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牛粪负载生物炭改变了自然酸化污染土壤中小麦对镉形态的分馏和植物毒性。

Cow manure-loaded biochar changes Cd fractionation and phytotoxicity potential for wheat in a natural acidic contaminated soil.

机构信息

Key Laboratory of Aquatic Botany and Watershed Ecology, Wuhan Botanical Garden, Chinese Academy of Science, Wuhan 430074, China; China Program of International Plant Nutrition Institute, Wuhan 430074, China; Soils and Water Department, Faculty of Agriculture, Benha University, Moshtohor, Toukh, Kalyoubia 13736, Egypt; Graduate University, Chinese Academy of Sciences, Beijing 100049, China.

Soils and Water Department, Faculty of Agriculture, Benha University, Moshtohor, Toukh, Kalyoubia 13736, Egypt.

出版信息

Ecotoxicol Environ Saf. 2018 Oct 30;162:348-353. doi: 10.1016/j.ecoenv.2018.06.065. Epub 2018 Jul 11.

Abstract

The current study aims to investigate the implications of amending a soil contaminated with Cd with peanut residues biochar (BP) solely or in combination with cow manure (CMPB) at different rates on phytotoxicity of Cd for wheat plants and its distribution in a mine contaminated soil. Soil pH and EC increased progressively in soils amended with either PB or CMPB. Exchangeable Cd was decreased while its non-exchangeable fractions were increased. Dry weights of wheat straw, roots and grains increased when soils amended with either PB or CMPB, especially at the higher application rate. Such increases were correlated significantly with the extractable soil-Cd. Concentrations of Cd in roots were higher than those in straw; whereas, the concentrations in grains seemed to be the lowest. Generally, values of bio-concentration and translocation factors did not exceed "1" and decreased with application of either PB or CMPB. In conclusion, enriching biochar with cow manure is a recommended strategy to reduce Cd uptake and translocation to straw and seeds. Moreover, Concentrations of Cd did not exceed the permissible levels in grains when soils amended with the highest rate of CMPB.

摘要

本研究旨在探讨在不同比例下,仅用或结合花生残渣生物炭(BP)和牛粪(CMPB)来改良受 Cd 污染的土壤对小麦植株 Cd 毒性及其在矿区污染土壤中分布的影响。在添加 PB 或 CMPB 的土壤中,土壤 pH 值和电导率逐渐增加。可交换态 Cd 减少,而非交换态 Cd 增加。添加 PB 或 CMPB 的土壤中,小麦秸秆、根系和籽粒的干重均增加,尤其是在较高的添加率下。这种增加与可提取土壤 Cd 显著相关。根系中 Cd 的浓度高于秸秆中的浓度,而籽粒中的浓度似乎最低。一般来说,生物浓缩和迁移系数的值不超过“1”,并随 PB 或 CMPB 的添加而降低。综上所述,用牛粪来丰富生物炭是一种减少 Cd 吸收和向秸秆和种子迁移的推荐策略。此外,当添加最高比例的 CMPB 时,土壤中 Cd 的浓度未超过谷物的允许水平。

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