Seasonal hypoxia in stratified estuaries and the adjacent coastal ocean have already been recognized as an increasingly serious environmental problem of worldwide concern (Breitburg et al., 2018;Diaz & Rosenberg, 2008). They were usually linked to the anthropogenic nutrient inputs (also referred to as eutrophication), which stimulates primary production and export of organic matter, thus resulting in increased oxygen consumption and eventual oxygen depletion (Conley, Bonsdorff, et al., 2009). However, this paradigm of eutrophication-driven coastal hypoxia can not be directly used to understand the persistent development of coastal hypoxia after the pollutant export has been strictly controlled in past decades Duarte et al., 2009). In general, seasonal hypoxia occur in the coastal ocean when strong oxygen sinks are coupled with restricted resupply induced by weakly mixing during periods of strong density stratification (Cui et al., 2019;Fennel & Testa, 2018). Total oxygen consumption (TOC) was generally considered to be composed of two components: (a) sediment oxygen demand (SOD), and (b) water oxygen consumption (WOC) by the degradation of dissolved and particulate organic matters (i.e., DOM and POM). In fact, the bed sediment not only determines SOD through the sediment-water interface oxygen consumption, but it possibly enhance WOC also after being resuspended into water column (Ackerman et al., 2001;Moriarty et al., 2018Moriarty et al., , 2021. For the sake of convenience, resuspended sediment will be termed as resuspended particles in the subsequent text, in contrast to immovable bed sediment.