University of Limerick, Department of Biological Sciences & The Bernal Institute, Co., Limerick, Ireland.
Rio Tinto Closure, Paris, France.
Sci Total Environ. 2020 Jan 1;698:134344. doi: 10.1016/j.scitotenv.2019.134344. Epub 2019 Sep 7.
Around 3 billion tonnes of bauxite residue (BR), the by-product of alumina extraction, have been produced and stockpiled worldwide, representing a potential risk for the environment due to the high alkalinity and the presence of relatively high concentrations of trace elements. Phytoremediation (or simply revegetation) is regarded as the most promising in situ remediation option to mitigate the environmental risk that might arise from the land-disposal of BR. Rehabilitation strategies (including the incorporation of amendments such as gypsum and organic matter) have been employed to address the main limitations to plant establishment and growth on BR, typically the high alkalinity, salinity and sodicity. However, the potential for trace element uptake and phytotoxicity have been largely unreported in revegetated BRs. In order to assess the ecotoxicological risk, samples of previously revegetated BR were collected from the field, characterized in the laboratory, and used to conduct ex-situ plant bioassays (Phytotoxkit™ and the RHIZOtest). Without rehabilitation, fresh BR severely inhibits seed germinationand root/shoot development in test species Lepidium sativum, Sinapis alba and Sorghum saccharatum. Plant uptake for Al, As, Cr, V was assessed with RHIZOtest bioassay trials with Lolium perenne and demonstrated that plants exposed to fresh BR take up and translocated trace elements to their shoots at concentrations (As = 4.13 mg/kg dm; Cr = 3.29 mg/kg dm; V = 85.66 mg/kg dm) exceeding phytotoxic levels (vanadium) or maximum levels specified for animal feed (arsenic), showing visible stress symptoms in the seedlings. Conversely, revegetated BR show improved chemical properties, allow seed germination, and permits seedling growth with no evidence of trace element phytotoxicity. However, Na can be taken up at concentrations that could elicit phytotoxicity and impair the success of revegetation. For future rehabilitation programmes, direct revegetation on BR after the incorporation of amendments such as gypsum and organic matter is recommended.
全世界已产生并储存了约 30 亿吨铝土矿残渣(BR),这是氧化铝提取的副产品,由于其高碱性和痕量元素浓度相对较高,因此对环境构成潜在风险。植物修复(或简称植被恢复)被认为是减轻 BR 土地处置可能带来的环境风险的最有前途的原位修复选择。修复策略(包括添加石膏和有机物等改良剂)已被用于解决在 BR 上植物定植和生长的主要限制因素,通常是高碱性、盐度和钠含量。然而,在植被恢复的 BR 中,痕量元素的吸收和植物毒性的潜力在很大程度上尚未得到报道。为了评估生态毒性风险,从现场采集了先前植被恢复的 BR 样本,在实验室进行了表征,并用于进行离体植物生物测定(Phytotoxkit™ 和 RHIZOtest)。未经修复,新鲜 BR 严重抑制测试物种生菜、油菜和高粱的种子发芽和根/茎发育。使用 RHIZOtest 生物测定试验对 Lolium perenne 进行了 Al、As、Cr、V 的植物吸收评估,结果表明,暴露于新鲜 BR 的植物吸收并将痕量元素转移到其茎中,浓度(As=4.13mg/kg dm;Cr=3.29mg/kg dm;V=85.66mg/kg dm)超过了植物毒性水平(钒)或动物饲料规定的最大水平(砷),在幼苗中表现出明显的胁迫症状。相反,植被恢复的 BR 显示出改善的化学性质,允许种子发芽,并允许幼苗生长,没有痕量元素植物毒性的证据。然而,Na 可以在可能引起植物毒性并损害植被恢复成功的浓度下被吸收。对于未来的修复计划,建议在添加石膏和有机物等改良剂后直接在 BR 上进行植被恢复。