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氧化还原循环过程中沉积物磷的形态及迁移转化规律
引用本文:郝文超,王从锋,杨正健,刘德富,纪道斌,赵萍,丹勇,胡子龙.氧化还原循环过程中沉积物磷的形态及迁移转化规律[J].环境科学,2019,40(2):640-648.
作者姓名:郝文超  王从锋  杨正健  刘德富  纪道斌  赵萍  丹勇  胡子龙
作者单位:三峡大学水利与环境学院, 宜昌 443002,三峡大学水利与环境学院, 宜昌 443002;三峡地区地质灾害与生态环境湖北省协同创新中心, 宜昌 443002,湖北工业大学河湖生态修复与藻类利用湖北省重点实验室, 武汉 430068,三峡大学水利与环境学院, 宜昌 443002;湖北工业大学河湖生态修复与藻类利用湖北省重点实验室, 武汉 430068,三峡大学水利与环境学院, 宜昌 443002,三峡大学水利与环境学院, 宜昌 443002,三峡大学水利与环境学院, 宜昌 443002,三峡大学水利与环境学院, 宜昌 443002
基金项目:国家自然科学基金重大项目(91647207)
摘    要:为研究沉积物在氧化还原循环过程中磷循环迁移转化机制,通过控制实验模拟分析氧化还原条件下,上覆水理化性质变化特征、沉积物各形态磷变化及机制研究,并量化沉积物中磷的重新分配和沉积物磷酸盐的释放通量影响.结果表明:(1)氧化还原电位Eh和p H体系、硫体系、碳体系以及与磷相关性密切的铁体系变化规律具有周期性,并对解释沉积物-水两相界面磷的迁移转化机制有重要作用;(2)在氧化还原循环过程中,各形态磷含量随着氧化还原条件和时间变化,根据水-沉积物磷素变化量化分析可得,可还原态磷(BD-P)和铁铝结合态磷(Na OH-rP)是可逆地重新分配到弱吸附态磷(NH4Cl-P)、聚磷/有机磷(Na OH-nrP)、残渣态磷(Rest-P)和间隙水溶解性活性磷(SRP)中,且沉积物中变化量93. 7%的磷在还原反应时不会释放到水体中;(3)上覆水总磷(TP)浓度变化的92%为上覆水的SRP,表明水-沉积物在该循环过程中以水溶性磷交换为主;(4)根据Fick第一定律得,还原阶段磷扩散通量最大值为0. 58 mg·(m~2·d)-1,而氧化阶段第7 d扩散通量约为0. 16~0. 22 mg·(m~2·d)-1;氧化反应阶段,扩散通量随时间逐渐降低,还原阶段的变化趋势相反,表明还原状态会加速沉积物磷的扩散程度,而曝氧降低了沉积物磷扩散通量.

关 键 词:氧化还原环境  磷形态  迁移转化    扩散通量  氧化还原体系
收稿时间:2018/6/26 0:00:00
修稿时间:2018/7/24 0:00:00

Speciation and Transformation of Phosphorus in Sediments During the Redox Cycle
HAO Wen-chao,WANG Cong-feng,YANG Zheng-jian,LIU De-fu,JI Dao-bin,ZHAO Ping,DAN Yong and HU Zi-long.Speciation and Transformation of Phosphorus in Sediments During the Redox Cycle[J].Chinese Journal of Environmental Science,2019,40(2):640-648.
Authors:HAO Wen-chao  WANG Cong-feng  YANG Zheng-jian  LIU De-fu  JI Dao-bin  ZHAO Ping  DAN Yong and HU Zi-long
Institution:College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China,College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China;Collaborative Innovation Center for Geo-hazards and Eco-Environment in Three Gorges Area, Hubei Province, Yichang 443002, China,Hubei Key Laboratory of Ecological Restoration of River-lakes and Algal Utilization, Hubei University of Technology, Wuhan 430068, China,College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China;Hubei Key Laboratory of Ecological Restoration of River-lakes and Algal Utilization, Hubei University of Technology, Wuhan 430068, China,College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China,College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China,College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China and College of Hydraulic and Environmental Engineering, China Three Gorges University, Yichang 443002, China
Abstract:To study the mechanism of phosphorus cycling in sediment during the redox cycle, changes in physicochemical properties of overlying water and various forms of phosphorus in sediments were investigated as a way to quantify the redistribution of phosphorus. Additionally, the effect of the release flux of phosphate from sediments under controlled redox conditions was analyzed. The results showed that the redox potential Eh and the pH system, sulfur system, carbon system, and iron-related changes exhibited periodicity and played an important role in explaining the migration and transformation mechanism in the interface phosphorus of the sediment-water phase. During the redox cycle, the phosphorus content of each species varied with the redox conditions and time. Because of this, quantitative analysis based on changes in water-sediment phosphorus could be obtained. Reducible phosphorus (BD-P) and iron-aluminum-bound phosphorus (NaOH-rP) were reversibly redistributed into weakly adsorbed phosphorus (NH4Cl-P), polyphosphorus/organophosphorous (NaOH-nrP), residual phosphorus (Rest-P), and interstitial water-soluble active phosphorus (SRP). Additionally, 93.7% of phosphorus in the sediment was not released into the water phase during the reduction reaction. The 92% of change in the overlying water total phosphorus (TP) was the SRP of overlying water, which showed that the exchange of the sediment-water phase were mainly soluble active phosphorus in this cycle. According to Fick''s First Law, the maximum phosphorus flux was 0.58 mg·(m2·d)-1 during reduction and 0.16-0.22 mg·(m2·d)-1 on day seven of the oxidation phase. In the oxidation stage, the diffusion flux decreased with time, while the opposite trend occurred in the reduction reaction. This indicated that the anaerobic state accelerated the diffusion of phosphorus in sediments, and that oxygen exposure decreased the phosphorus flux in sediments.
Keywords:redox environment  phosphorus speciation  migration and transformation  diffusion flux  redox system
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