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.
Environ Pollut. 2019 Mar;246:472-481. doi: 10.1016/j.envpol.2018.12.031. Epub 2018 Dec 13.
Iron (Fe) and manganese (Mn) reactions have been regarded as the primary factors responsible for the mobilization of phosphorus (P) in lake sediments, although their individual roles are hard to distinguish. In this study, in situ mobilization of P, Fe and Mn in sediments was assessed by high resolution spatio-temporal sampling of their labile forms using diffusive gradient in thin films (DGT) and suction device (Rhizon) techniques. It was found that the monthly concentration distributions showed greater agreement and better correlation coefficients between labile P and labile Fe, than those between labile P and labile Mn, implying that Fe plays a key role in controlling P release in sediments. Furthermore, better correlations were observed between hourly changes in concentrations of soluble reactive phosphorus (SRP) and soluble Fe(II), than those between SRP and soluble Mn. Changes were observed under simulated anaerobic incubation conditions, suggesting that P release was caused by the reductive dissolution of Fe oxides. This was supported by the lack of influences on P release from reductive dissolution of Mn oxides in the sediment-water interface and top sediment layers under the anaerobic incubations. In simulated algal bloom experiments, positive correlations and consistent changes were observed between SRP and soluble Fe(II) concentrations, but not between SRP and soluble Mn concentrations. This further demonstrated the Fe-dependent and Mn-independent release of P in sediments. Therefore, Fe redox reactions have a high impact on P mobilization in sediments, while Mn redox reactions appear to have negligible influences.
铁(Fe)和锰(Mn)反应被认为是湖泊沉积物中磷(P)释放的主要因素,尽管它们各自的作用难以区分。在这项研究中,通过使用扩散梯度薄膜(DGT)和吸力装置(Rhizon)技术对其可利用形态进行高分辨率时空采样,评估了沉积物中 P、Fe 和 Mn 的原位可利用性。结果表明,月浓度分布显示可利用 P 和可利用 Fe 之间的一致性更好,相关性系数更高,而可利用 P 和可利用 Mn 之间的相关性则较差,这表明 Fe 在控制沉积物中 P 释放方面发挥了关键作用。此外,在模拟厌氧培养条件下,观察到可溶性反应性磷(SRP)和可溶性 Fe(II)浓度的小时变化之间存在更好的相关性,而 SRP 和可溶性 Mn 之间的相关性则较差。在厌氧培养条件下,在沉积物-水界面和上层沉积物中观察到 Mn 氧化物的还原溶解对 P 释放没有影响,这表明 P 的释放是由 Fe 氧化物的还原溶解引起的。在模拟藻类爆发实验中,观察到 SRP 和可溶性 Fe(II)浓度之间存在正相关和一致的变化,但 SRP 和可溶性 Mn 浓度之间没有。这进一步证明了沉积物中 P 的释放与 Fe 有关,与 Mn 无关。因此,Fe 的氧化还原反应对沉积物中 P 的迁移有很大影响,而 Mn 的氧化还原反应似乎影响较小。