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应用生态学报 ›› 2026, Vol. 37 ›› Issue (9): 2945-2962.doi: 10.13287/j.1001-9332.202609.039

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湿地植被调控沉积物-水界面磷迁移转化机制研究进展

余炜诚1,2, 李峰1,2*, 谢永宏1,2, 耿明明1,2, 朱可欣1,2, 何昊轩1,2   

  1. 1中国科学院亚热带农业生态研究所, 长沙 410125;
    2湖南洞庭湖湖泊湿地生态系统国家野外科学观测研究站, 湖南岳阳 414018
  • 收稿日期:2026-05-07 接受日期:2026-07-14 出版日期:2026-09-18 发布日期:2026-10-12
  • 通讯作者: *E-mail: changshalifeng@163.com
  • 作者简介:余炜诚, 男, 1993年生, 博士, 助理研究员。主要从事湿地植被恢复与内源氮、磷负荷调控研究。E-mail:yuweicheng@isa.ac.cn
  • 基金资助:
    国家自然科学基金联合基金项目(U2571204)、国家自然科学基金项目(42301068)和湖南省揭榜挂帅项目(2024QK3001)

Mechanisms underlying the regulations of wetland vegetation on phosphorus migration and transformation at the sediment-water interface:A review.

YU Weicheng1,2, LI Feng1,2*, XIE Yonghong1,2, GENG Mingming1,2, ZHU Kexin1,2, HE Haoxuan1,2   

  1. 1Institute of Subtropical Agriculture, Chinese Academy of Sciences, Changsha 410125, China;
    2Hunan Dongting Lake Station for Wetland Ecosystem Research, Yueyang 414018, Hunan, China
  • Received:2026-05-07 Accepted:2026-07-14 Online:2026-09-18 Published:2026-10-12

摘要: 沉积物-水界面是湿地内源磷释放、固定与形态转化的关键区域,湿地植被可通过调节水动力、根际氧化还原环境、植物吸收和微生物过程,影响界面磷的源汇状态。本文围绕湿地植被调控沉积物-水界面磷迁移转化这一主线,综述了植被物理稳泥、根际泌氧与铁-磷耦合、植物-微生物互作及残体分解反馈等主要机制,并比较了不同植物生活型和群落特征的调控差异。挺水植物通常具有较强的根际泌氧和稳泥能力,有利于界面磷固定;沉水植物可通过提高近底层溶解氧、吸收磷和抑制底泥再悬浮降低磷释放风险;浮叶和漂浮植物的长期效应则更依赖覆盖度、残体管理和底层氧环境。植被调控效果受到水文波动与干湿交替、温度、溶解氧、pH、沉积物性质、初始磷赋存形态及外源负荷等因素共同制约。植物生长期通常以磷吸收和界面固定为主,衰败期或扰动期则可能因残体归还、耗氧及稳泥作用减弱而增加释磷风险,其长期净效应具有明显的情境依赖性。未来应加强多因子耦合阈值识别、植物-微生物功能互作解析、原位高分辨动态监测及长期源汇稳定性评估,为湿地植被恢复和内源磷精准管理提供科学依据。

关键词: 沉积物-水界面, 内源磷释放, 湿地植被, 根际过程, 磷形态, 氧化还原条件, 生态修复

Abstract: The sediment-water interface is a key zone for the release, retention, and transformation of internal phosphorus (P) in wetlands. Wetland vegetation can alter the source-sink status of P at this interface by modifying hydrodynamic conditions, rhizosphere redox environments, plant uptake, and microbial processes. We synthesized the mechanisms by which wetland vegetation regulates P transport and transformation across the sediment-water interface, including physical sediment stabilization, radial oxygen loss, and iron-phosphorus coupling, plant-microbe interactions, and litter decomposition feedbacks. We further compared the regulatory effects of different plant life forms and community characteristics. Emergent plants generally exhibit strong rhizosphere oxygenation and sediment-stabilizing capacities, thereby favoring P retention at the interface. Submerged plants can reduce P release by increasing near-bottom dissolved oxygen, taking up P, and suppressing sediment resuspension. By contrast, the long-term effects of floating-leaved and free-floating plants depend more strongly on vegetation coverage, litter management, and bottom-water oxygen conditions. The effectiveness of vegetation-mediated P regulation is jointly constrained by hydrological fluctuations and wetting-drying cycles, temperature, dissolved oxygen, pH, sediment properties, initial P speciation, and external P loading. During the growing season, plant P uptake and interfacial P retention generally predominate, whereas senescence or disturbance may increase P release risks through litter return, oxygen depletion, and weakened sediment stabilization. Consequently, the long-term effect of wetland vegetation on P cycling is strongly context dependent. Future research should focus on identifying thresholds under multiple interacting factors, elucidating functional plant-microbe interactions, developing high-resolution in situ monitoring approaches, and evaluating the long-term stability of P source-sink dynamics, thereby providing a scientific basis for wetland vegetation restoration and precise management of internal P loading.

Key words: sediment-water interface, internal phosphorus release, wetland vegetation, rhizosphere process, phosphorus fraction, redox condition, ecological restoration