Why is calcite a strong phosphorus sink in freshwater? Investigating the adsorption mechanism using batch experiments and surface complexation modeling
Why is calcite a strong phosphorus sink in freshwater? Investigating the adsorption mechanism using batch experiments and surface complexation modeling
复制标题
为什么方解石在淡水中具有很强的磷沉降作用?
DOI:
10.1016/j.chemosphere.2021.131596
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发表时间:
2022
期刊:
影响因子:
8.8
通讯作者:
Dalton, Robert
中科院分区:
文献类型:
--
作者:
Flower, Hilary;Rains, Mark;Taşcı, Yasemin;Zhang, Jia-Zhong;Trout, Kenneth;Lewis, David;Das, Arundhati;Dalton, Robert
One of the primary drivers of Phosphorus (P) limitation in aquatic systems is P adsorption to sediments. Sediments adsorb more P in freshwater compared to other natural solutions, but the mechanism driving this difference is poorly understood. To provide insights into the mechanism, we conducted batch experiments of P adsorption to calcite in freshwater and seawater, and used computer software to develop complexation models. Our simulations revealed three main reasons that, combining together, may explain the greater P adsorption to calcite in freshwater vs. seawater. First, aqueous speciation of P makes a difference. The ion pair CaPO4−is much more abundant in freshwater; although seawater has more Ca2+ions, MgHPO40and NaHPO40are more thermodynamically favored. Second, the adsorbing species of P make a difference. The ion pair CaPO4−(the preferred adsorbate in freshwater) is able to access adsorption sites that are not available to HPO42−(the preferred adsorbate in seawater), thereby raising the maximum concentration of P that can adsorb to the calcite surface in freshwater. Third, water chemistry affects the competition among ions for surface sites. Other ions (including P) compete more effectively against CO32−when immersed in freshwater vs. seawater, even when the concentration of HCO3−/CO32−is higher in freshwater vs. seawater. In addition, we found that under oligotrophic conditions, P adsorption is driven by the higher energy adsorption sites, and by the lower energy sites in eutrophic conditions. This study is the first to model P adsorption mechanisms to calcite in freshwater and seawater.