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施用镉污染稻草后土壤中镉的形态与生物有效性。

Speciation and phytoavailability of cadmium in soil treated with cadmium-contaminated rice straw.

机构信息

Key Laboratory of Agro-ecological Processes in Subtropical Region, Institute of Subtropical Agriculture, Chinese Academy of Sciences, Changsha, Hunan Province, China, 410125.

出版信息

Environ Sci Pollut Res Int. 2015 Feb;22(4):2679-86. doi: 10.1007/s11356-014-3515-2. Epub 2014 Sep 9.

Abstract

When grown on Cd-contaminated soil, rice typically accumulates considerable Cd in straw, and which may return to the soil after harvest. This work was undertaken to assess the pollution risk of Cd associated to the Cd-contaminated rice straw after incorporating into an uncontaminated soil. With the Cd-contaminated rice straw added at 0, 1, 2, 3, 4 and 5 % (w/w), an incubation experiment (28 days) with non-planting and a followed pot experiment sequent with two planting (rice and Chinese cabbage, transplanted after 28-day incubation) were carried out to investigate the changes of soil Cd speciation and phytoavailability. The results indicated that the Cd-contaminated rice straw addition significantly increased soil pH and dissolved organic carbon during the 28-day incubation. For the high availability of Cd in contaminated rice straw, diethylenetriaminepentaacetic acid (DTPA) extractable Cd significantly increased, and the percentages of acetic acid extractable and reducible Cd in soil significantly enhanced after the addition of Cd-contaminated rice straw. However, the Cd-contaminated rice straw addition inhibited the rice growth and induced the decrease of Cd in rice grain and straw by 12.8 to 70.2 % and 39.3 to 57.3 %, respectively, whereas the Cd contents increased by 13.9 to 84.1 % in Chinese cabbage that planted after rice harvest. In conclusion, Cd associated with Cd-contaminated rice straw was highly available after incorporating into the soil, and thus the Cd pollution risk via the Cd-contaminated rice straw incorporation should be evaluated in the Cd-contaminated paddy region.

摘要

当在受镉污染的土壤上种植时,水稻通常会在秸秆中积累相当数量的镉,而这些镉在收获后可能会返回土壤中。本研究旨在评估将受镉污染的水稻秸秆掺入未受污染的土壤后,与镉相关的污染风险。通过添加 0、1、2、3、4 和 5%(w/w)的受镉污染的水稻秸秆进行了 28 天的不种植孵化实验和随后的盆栽实验(在 28 天孵化后种植水稻和白菜),以研究土壤中镉形态和植物可利用性的变化。结果表明,在 28 天的孵化期间,添加受镉污染的水稻秸秆会显著增加土壤 pH 值和溶解性有机碳。由于受污染的水稻秸秆中镉的高生物有效性,二乙三胺五乙酸(DTPA)可提取的镉显著增加,土壤中乙酸可提取和可还原的镉比例在添加受镉污染的水稻秸秆后显著提高。然而,添加受镉污染的水稻秸秆会抑制水稻生长,并导致水稻籽粒和秸秆中的镉含量分别降低 12.8%至 70.2%和 39.3%至 57.3%,而在水稻收获后种植的白菜中,镉含量增加 13.9%至 84.1%。总之,将受镉污染的水稻秸秆掺入土壤后,与镉相关的污染风险很高,因此在镉污染的稻田地区应评估受镉污染的水稻秸秆掺入带来的镉污染风险。

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