Architectural and Environmental Engineering, The University of Texas, Austin, Texas, USA.
Environ Toxicol Chem. 2011 Aug;30(8):1775-84. doi: 10.1002/etc.584. Epub 2011 Jun 7.
The effects of dynamic changes in pH and salinity on metal speciation and release are investigated with sediments posed in a simulated estuarine environment. The release of Zn, Cd, Mn, and Fe was studied using sediment from the Anacostia River (Washington, DC, USA) spiked with freshly precipitated amorphous cadmium sulfide to increase Cd content. The sediment was exposed to salt water (high pH, ionic strength) and freshwater (neutral pH, minimal ionic strength) continuously and alternately (to mimic tidal changes) in small microcosms over 100 d. At the conclusion of the experiments, the vertical profiles of acid volatile sulfide (AVS) and simultaneously extracted metals (SEM) as well as porewater metals and anion concentrations were characterized. Acid volatile sulfide oxidation at the sediment surface led to a commensurate increase in dissolved metal species and metal release that was strongly dependent on the changes in the overlying water characteristics. Total Cd release was substantially higher during exposure to salt water, although, as a result of complexation, predicted dissolved Cd(2+) concentration in the overlying water was higher during exposure to freshwater. Total Zn release was little changed during exposure to salt water and freshwater, although the predicted dissolved Zn(2+) concentration was much higher during freshwater exposures. No significant iron was released because of the rapid oxidation of ferrous iron (Fe(2+)) in aerobic surficial sediments and overlying water. The present study suggests that cyclic changes in pH and salinity in the overlying water can dramatically influence metal release from estuarine sediments.
采用模拟河口环境下的沉积物来研究 pH 值和盐度的动态变化对金属形态和释放的影响。使用从美国华盛顿特区的阿纳科斯蒂亚河采集的沉积物进行研究,向其中添加新沉淀的无定形硫化镉以增加 Cd 含量。将沉积物暴露于咸水(高 pH 值、离子强度)和淡水(中性 pH 值、最小离子强度)中,并连续且交替(模拟潮汐变化)在小的微环境中进行 100 天。在实验结束时,对酸可挥发性硫化物(AVS)和同时提取的金属(SEM)以及孔隙水金属和阴离子浓度的垂直分布进行了表征。沉积物表面的酸可挥发性硫化物氧化导致溶解金属物种和金属释放的相应增加,这强烈依赖于上覆水特征的变化。尽管由于螯合作用,在暴露于淡水中时,预测的上覆水中溶解的 Cd(2+)浓度更高,但在暴露于咸水中时,总 Cd 的释放量要高得多。在暴露于咸水和淡水时,总 Zn 的释放量变化不大,尽管在淡水暴露时预测的溶解 Zn(2+)浓度要高得多。由于好氧表层沉积物和上覆水中的二价铁(Fe(2+))迅速氧化,没有释放出大量的铁。本研究表明,上覆水中 pH 值和盐度的周期性变化可以显著影响河口沉积物中金属的释放。