School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan, Hubei, 430074, PR China; Hubei Provincial Engineering Laboratory of Solid Waste Treatment, Disposal and Recycling, Wuhan, Hubei, 430074, PR China; Tsinghua-Berkeley Shenzhen Institute, Tsinghua University, Shenzhen, Guangdong, 518055, PR China; Tsinghua Shenzhen International Graduate School, Tsinghua University, Shenzhen, Guangdong, 518055, PR China.
School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan, Hubei, 430074, PR China; Hubei Provincial Engineering Laboratory of Solid Waste Treatment, Disposal and Recycling, Wuhan, Hubei, 430074, PR China.
Chemosphere. 2023 Jan;312(Pt 2):137063. doi: 10.1016/j.chemosphere.2022.137063. Epub 2022 Nov 14.
Arsenic-alkali residue (AAR) from antimony production can pose significant health and environmental hazards due to the risk of arsenic (As) leaching. In this study, geopolymer composite synthesized from fly ash (FA) was investigated for efficient stabilization of high-arsenic-containing AAR (AsO of 22.74 wt%). Two industrial wastes, e.g., granulated blast furnace slag (GBFS) with active calcium composition and water-quenched slag (WQS) from lead-zinc smelting with active iron composition, were investigated for the reinforcement of AAR geopolymer solidification. A wide pH stabilization (from pH = 3-pH = 12) of AAR with the geopolymer composite was successfully achieved, and As leaching concentration of geopolymer with the addition of 5 wt% AAR was significantly reduced from 2343.73 mg/L (AAR) to that below 0.18 mg/L, which successfully meet the regulatory limit of Chinese domestic waste landfill (GB, 18598-2019, 1.2 mg/L) and hazardous waste landfill (GB16889-2008, 0.3 mg/L). Johnbaumite (Ca(AsO)(OH)) was formed in geopolymer composite and leached samples with initial pH from 2.6 to 6 (final pH from 5.54 to 13.15). Magnetite and iron hydroxide phases with strong adsorption and/or As co-precipitation capability were also observed. As stabilization was also achieved with iron oxidation from As(III) to As(V). This study solves the problem of unstable As leaching at different pH for the solidification of arsenic-bearing solid waste, and provides a promising and practical strategy for efficient solidification/stabilization of AAR as well as other similar arsenic-bearing solid wastes with geopolymer composite.
砷碱渣(AAR)来自锑生产,由于砷(As)浸出的风险,会对健康和环境造成重大危害。在这项研究中,从粉煤灰(FA)合成的地质聚合物复合材料被用于高效稳定高含砷 AAR(AsO 为 22.74wt%)。研究了两种工业废料,即具有活性钙成分的粒化高炉矿渣(GBFS)和具有活性铁成分的铅锌冶炼水淬渣(WQS),以增强 AAR 地质聚合物固化。成功地实现了 AAR 的宽 pH 稳定(pH=3-pH=12),并且添加 5wt%AAR 的地质聚合物中 As 的浸出浓度从 2343.73mg/L(AAR)显著降低到低于 0.18mg/L,成功满足了中国国内废物填埋场(GB,18598-2019,1.2mg/L)和危险废物填埋场(GB16889-2008,0.3mg/L)的法规限制。在地质聚合物复合材料和浸出样品中形成了钙砷石(Ca(AsO)(OH)),初始 pH 值从 2.6 到 6(最终 pH 值从 5.54 到 13.15)。还观察到具有强吸附和/或 As 共沉淀能力的磁铁矿和氢氧化铁相。As 的稳定化也通过 As(III)氧化为 As(V)来实现。这项研究解决了含砷固体废物固化过程中不同 pH 值下不稳定的 As 浸出问题,为地质聚合物复合材料有效固化/稳定 AAR 以及其他类似含砷固体废物提供了一种有前景和实用的策略。