was conducted to investigate the effects of biochar on soil properties, cadmium (Cd) bioavailability, and amaranth (Amaranthus mangostanus L.) growth in soils co-contaminated with polypropylene (PP) plastics and Cd, across varying PP dosages (0.1% and 1%) and particle sizes. The results indicated that in low-dose (0.1%) plastic-Cd co-contaminated soil, biochar significantly increased soil cation exchange capacity, ammonium nitrogen, and available phosphorus by 4.14%-22.75%, 92.82%-130.57%, and 2.86%-18.91%, respectively. In contrast, in high-dose (1%) plastic-Cd co-contaminated soil, greater increases in soil pH and dissolved organic carbon content were observed. Biochar reduced the available Cd content, amaranth Cd content, and the Cd enrichment factor of amaranth in low-dose plastic-Cd co-contaminated soil by 10.29%-23.35%, 4.40%-39.06%, and 10.92%-34.45%, respectively, primarily through physical adsorption and chemical passivation. However, in the high-dose plastic-Cd co-contaminated soil, biochar unexpectedly promoted Cd uptake by amaranth, with greater Cd accumulation observed under smaller plastic particle sizes. Furthermore, biochar significantly increased amaranth biomass and antioxidant enzyme activity, exhibiting more pronounced effects under conditions of low-dose and large-size plastic contamination. Redundancy analysis and partial least squares path modeling revealed that biochar alleviated co-contamination stress by adsorbing and immobilizing Cd, improving soil physicochemical properties and nutrient availability, suppressing the plastic-heavy metal synergistic effect, and activating the plant antioxidant defence system. In conclusion, rice husk biochar significantly improved soil physicochemical properties, reduced Cd bioavailability, and promoted plant growth in low-dose plastic-Cd co-contaminated soil. For high-dose plastic-Cd contamination, a combined strategy of biochar with phytoremediation is required to enhance Cd immobilization.

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来源期刊
环境科学
环境科学 Environmental Science-Environmental Science (all)
CiteScore
4.40
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0.00%
发文量
15329
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