Liu Yingying, Wu Pingxiao, Chen Meiqing, Wang Tianming, Sun Leiye, Lu Bingxin, Zhu Nengwu, Dang Zhi
School of Environment and Energy, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006, PR China.
School of Environment and Energy, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006, PR China; The Key Lab of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, Guangzhou 510006, PR China; Guangdong Provincial Key Laboratory of Solid Wastes Pollution Control and Recycling, Guangzhou 510006, PR China; Guangdong Engineering and Technology Research Center for Environmental Nanomaterials, Guangzhou 510006, PR China.
Sci Total Environ. 2024 Dec 1;954:176537. doi: 10.1016/j.scitotenv.2024.176537. Epub 2024 Sep 26.
The widespread mining and application of rare earth elements (REEs) have led to their continuous accumulation in the environment, with increasing concentrations in soil. The interaction between the most abundant REEs, cerium (Ce), and the prevalent hexagonal birnessite (HB) in the environment is worth attention. HB is one of the most effective metal oxides for the oxidation of arsenite [As(III)] and subsequent adsorption, and thus for arsenic (As) immobilization. Therefore, in this study, we investigated the effect of the presence of Ce(III) ion on the HB formation process and the influence of generating minerals on the oxidation and removal of As(III). Research has found that the interfacial reactions of REEs in manganese (Mn) minerals not only affect their cycling but also alter the properties of the Mn minerals, thereby affecting the environmental fate of As. The results indicated that the presence of Ce ions affected the structure of HB during mineral synthesis and reduced the crystallinity of the conversion products. Their substitution for Mn(IV) in the lattice increased the specific surface area of minerals, reduced particle size, and produced more hydroxyl groups that were conducive to the immobilization of As(III). Meanwhile, Ce(III) was oxidized to Ce(IV) during the formation of Ce-bearing hexagonal birnessite (Ce-HB), and CeO nanoparticles were formed on the mineral surface and the removal rate of As(III) by Ce-HB was greatly improved. When the As concentration was lower than 6 mg·L, the removal effect of Ce-HB could reach the drinking water standard. However, the oxidation rate decreased due to the decrease in the proportion of Mn(IV). This study fundamentally reveals the behavior of HB coexisting with Ce in the migration and transformation of As(III) in the environment.
稀土元素(REEs)的广泛开采和应用导致其在环境中不断积累,土壤中的浓度也在增加。环境中含量最高的稀土元素铈(Ce)与普遍存在的六方水钠锰矿(HB)之间的相互作用值得关注。HB是氧化亚砷[As(III)]并随后进行吸附从而固定砷(As)的最有效金属氧化物之一。因此,在本研究中,我们研究了Ce(III)离子的存在对HB形成过程的影响以及生成的矿物对As(III)氧化和去除的影响。研究发现,稀土元素在锰(Mn)矿物中的界面反应不仅影响它们的循环,还会改变锰矿物的性质,从而影响As的环境归宿。结果表明,Ce离子的存在在矿物合成过程中影响了HB的结构,降低了转化产物的结晶度。它们在晶格中取代Mn(IV)增加了矿物的比表面积,减小了粒径,并产生了更多有利于固定As(III)的羟基。同时,在含铈六方水钠锰矿(Ce-HB)形成过程中Ce(III)被氧化为Ce(IV),并在矿物表面形成CeO纳米颗粒,Ce-HB对As(III)的去除率大大提高。当As浓度低于6 mg·L时,Ce-HB的去除效果可达到饮用水标准。然而,由于Mn(IV)比例的降低,氧化速率下降。本研究从根本上揭示了HB与Ce共存时As(III)在环境中迁移转化的行为。