State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China.
State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China.
Water Res. 2018 Apr 15;133:153-164. doi: 10.1016/j.watres.2018.01.040. Epub 2018 Jan 18.
Algal growth causes a drastic change in aquatic conditions over a diel cycle, which may induce sensitive feedback systems in sediments, causing P release. In this study, a microcosm experiment was performed using a suction sampler (Rhizon) to observe changes in soluble reactive phosphorus (SRP) and soluble Fe(II) concentrations in the top 20 mm sediment layer on a 3-h time interval, at different phases of harmful algal bloom (HAB) development. The results showed that the algal blooms prevailed up to 15 days after incubation, after which the process of bloom collapse proceeded until the 70th day. The concentrations of pore-water soluble Fe(II) and SRP increased throughout the incubation period. Compared to day 1, maximum increases of 214% in soluble Fe(II) and 387% in SRP were observed at night during the bloom and collapse periods, respectively. The diffusive fluxes of Fe and P at the sediment-water interface (SWI) generally corresponded to their changes in concentrations. Hourly fluctuation in soluble Fe(II) and SRP concentrations were observed with two distinct concentration peaks occurred at 21:00 p.m. and 06:00 a.m. (or 03:00 a.m.), respectively. These findings suggest that Fe-P coupling mechanisms are responsible for the release of P from sediments. During the collapse period, soluble Fe(II) concentrations were suppressed by the increase of labile S(-II) at night. Meanwhile, SRP concentrations were decoupled from Fe cycling with small fluctuations (<11% RSD) on an hourly timescale, and the decomposition of algae was a dominant source contributing to the release of P from sediments. These results significantly improved the understanding of processes and mechanisms behind the stimulated release of P from sediments during HABs.
藻类生长会导致水生环境在昼夜周期内发生剧烈变化,这可能会引发沉积物中敏感的反馈系统,导致磷释放。在这项研究中,使用抽吸采样器(Rhizon)进行了一个微宇宙实验,以观察有害藻华(HAB)发展的不同阶段中,在 3 小时的时间间隔内,上覆 20mm 沉积物层中可溶性反应磷(SRP)和可溶性 Fe(II)浓度的变化。结果表明,藻类水华持续了 15 天的潜伏期,之后水华崩溃过程持续到第 70 天。整个孵育期间,孔隙水可溶性 Fe(II)和 SRP 浓度均增加。与第 1 天相比,在水华和崩溃期的夜间,分别观察到可溶性 Fe(II)和 SRP 的最大增加 214%和 387%。在沉积物-水界面(SWI)处铁和磷的扩散通量通常与它们的浓度变化相对应。在孵育期间,观察到可溶性 Fe(II)和 SRP 浓度的小时波动,分别在晚上 9 点和凌晨 3 点(或凌晨 6 点)出现两个明显的浓度峰值。这些发现表明,铁-磷耦合机制是沉积物中磷释放的原因。在崩溃期,夜间可利用 S(-II)的增加抑制了可溶性 Fe(II)浓度的增加。同时,SRP 浓度与 Fe 循环脱耦,在小时时间尺度上波动较小(<11%RSD),藻类分解是导致沉积物中磷释放的主要来源。这些结果显著提高了对有害藻华期间沉积物中磷刺激释放过程和机制的理解。