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Effect of bamboo and rice straw biochars on the mobility and redistribution of heavy metals (Cd, Cu, Pb and Zn) in contaminated soil

机译:竹稻稻秸秆生物炭对污染土壤中重金属(Cd,Cu,Pb和Zn)迁移率和再分布的影响

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摘要

Biochar has emerged as an efficient tool to affect bioavailability of heavy metals in contaminated soils. Although partially understood, a carefully designed incubation experiment was performed to examine the effect of biochar on mobility and redistribution of Cd, Cu, Pb and Zn in a sandy loam soil collected from the surroundings of a copper smelter. Bamboo and rice straw biochars with different mesh sizes (<0.25 mm and <1 mm), were applied at three rates (0,1, and 5% w/w). Heavy metal concentrations in pore water were determined after extraction with 0.01 M CaCl_2. Phytoavailable metals were extracted using DTPA/TEA (pH 7.3). The European Union Bureau of Reference (EUBCR) sequential extraction procedure was adopted to determine metal partitioning and redistribution of heavy metals. Results showed that CaCl_2-and DTPA-extractable Cd, Cu, Pb and Zn concentrations were significantly (p < 0.05) lower in the bamboo and rice straw biochar treated soils, especially at 5% application rate, than those in the unamended soil. Soil pH values were significantly correlated with CaCl_2-extractable metal concentrations (p < 0.01). The EUBCR sequential extraction procedure revealed that the acid extractable fractions of Cd, Cu, Pb and Zn decreased significantly (p < 0.05) with biochar addition. Rice straw biochar was more effective than bamboo biochar in decreasing the acid extractable metal fractions, and the effect was more pronounced with increasing biochar application rate. The effect of biochar particle size on extractable metal concentrations was not consistent. The 5% rice straw biochar treatment reduced the DTPA-extractable metal concentrations in the order of Cd < Cu < Pb < Zn, and reduced the acid extractable pool of Cd, Cu, Pb and Zn by 11,17, 34 and 6%, respectively, compared to the control. In the same 5% rice straw biochar treatments, the organic bound fraction increased by 37, 58, 68 and 18% for Cd, Cu, Pb and Zn, respectively, compared to the control, indicating that the immobilized metals were mainly bound in the soil organic matter fraction. The results demonstrated that the rice straw biochar can effectively immobilize heavy metals, thereby reducing their mobility and bioavailability in contaminated soils.
机译:生物炭已经成为影响受污染土壤中重金属生物利用度的有效工具。尽管部分理解,但进行了精心设计的孵化实验,以检查生物炭对从铜冶炼厂周围收集的砂壤土中Cd,Cu,Pb和Zn的迁移率和再分布的影响。以三种比率(0.1和5%w / w)施用具有不同筛目尺寸(<0.25 mm和<1 mm)的竹和稻草生物炭。用0.01 M CaCl_2萃取后,测定孔隙水中的重金属浓度。使用DTPA / TEA(pH 7.3)提取植物可用金属。采用了欧盟参考局(EUBCR)的顺序提取程序来确定重金属的金属分配和再分配。结果表明,在竹炭和稻草秸秆生物炭处理过的土壤中,CaCl_2和DTPA可提取的Cd,Cu,Pb和Zn浓度显着降低(p <0.05),特别是在5%施用量下,比未经改良的土壤要低。土壤pH值与CaCl_2可提取的金属浓度显着相关(p <0.01)。 EUBCR顺序萃取程序显示,添加生物炭后,Cd,Cu,Pb和Zn的可酸萃取级分显着降低(p <0.05)。稻草生物炭比竹生物炭在减少酸可提取金属组分方面更有效,并且随着生物炭施用量的增加,效果更明显。生物炭粒度对可提取金属浓度的影响不一致。 5%稻草生物炭处理降低了DTPA可萃取金属的浓度,按Cd <Cu <Pb <Zn的顺序,将Cd,Cu,Pb和Zn的酸可萃取池减少了11,17、34和6%,分别与对照进行比较。在相同的5%稻草生物炭处理中,与对照相比,Cd,Cu,Pb和Zn的有机结合率分别增加了37%,58%,68%和18%,这表明固定化的金属主要结合在土壤中。土壤有机质分数。结果表明,稻草生物炭可以有效地固定重金属,从而降低其在污染土壤中的迁移率和生物利用度。

著录项

  • 来源
    《Journal of Environmental Management》 |2017年第2期|285-292|共8页
  • 作者单位

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China;

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China;

    Scion, Private Bag 3020, Rotorua 3046, New Zealand;

    Global Institute for Environmental Research, The University of Newcastle, University Drive, Callaghan, NSW 2308, Australia;

    Korea Biochar Research Center, Kangwon National University, Chuncheon 24341, South Korea;

    Institute of Soil and Environmental Sciences, University of Agriculture Faisalabad, Faisalabad 38040, Pakistan;

    School of Environmental and Chemical Engineering, Foshan University, Foshan, Guangdong 528000, China;

    Guangdong Dazhong Agriculture Science Co. Ltd., Hongmei Town, Dongguan City, Guangdong 523169, China;

    School of Environmental and Chemical Engineering, Foshan University, Foshan, Guangdong 528000, China;

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China;

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China;

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China;

    Guangdong Dazhong Agriculture Science Co. Ltd., Hongmei Town, Dongguan City, Guangdong 523169, China;

    Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A&F University, Lin'an, Hangzhou, Zhejiang 311300, China,School of Environmental and Chemical Engineering, Foshan University, Foshan, Guangdong 528000, China,Guangdong Dazhong Agriculture Science Co. Ltd., Hongmei Town, Dongguan City, Guangdong 523169, China;

  • 收录信息 美国《科学引文索引》(SCI);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Biochar; Heavy metals; Sequential extraction; Soil remediation; Stabilization;

    机译:生物炭重金属;顺序提取;土壤修复;稳定化;

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