Zhao Shengnan, Zhao Yunxi, Cui Zhimou, Zhang Hui, Zhang Jinda
Water Conservancy and Civil Engineering College, Inner Mongolia Agricultural University, Hohhot 010018, China.
Inner Mongolia Water Resource Protection and Utilization Key Laboratory, Hohhot 010018, China.
Toxics. 2024 Jul 5;12(7):494. doi: 10.3390/toxics12070494.
Heavy metals (HMs) in aquatic environments are characterized by high toxicity, a propensity for bioaccumulation, and non-degradability, and pose significant risks to biological communities. Previous studies of HMs in lakes have shown that the physical and chemical characteristics of the lake water may control both the migration of HMs in the sediments and the concentration of heavy metals in the lake water. In fact, the change in aquatic environments changes the heavy metal fraction in the sediment, which controls the release of HMs. In this paper, we investigated the effects of the pH, temperature, and salinity levels of overlying water on the chemical fraction of Cu and Zn in Wuliangsuhai Lake surface sediments. The results show that lower water pH and higher water salinity and temperature could increase Cu and Zn release from the sediment. An increase in pH led to changes in the speciation of solid fractions of Zn, namely increases in the residual fraction and decreases in the organic matter and sulfide, whereas acid-extractable and Fe-Mn oxide fractions remained largely the same. Increases in temperature and salinity led to opposite changes in the speciation of solid fractions, namely decreases in the residual fraction and increases in the organic matter and sulfide and Fe-Mn oxide fractions, whereas acid-extractable fractions remained largely the same. The effect of pH, temperature, and salinity on Cu fractions in the solids was much smaller. According to the ratio of the secondary phase to the primary phase (RSP), acidic, high-temperature, and high-salt conditions increase the release risks of Zn. Changes in water temperature have the greatest influence on the risk of Zn and Cu release from sediments, followed by the influence of salinity changes.
水生环境中的重金属具有高毒性、生物累积倾向和不可降解性,对生物群落构成重大风险。先前对湖泊中重金属的研究表明,湖水的物理和化学特性可能控制着沉积物中重金属的迁移以及湖水中重金属的浓度。事实上,水生环境的变化会改变沉积物中的重金属形态,从而控制重金属的释放。在本文中,我们研究了乌梁素海表层沉积物上覆水的pH值、温度和盐度水平对铜和锌化学形态的影响。结果表明,较低的水体pH值、较高的水体盐度和温度会增加沉积物中铜和锌的释放。pH值升高导致锌固体形态发生变化,即残渣态增加,有机质态和硫化物态减少,而酸可提取态和铁锰氧化物态基本保持不变。温度和盐度升高导致固体形态发生相反变化,即残渣态减少,有机质态、硫化物态和铁锰氧化物态增加,而酸可提取态基本保持不变。pH值、温度和盐度对固体中铜形态的影响要小得多。根据次生相与原生相的比例(RSP),酸性、高温和高盐条件会增加锌的释放风险。水温变化对沉积物中锌和铜释放风险的影响最大,其次是盐度变化的影响。