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减少共污染土壤中砷和锑浸出的改良措施评估。

Evaluation of amendments to reduce arsenic and antimony leaching from co-contaminated soils.

作者信息

Doherty Steven J, Tighe Matthew K, Wilson Susan C

机构信息

School of Environmental and Rural Science, University of New England, Armidale, NSW, Australia.

School of Environmental and Rural Science, University of New England, Armidale, NSW, Australia.

出版信息

Chemosphere. 2017 May;174:208-217. doi: 10.1016/j.chemosphere.2017.01.100. Epub 2017 Jan 23.

Abstract

Co-contamination of soils with arsenic (As) and antimony (Sb) presents unique challenges for risk management. In this study a sequence of leaching experiments evaluated zero valent iron powder, ferrihydrite, ferric chloride, aluminium and manganese oxides, and kaolinite for As and Sb immobilisation in co-contaminated soils. Iron based amendments were most effective for the reduction of As and Sb in leachate in a column leaching study. Over 48 h zero valent iron powder and ferrihydrite applied at 3% (w/w dry weight) were most efficient, decreasing total As and Sb leachate concentrations by more than 80%. Careful moderation of pH (to > 2.5 but < ∼6) with lime was required for effective co-immobilisation of both metalloids using ferric chloride. In a subsequent batch study with pH optimised for maximum sorption using 2% lime, ferric chloride (3%) added to two co-contaminated soils decreased As and Sb in solution after 7 days by at least 79%. Ferrihydrite (3%) and iron powder (3%) were less effective. Ferrihydrite (3%) was then used in a 12-week larger scale Cynodon dactylon plant experiment that also considered plant bioavailability. Porewater As and Sb decreased by up to 90% but over the 12 week trial period no significant change in shoot or root metalloid concentrations was observed. The study demonstrates that iron-based amendments can be extremely effective for co-immobilisation of As and Sb in contaminated soils, but for large scale application amendment feasibility considerations and site specific pH moderation are essential.

摘要

土壤中砷(As)和锑(Sb)的共同污染给风险管理带来了独特的挑战。在本研究中,一系列浸出实验评估了零价铁粉、水铁矿、氯化铁、铝和锰的氧化物以及高岭土对共同污染土壤中砷和锑的固定作用。在柱浸实验中,铁基改良剂对降低渗滤液中的砷和锑最为有效。在48小时内,以3%(w/w干重)施用的零价铁粉和水铁矿最为有效,可使砷和锑的总渗滤液浓度降低80%以上。使用氯化铁有效共同固定两种类金属需要用石灰仔细调节pH值(至>2.5但<~6)。在随后的批量研究中,使用2%石灰将pH值优化至最大吸附量,添加到两种共同污染土壤中的3%氯化铁在7天后使溶液中的砷和锑至少降低了79%。3%的水铁矿和3%的铁粉效果较差。然后,3%的水铁矿被用于一项为期12周的更大规模的狗牙根植物实验,该实验也考虑了植物的生物可利用性。孔隙水中的砷和锑最多降低了90%,但在12周的试验期内,地上部或根部类金属浓度没有显著变化。该研究表明,铁基改良剂对污染土壤中砷和锑的共同固定可能极其有效,但对于大规模应用,必须考虑改良剂的可行性以及特定场地的pH调节。

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