Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O Box 7050, 750 07, Uppsala, Sweden.
Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, P.O Box 7050, 750 07, Uppsala, Sweden.
Water Res. 2020 Oct 15;185:116150. doi: 10.1016/j.watres.2020.116150. Epub 2020 Jul 26.
Historical accumulation of phosphorus (P) in lake sediment often contributes to and sustains eutrophic conditions in lakes, even when external sources of P are reduced. The most cost-effective and commonly used method to restore the balance between P and P-binding metals in the sediment is aluminum (Al) treatment. The binding efficiency of Al, however, has varied greatly among treatments conducted over the past five decades, resulting in substantial differences in the amount of P bound per unit Al. We analyzed sediment from seven previously Al treated Swedish lakes to investigate factors controlling binding efficiency. In contrast to earlier work, lake morphology was negatively correlated to binding efficiency, meaning that binding efficiency was higher in lakes with steeply sloping bathymetry than in lakes with more gradually sloping bottoms. This was likely due to Al generally being added directly into the sediment, and not to the water column. Higher binding efficiencies were detected when Al was applied directly into the sediment, whereas the lowest binding efficiency was detected where Al was instead added to the water column. Al dose, mobile sediment P and lake morphology together explained 87% of the variation in binding efficiency among lakes where Al was added directly into the sediment. This led to the development of a model able to predict the optimal Al dose to maximize binding efficiency based on mobile sediment P mass and lake morphology. The predictive model can be used to evaluate cost-effectiveness and potential outcomes when planning Al-treatment using direct sediment application to restore water quality in eutrophic lakes.
湖泊沉积物中磷(P)的历史积累常常导致并维持湖泊富营养化,即使减少了外部 P 源。恢复沉积物中 P 与 P 结合金属之间平衡最具成本效益且常用的方法是使用铝(Al)处理。然而,在过去五十年间进行的各种处理中,Al 的结合效率差异很大,导致单位 Al 结合的 P 量存在很大差异。我们分析了来自瑞典七个先前经过 Al 处理的湖泊的沉积物,以研究控制结合效率的因素。与早期的研究工作相反,湖泊形态与结合效率呈负相关,这意味着在地形陡峭的湖泊中,结合效率高于地形平缓的湖泊。这可能是因为 Al 通常直接添加到沉积物中,而不是添加到水柱中。当 Al 直接添加到沉积物中时,检测到更高的结合效率,而当 Al 被添加到水柱中时,检测到最低的结合效率。Al 剂量、可移动沉积物 P 和湖泊形态共同解释了直接向沉积物中添加 Al 的湖泊中结合效率变化的 87%。这导致了一种能够根据可移动沉积物 P 质量和湖泊形态预测最大结合效率的最优 Al 剂量的模型的发展。该预测模型可用于评估直接向沉积物中添加 Al 以恢复富营养化湖泊水质的成本效益和潜在结果。