Fine suspended particles are ubiquitous in streams and rivers. Suspended material typically includes sedimentary particles (Wharton et al., 2017), particulate organic matter (Johnson et al., 2018), microplastics (Li et al., 2020, and microbiota such as bacteria, algae, and viruses (Lenaker et al., 2018). Transport and deposition of fine suspended particles play a key role in regulating river-groundwater interactions, river morphodynamics, and hyporheic biogeochemistry (Boano et al., 2014). Clay particle deposition decreases streambed hydraulic conductivity by filling porespace, ultimately clogging the bed, altering patterns of porewater flow, and degrading the benthic and hyporheic ecosystem (Brunke, 1999;Brunke & Gonser, 1997;Fox et al., 2018). Clay in the streambed can also reduce bed sediment motion (Dallmann et al., 2020). The deposition of fine particulate organic matter drives hyporheic metabolism (Newbold et al., 2005) and plays an important role in fluvial carbon cycling (Brunke & Gonser, 1997;Hope et al., 1994). Additionally, fine sediment particles play an important role in the colloid-facilitated transport of sorbed metals (Droppo et al., 2014;Foster & Charlesworth, 1996), as well as the accumulation of contaminants in bed sediment (Arce et al., 2017;Stone & Droppo, 1994). Despite the importance of spatial patterns of particle deposition for hyporheic ecosystems, fluvial biogeochemical processes, and river contamination most studies of riverine fine particles focus on the water column (Drummond et al., 2019;Park & Hunt, 2018;. Considerably less effort has been put into understanding the dynamics