Department of Geochemistry, Geological Survey of Denmark and Greenland (GEUS), Øster Voldgade 10, Copenhagen1350, Denmark.
Department of Plant and Environmental Sciences, University of Copenhagen, Thorvaldsensvej 40, 1871 Frederiksberg C, Denmark.
Environ Sci Technol. 2024 Jun 25;58(25):11175-11184. doi: 10.1021/acs.est.4c00939. Epub 2024 Jun 10.
Arsenic (As)-bearing Fe(III) precipitate groundwater treatment sludge has traditionally been viewed by the water sector as a disposal issue rather than a resource opportunity, partly due to assumptions of the low value of As. However, As has now been classified as a Critical Raw Material (CRM) in many regions, providing new incentives to recover As and other useful components of the sludge, such as phosphate (P) and the reactive hydrous ferric oxide (HFO) sorbent. Here, we investigate alkali extraction to separate As from a variety of field and synthetic As-bearing HFO sludges, which is a critical first step to enable sludge upcycling. We found that As extraction was most effective using NaOH, with the As extraction efficiency increasing up to >99% with increasing NaOH concentrations (0.01, 0.1, and 1 M). Extraction with NaCO and Ca(OH) was ineffective (<5%). Extraction time (hour, day, week) played a secondary role in As release but tended to be important at lower NaOH concentrations. Little difference in As extraction efficiency was observed for several key variables, including sludge aging time (50 days) and cosorbed oxyanions (e.g., Si, P). However, the presence of ∼10 mass% calcite decreased As release from field and synthetic sludges considerably (<70% As extracted). Concomitant with As release, alkali extraction promoted crystallization of poorly ordered HFO and decreased particle specific surface area, with structural modifications increasing with NaOH concentration and extraction time. Taken together, these results provide essential information to inform and optimize the design of resource recovery methods for As-bearing treatment sludge.
含砷(As)的三价铁沉淀物地下水处理污泥一直被水务部门视为一个处置问题,而不是一个资源机会,部分原因是假设 As 的价值较低。然而,As 现在已在许多地区被归类为关键原材料(CRM),这为回收 As 和污泥中的其他有用成分(如磷酸盐(P)和反应性水合氧化铁(HFO)吸附剂)提供了新的激励。在这里,我们研究了碱提取来分离各种现场和合成含 As 的 HFO 污泥中的 As,这是实现污泥升级利用的关键第一步。我们发现,使用 NaOH 进行 As 提取最为有效,随着 NaOH 浓度(0.01、0.1 和 1 M)的增加,As 的提取效率增加到>99%。使用 NaCO 和 Ca(OH)2 提取效果不佳(<5%)。提取时间(小时、天、周)在 As 释放中起次要作用,但在较低的 NaOH 浓度下往往很重要。在几个关键变量中,包括污泥老化时间(50 天)和共吸附的含氧阴离子(如 Si、P),As 提取效率几乎没有差异。然而,存在约 10%质量%的方解石会大大降低来自现场和合成污泥的 As 释放量(<70%的 As 被提取)。与 As 释放同时发生的是,碱提取促进了无序 HFO 的结晶并降低了颗粒比表面积,随着 NaOH 浓度和提取时间的增加,结构改性增加。总之,这些结果提供了必要的信息,为含 As 处理污泥的资源回收方法的设计提供信息和优化。