Biology Centre CAS, v.v.i., Institute of Hydrobiology and Soil & Water Research Infrastructure, Na Sádkách 7, České Budějovice, Czech Republic; Faculty of Science, University of South Bohemia in České Budějovice, Branišovská 1760, České Budějovice, Czech Republic.
Biology Centre CAS, v.v.i., Institute of Hydrobiology and Soil & Water Research Infrastructure, Na Sádkách 7, České Budějovice, Czech Republic; Faculty of Science, University of South Bohemia in České Budějovice, Branišovská 1760, České Budějovice, Czech Republic.
Chemosphere. 2018 Feb;193:1018-1026. doi: 10.1016/j.chemosphere.2017.11.140. Epub 2017 Nov 23.
In situ experiments were done to determine the effects of the photochemical degradation of dissolved organic matter (DOM) and subsequent formation of particulate matter on dissolved phosphorus (P) concentrations in surface waters. Filtered (1.2 or 0.4 μm) headwaters (DOM of 8.1-26 mg L; P of 22-43 μg L) were exposed to solar radiation in quartz bottles located 5 cm below the water surface for 7-10 days. Dark controls were wrapped in aluminum foil. After incubation, particulate organic carbon (POC) and particulate phosphorus (PP) were determined in both the filtrate and newly formed particles. The results revealed increasing concentrations of PP and POC in exposed samples with increasing exposure time (cumulative irradiation energy). At the end of experiments, PP concentrations were from 5 to 20 μg L in the exposed samples. Based on an enumeration of bacteria in the samples, we estimated the contribution of biotic and abiotic processes to the PP production. The abiotic PP formation ranged from 56 to 83% and 50-95% of the total PP in the exposed and control samples, respectively. The remainder was assumed to be bacterial P uptake. Despite the overlapping intervals, biotic and abiotic PP productions were usually higher in exposed samples than in controls. The PP and POC production was affected by the properties of DOM, such as its humic content and freshness index. We hypothesize that the observed immobilization of dissolved P in bacteria and on photochemically-formed particles can contribute to a P limitation of primary production in headwater environments that receive waters rich in soil DOM.
进行了现场实验,以确定溶解有机质(DOM)的光化学降解及其随后形成的颗粒物对地表水中溶解磷(P)浓度的影响。将过滤(1.2 或 0.4 μm)的源头水(DOM 为 8.1-26 mg L;P 为 22-43 μg L)暴露在石英瓶中的水面下 5 cm 处的太阳辐射下 7-10 天。黑暗对照用铝箔包裹。孵育后,在滤出液和新形成的颗粒中测定了颗粒有机碳(POC)和颗粒磷(PP)。结果表明,随着暴露时间(累积辐照能)的增加,暴露样品中 PP 和 POC 的浓度增加。实验结束时,暴露样品中的 PP 浓度在 5 至 20 μg L 之间。基于对样品中细菌的计数,我们估计了生物和非生物过程对 PP 生成的贡献。非生物 PP 的形成范围分别为暴露和对照样品中总 PP 的 56-83%和 50-95%。其余的则被认为是细菌对 P 的吸收。尽管重叠间隔,暴露样品中的生物和非生物 PP 生成通常高于对照。PP 和 POC 的产生受 DOM 的特性影响,如腐殖质含量和新鲜度指数。我们假设,观察到的溶解 P 在细菌中和光化学形成的颗粒上的固定化可能导致接受富含土壤 DOM 的水的源头环境中的初级生产力受到 P 的限制。