ORISE Postdoctoral Fellow at U.S. Environmental Protection Agency. ORD, CESER, WID, DWMB, 26 W. Martin Luther King Drive, Cincinnati, OH 45268, USA.
U.S. Environmental Protection Agency. ORD, CESER, WID, DWMB, 26 W. Martin Luther King Drive, Cincinnati, OH 45268, USA.
Water Res. 2021 Apr 15;194:116942. doi: 10.1016/j.watres.2021.116942. Epub 2021 Feb 18.
Various iron oxyhydroxide and oxide minerals commonly found in old cast iron pipe scale were shown to exhibit high and similar affinity for arsenate [As(V)] and orthophosphate (PO) via adsorption, co-precipitation, and other factors. PO is a common drinking water corrosion inhibitor. This 7.5-year study examined the accumulation and release of As from an old cast iron pipe scale by changing initial As(V) (0, 75, or 180 µg/L as As) and initial PO (0 or 3 mg/L as PO) levels in the simulated drinking water. The results showed that sites within the iron scale accumulated As with a large capacity and concentrated 27% of the total amount As in water into the scale during the 7.5-year study. When no PO was added, the As accumulation followed a linear regression model with an accumulation rate of 0.27/hr (R = 0.80, p < 0.001), and higher initial As level of 180 µg/L (vs 75 µg/L) resulted in 2.3-3 times larger As accumulation rate at 0.25 mg/day (vs 0.084-0.11 mg/day). As much as 44 µg/L As was released back to water following the changes in the initial As and PO concentrations in water. Addition of 3 mg/L PO caused a rapid increase in As release from iron scale that gradually dropped off with time while PO was incorporated into the scale and most PO remained tightly bound to certain iron scale sites. Proactive measures such as sampling for As in the distribution systems following PO corrosion control treatment changes would help identify exposure risks.
各种常见于旧铸铁管水垢中的铁氧氢氧化物和氧化物矿物通过吸附、共沉淀和其他因素表现出对砷酸盐[As(V)]和正磷酸盐(PO)的高亲和性。PO 是一种常见的饮用水腐蚀抑制剂。这项为期 7.5 年的研究通过改变模拟饮用水中初始 As(V)(0、75 或 180 µg/L 作为 As)和初始 PO(0 或 3 mg/L 作为 PO)水平,考察了旧铸铁管水垢中砷的积累和释放。结果表明,水垢中的点位具有很大的砷积累能力,在 7.5 年的研究期间,将水中 27%的总砷量浓缩到水垢中。当不添加 PO 时,砷的积累遵循线性回归模型,积累速率为 0.27/hr(R=0.80,p<0.001),较高的初始 As 水平为 180 µg/L(与 75 µg/L 相比)导致 0.25 mg/天(与 0.084-0.11 mg/天相比)的砷积累速率增加 2.3-3 倍。随着初始 As 和 PO 浓度在水中的变化,多达 44 µg/L 的 As 被释放回水中。添加 3 mg/L 的 PO 会导致铁垢中砷的迅速释放,随着时间的推移逐渐下降,而 PO 则被纳入到水垢中,并且大部分 PO 仍然与某些铁垢点位紧密结合。在实施 PO 腐蚀控制处理变化后,对分配系统中的 As 进行采样,可以帮助识别暴露风险。