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Alternative Method for the Treatment of Hydrometallurgical Arsenic–Calcium Residues: The Immobilization of Arsenic as Scorodite

机译:液压冶金砷 - 钙残基治疗的替代方法:砷作为焦散岩的固定化

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Arsenic–calcium residue (ACR) is one of the major hazardous solid wastes produced by the metallurgical industry that poses a serious threat to the environment. However, a suitable method for the effective treatment of ACR is still lacking. In this study, an alternative treatment method for ACRs via the immobilization of As as scorodite was proposed with the use of two types of ACRs (ACR_(real) directly collected from a Pb refinery and ACR_(lab) precipitated from waste sulfuric acid in the lab). The treatment of ACR included preparing the As-enriched solution via H_(2)SO_(4) dissolution–neutralization of ACR at pH < 2, As(III) was oxidized by H_(2)O_(2), and As(V) was immobilized as scorodite. The results showed that gypsum produced from ACR_(lab) in the dissolution–neutralization process contained 68 mg/kg of As, far below the Chinese national standard for hazardous solid wastes (<0.1 wt %, GB5085.62007). The gypsum produced from ACR_(real) contained 5400 mg/kg of As due to the presence of original high-As gypsum (1.6 wt %) in ACR_(real). These results showed that the preliminary removal of SO_(4)~(2–) from waste sulfuric acid by lime neutralization–precipitation at pH ~ 2 could produce pure-phase gypsum by avoiding the HAsO_(4)~(2–) isomorphic substitution for SO_(4)~(2–). The scorodite produced from both ACRs displayed good As stability at pH 4.95 (0.9 and 0.5 mg/L) via the toxicity characteristic leaching procedure (TCLP) method and at pH 3–7 (0.4–3.0 mg/L) via a 15 day short-term stability test.
机译:砷 - 钙渣(ACR)是由冶金行业生产的主要危险固体废物之一,对环境构成严重威胁。然而,仍然缺乏对ACR的有效治疗的合适方法。在该研究中,通过使用两种类型的分组(ACR_(REAL)直接从来自废硫酸中沉淀的PB炼油厂直接收集的ACRS(ACR_(REAL)的固定化的ACRS的替代处理方法。实验室)。 ACR的处理包括通过H×(2)SO_(4)在pH <2时通过H_(2)SO_(4)溶解中和的溶解 - 用H_(2)o_(2)氧化(III),以及(v )被固定为焦散岩。结果表明,由溶出 - 中和过程中的ACR_(实验室)产生的石膏含有68毫克/千克,远低于中国国家危险固体废物的国家标准(<0.1wt%,GB5085.62007)。由ACR_(REAL)产生的石膏包含5400mg / kg,因为ACR_(REAL)中的原始高可石膏(1.6wt%)存在。这些结果表明,通过在pH〜2下通过石灰中和沉淀从废硫酸中初步除去SO_(4)〜(2-)可以通过避免哈索(4)〜(2-)正像替代来产生纯相石膏对于SO_(4)〜(2-)。通过毒性特征浸出程序(TCLP)方法和pH 3-7(0.4-3.0mg / L)在pH 4.95(0.9和0.5mg / L)下,从两种输出的稳定性均匀地显示出良好的稳定性。 - 稳定性测试。

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