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Updated: Jul 3, 2026

Visualizing Methane-Cycling Microbial Dynamics in Coastal Wetlands
Published on: January 31, 2025
Preserving bare mudflats reduces methane emissions: Implications for coastal wetland management
Zhihao Xu1, Xin Zhao2, Yangjie Li1
1Key Laboratory of Marine Ecosystem Dynamics, Second Institute of Oceanography, Ministry of Natural Resources, Hangzhou, 310012, China.
None:
Spartina alterniflora invasion and coastal ecological engineering may influence methane (CH4) emissions by altering wetland ecosystem carbon cycling processes. However, there remains a paucity of systematic studies on the dynamics of CH4 production and emissions resulting from these interconnected natural and anthropogenic processes. This study employed a combined method of static chambers and greenhouse gas online analyzers to conduct in situ monitoring of CH4 exchange fluxes across four typical coastal wetland types (bare mudflat, S. alterniflora salt marsh, deep excavation-burial treatment zone for S. alterniflora eradication and artificial mangrove introduction areas). Concurrent measurements included sediment porewater CH4 concentration, organic carbon content with stable isotopic composition, belowground biomass, Eh, and pH, aiming to elucidate CH4 emission characteristics and their driving mechanisms in these distinct habitats. Research has demonstrated that the belowground biomass of S. alterniflora modulates CH4 production pathways. In managed zones, the accumulation of CH4 in sediments was attributed to plant debris decomposition-induced alterations in organic matter content, redox potential, pH, as well as sediment water content and bulk density. The study revealed that all habitat types function as atmospheric CH4 sources, with emission intensities exhibiting the following gradient: bare mudflat < S. alterniflora salt marsh < artificial mangrove < S. alterniflora deep excavation-burial treatment zone. S. alterniflora invasion facilitates efficient CH4 transport via aerenchyma, achieving a 40-fold enhancement in emission fluxes despite lower porewater CH4 concentrations than mudflats. Notably, the engineered treatment zone demonstrated an average CH4 flux of 7.421 mg m-2·h-1, representing a 285-fold enhancement compared to mudflat emissions. The substantial CH4 emissions from the S. alterniflora eradication zone primarily arise from the synergistic effects of porewater CH4 accumulation and subsequent pulsed ebullition. Regrettably, mangrove transplantation following S. alterniflora removal can't reduce CH4 emissions to the level of bare mudflat in the short term. The bare mudflats exhibit significantly lower CH4 emissions than restored areas, a feature that, from the perspective of CH4 emissions alone, suggests a more climate-friendly alternative. Ecological restoration practices should fully consider the impact of anthropogenic disturbances on CH4 production to avoid amplifying CH4 emissions due to inappropriate engineering measures.
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