Laboratório de Biologia Genômica e Molecular, Pontifícia Universidade Católica do Rio Grande do Sul (PUCRS). Av. Ipiranga, 6681. CEP: 90.619.900, Porto Alegre, RS, Brazil; Programa de Biologia Celular e Molecular, Escola de Ciências da Saúde e da Vida, PUCRS. Av. Ipiranga, 6681. CEP: 90.619.900, Porto Alegre, RS, Brazil.
Laboratório de Tecnologia Mineral e Ambiental, Programa de Pós-Graduação em Engenharia de Minas, Metalúrgica e de Materiais, Escola de Engenharia, Universidade Federal do Rio Grande do Sul (UFRGS). Av. Bento Gonçalves, 9500. CEP-91501-970, Porto Alegre, RS, Brazil.
Chemosphere. 2020 Aug;253:126665. doi: 10.1016/j.chemosphere.2020.126665. Epub 2020 Apr 3.
Acid mine drainage (AMD) represents a major problem in the mining industry worldwide due to the risk of water and soil pollution. Its active treatment involves the addition of alkaline reagents such as NaOH or Ca(OH) to increase the pH and precipitate the dissolved metals, although substantial amounts of dissolved ions might persists. Under a remediation approach, the aim of this work was to assess the chemical and physical characteristics of treated effluent and to evaluate its ecotoxicological effects on zebrafish (Danio rerio) embryonic and larval stages, through developmental, functional, morphological, and behavioral end-points. The studied AMD sample, highly associated with pyrite, presented high sulfate and dissolved metal ions content and was submitted to the following treatment conditions: NaOH - pH 7.0 and 8.7, and Ca(OH) - pH 7.0 and 8.7. All neutralizing treatments resulted in a satisfactory reduction of the metals concentration, with best results achieved using Ca(OH) at pH 8.7; although Mn and As still remained above or very near the discharge maximum limits according to Brazilian legislation. Therefore, an additional step was employed to Mn and As adsorption by algal biomass. Regarding in-vivo toxicological assays, no significant lethality was recorded in all treated AMD groups, although adverse effects were observed in all endpoints analyzed. Ca(OH) groups performed closer to control than NaOH-treated groups. The additional polishing stage treatment with the algae Scenesmus sp. allowed tenuous improvements in terms of removal of residual amounts of As and Mn but not in the toxicological characteristics of treated AMD.
酸性矿山排水 (AMD) 是全球采矿业面临的一个主要问题,因为它存在水污染和土壤污染的风险。其活性处理涉及添加碱性试剂,如 NaOH 或 Ca(OH),以提高 pH 值并沉淀溶解的金属,尽管仍可能存在大量溶解的离子。在修复方法中,这项工作的目的是评估处理后的废水的化学和物理特性,并通过发育、功能、形态和行为终点评估其对斑马鱼 (Danio rerio) 胚胎和幼虫阶段的生态毒性影响。研究的 AMD 样本与黄铁矿高度相关,具有高硫酸盐和溶解金属离子含量,并经历了以下处理条件:NaOH - pH 7.0 和 8.7,以及 Ca(OH) - pH 7.0 和 8.7。所有中和处理都导致金属浓度的显著降低,使用 Ca(OH) 在 pH 8.7 时效果最佳;尽管 Mn 和 As 的浓度仍高于或非常接近巴西法规规定的排放最大值。因此,采用了另一个步骤来吸附 Mn 和 As,使用藻类生物质。关于体内毒理学试验,所有处理过的 AMD 组均未记录到显著的致死率,但在分析的所有终点都观察到了不良反应。与 NaOH 处理组相比,Ca(OH)组更接近对照组。用藻类 Scenesmus sp.进行的额外抛光处理在去除残余 As 和 Mn 方面略有改善,但对处理后的 AMD 的毒理学特性没有影响。