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生物炭、堆肥、氧化铁、粪肥和无机肥料会影响砷的生物有效性,并改善废弃砷污染金矿废石场的土壤质量。

Biochar, compost, iron oxide, manure, and inorganic fertilizer affect bioavailability of arsenic and improve soil quality of an abandoned arsenic-contaminated gold mine spoil.

作者信息

Mensah Albert Kobina, Marschner Bernd, Shaheen Sabry M, Rinklebe Jörg

机构信息

Department of Soil Science and Soil Ecology, Institute of Geography, Ruhr-Universitaet Bochum, Universitaet Strasse 150, 44801 Bochum, Germany.

University of Wuppertal, School of Architecture and Civil Engineering, Institute of Foundation Engineering, Water, and Waste-Management, Laboratory of Soil, and Groundwater-Management, Pauluskirchstraße 7, 42285 Wuppertal, Germany; King Abdulaziz University, Faculty of Meteorology, Environment, and Arid Land Agriculture, Department of Arid Land Agriculture, Jeddah 21589, Saudi Arabia; University of Kafrelsheikh, Faculty of Agriculture, Department of Soil and Water Sciences, 33516, Kafr El-Sheikh, Egypt.

出版信息

Ecotoxicol Environ Saf. 2022 Apr 1;234:113358. doi: 10.1016/j.ecoenv.2022.113358. Epub 2022 Mar 4.

Abstract

Arsenic (As) contaminated mining spoils pose health threats to environmental resources and humans, and thus, mitigating this potential risk is worth investigating. Here, we studied the impacts of biochar, compost, iron oxide, manure, and inorganic fertilizer on the non-specifically (readily bioavailable)- and specifically- sorbed As and soil quality improvement of an abandoned mine spoil highly contaminated with As (total As = 1807 mg/kg). Compost, iron oxide, manure, and biochar were each applied at 0.5%, 2%, and 5% (w/w) to the contaminated soil; and NPK fertilizer at 0.1, 0.2, and 5.0 g/kg. The non-specifically (readily bioavailable)- and specifically- sorbed As were extracted sequentially and available P, total C and N, dissolved organic carbon, soil soluble anions, and exchangeable cations were extracted after 1- and 28-day incubation. Compost, manure, and biochar at 5% improved the total C and N and exchangeable K, Mg and Na. However, manure, compost, and iron oxide at 5% reduced available P from 118.5 to 60.3, 12.6, and 7.1 mg/kg, respectively. As compared to the untreated soil, the addition of iron oxide doses reduced the readily bioavailable As by 93%; while compost, manure, inorganic fertilizers, and biochar increased it by 106-332%, 24-315%, 19-398%, and 28-47%, respectively, with a significantly higher impact for the 5% doses. Furthermore, compost reduced specifically-sorbed As content (14-37%), but the other amendments did not significantly affect it. The impacts of the amendments on the readily bioavailable As was stronger than on specifically-sorbed As; but these were not affected by the incubation period. Arsenic bioavailability in our soil increased with increasing the soil pH and the contents of Cl, DOC, and exchangeable K and Na. We conclude that iron-rich materials can be used to reduce As bioavailability and to mitigate the associated environmental and human health risk in such mining spoils. However, the carbon-, and P-rich and alkaline materials increased the bioavailability of As, which indicates that these amendments may increase the risk of As, but can be used to enhance phytoextraction efficiency of As in the gold mining spoil.

摘要

受砷(As)污染的采矿废土对环境资源和人类健康构成威胁,因此,减轻这种潜在风险值得研究。在此,我们研究了生物炭、堆肥、氧化铁、粪肥和无机肥料对废弃矿山高砷污染土壤(总砷含量为1807mg/kg)中非特异性(易生物利用)和特异性吸附的砷以及土壤质量改善的影响。将堆肥、氧化铁、粪肥和生物炭分别以0.5%、2%和5%(w/w)的比例施用于污染土壤;将氮磷钾肥料分别以0.1、0.2和5.0g/kg的用量施用。在培养1天和28天后,依次提取非特异性(易生物利用)和特异性吸附的砷,并提取有效磷、总碳和氮、溶解有机碳、土壤可溶性阴离子和交换性阳离子。5%的堆肥、粪肥和生物炭提高了总碳和氮以及交换性钾、镁和钠的含量。然而,5%的粪肥、堆肥和氧化铁分别将有效磷含量从118.5mg/kg降至60.3mg/kg、12.6mg/kg和7.1mg/kg。与未处理土壤相比,添加氧化铁剂量使易生物利用的砷减少了93%;而堆肥、粪肥、无机肥料和生物炭分别使其增加了106% - 332%、24% - 315%、19% - 398%和28% - 47%,5%剂量的影响显著更高。此外,堆肥降低了特异性吸附的砷含量(14% - 37%),但其他改良剂对其影响不显著。改良剂对易生物利用砷的影响比对特异性吸附砷的影响更强;但这些不受培养期的影响。我们土壤中的砷生物有效性随着土壤pH值以及氯、溶解有机碳和交换性钾、钠含量的增加而增加。我们得出结论,富铁材料可用于降低砷的生物有效性,并减轻此类采矿废土中相关的环境和人类健康风险。然而,富含碳、磷和碱性的材料增加了砷的生物有效性,这表明这些改良剂可能会增加砷的风险,但可用于提高金矿废土中砷的植物提取效率。

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