4.7 Article

Phosphorus mobilization and availability across the freshwater to oligohaline water transition in subtropical estuarine marshes

Journal

CATENA
Volume 201, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.catena.2021.105195

Keywords

Phosphorus; Iron; Diffusive gradients in thin films; Saltwater intrusion; Estuarine tidal marsh

Funding

  1. National Science Foundation of China [41801062, 41877335]
  2. Key Natural Science Foundation of Fujian Province [2019J02008]
  3. European Research Council Synergy Grant [ERC-SyG-2013-610028 IMBALANCE-P]
  4. Spanish Government [CGL2016-79835-P]
  5. Catalan Government [SGR 2017-1005]

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This study investigated the impact of salinity gradient on phosphorus release from sediments in estuarine tidal marshes. Results showed significant variations in phosphorus concentrations along the freshwater-oligohaline transition, with a possible link to the release of iron-bonded phosphorus stimulated by sulfate reduction.
Internal phosphorus (P) released from sediments, which has been verified to be affected by iron (Fe) and sulfur (S) reactions, strongly influences P cycling and water eutrophication. However, minimal research has been performed to determine how increased low-level salinity in estuarine tidal marshes affects P mobility and its coupled processes. Herein, in situ high-resolution distributions of labile P, Fe, and S in sediment-overlying water profiles were simultaneously measured along an estuarine freshwater-oligohaline gradient (MM River Estuary, China) utilizing newly developed diffusive gradients in thin films technique. Significant variations in the P, Fe, and S concentrations were observed with significantly higher sediment labile P concentrations in the freshwater-oligohaline transition. The observed labile P and Fe coupling confirmed the Fe redox-driven P release mechanism in the sediment, although this coupling was weakened in the freshwater-oligohaline transition. The diffusion flux results revealed that the sediments shifted from P sink to source with the transition from a freshwater to an oligohaline environment, probably caused by the release of Fe-bonded P stimulated by sulfate reduction. This study determined that increased salinity and the associated environmental responses alter the P remobilization capacity and internal P cycling by changing the sediment P pool and the P-Fe-S couplings across the sediment-water interface. Furthermore, saltwater intrusion into tidal freshwater wetlands caused by strong typhoons or sea-level rise may increase internal P release from sediments, which could have future implications.

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