Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; University of Chinese Academy of Sciences, Beijing 100049, China.
Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China.
Sci Total Environ. 2022 Feb 1;806(Pt 2):150549. doi: 10.1016/j.scitotenv.2021.150549. Epub 2021 Sep 24.
Pipe scales that form in drinking water distribution systems (DWDS) can accumulate pollutants that may be re-released into bulk water, posing a significant threat to water safety. This study aims to evaluate the pollutant enrichment capacity of the pipe scale and identify speciation changes in heavy metals under variations in water quality. When the water quality conditions changed, the forms of inorganic metal elements in drinking water pipe scales also changed and the proportion of unstable forms increased, thereby increasing the risk of secondary pollution. Morphological analysis showed that the pipe scale samples had porous structures and large specific surface areas (the maximum was 52.94 m/g, which is higher than that of many natural adsorbents), which could promote the accumulation of contaminants. XRD profiles also showed that the pipe scale samples were rich in substances with heavy metal adsorption capacities, such as FeO. As the pH changed from 6 to 10, no significant difference in the release of heavy metals was found. The maximum release of Cu, Cr, As, Pb, and Cd at pH 8 was 0.56, 0.51, 1.82, 0.84, and 0.72 μg/g, respectively. Although the amounts were small, the speciation distribution of the heavy metals changed significantly. In addition, the proportion of unstable fractions increased, which increased the release risk of the pipe scale. The presence of humic acid accelerated the dissolution of organic matter and metals in the pipe scale, which further proved that the pipe scales were unstable and susceptible to water quality conditions. The pipe scales could not maintain stability when the water quality changed, and the DWDS should be regularly monitored and cleaned when necessary.
饮用水配水系统(DWDS)中形成的管垢会积累污染物,这些污染物可能会重新释放到水中,对水安全构成重大威胁。本研究旨在评估管垢的污染物富集能力,并确定水质变化下重金属的形态变化。当水质条件发生变化时,饮用水管垢中无机金属元素的形态也会发生变化,不稳定形态的比例增加,从而增加了二次污染的风险。形态分析表明,管垢样品具有多孔结构和较大的比表面积(最大为 52.94 m/g,高于许多天然吸附剂),这可以促进污染物的积累。XRD 图谱也表明,管垢样品富含具有重金属吸附能力的物质,如 FeO。当 pH 值从 6 变为 10 时,重金属的释放没有明显差异。在 pH 8 时,Cu、Cr、As、Pb 和 Cd 的最大释放量分别为 0.56、0.51、1.82、0.84 和 0.72 μg/g。尽管数量很小,但重金属的形态分布发生了显著变化。此外,不稳定分数的比例增加,增加了管垢的释放风险。腐殖酸的存在加速了管垢中有机物和金属的溶解,进一步证明了管垢的不稳定性和对水质条件的敏感性。当水质发生变化时,管垢无法保持稳定,因此有必要定期监测和清洁 DWDS。