Tidal flats and salt marshes connect the land and the ocean by mediating the exchange of water, sediments, and nutrients within coastal landscapes (FitzGerald & Hughes, 2019;Mitsch & Gosselink, 2000;Zedler & Kercher, 2005). Salt marshes are typically covered by halophytic vegetation. They occupy elevations higher than mean sea level (MSL) and are periodically inundated by the tide (Allen, 2000;Friedrichs & Perry, 2001). Conversely, tidal flats lie below mean sea level and hence, are intermittently exposed during low tides (Zhou et al., 2016). They do not host halophytic vegetation, but can be covered by microbial biofilms or colonized by sea grasses, which contribute to stabilize the sediment bed (Chen et al., 2017;Yallop et al., 1994).Depending on the rate of relative sea level rise (RSLR) and sediment availability, tidal flats can evolve into salt marshes and vice versa (Fagherazzi et al., 2006;Marani et al., 2007;Zhou et al., 2016). As the elevation of the intertidal platform increases within the tidal frame, flow conditions become suitable for the settlement of vegetation seeds. The bare surface of tidal flats is thus progressively encroached by vegetation patches, and eventually a salt marsh forms, as a result of the interaction of physical and biological processes (Bouma et al., 2014;Hu et al., 2015). On the contrary, a salt marsh can experience a transition into a tidal