Large wood (>10 cm diameter and 1 m long) creates numerous geomorphic and ecologic effects in stream corridors (active channel and floodplain). By creating obstructions and increasing hydraulic roughness, large wood affects the distribution of hydraulic force (Manners et al., 2007;Shields & Smith, 1992) and therefore hyporheic exchange flows and solute dynamics (Doughty et al., 2020;Sawyer et al., 2011), as well as the transport of sediment and particulate organic matter (Hinshaw et al., 2020;Wohl & Scott, 2017). The presence of large wood can influence the type and dimensions of channel bedforms (MacFarlane & Wohl, 2003); the presence and grain-size distribution of alluvium (Faustini & Jones, 2003;Massong & Montgomery, 2000;Ryan et al., 2014); and the characteristics of reach-scale gradient, cross-sectional geometry, and planform geometry (Collins et al., 2012;O'Connor et al., 2003). The flow obstructions and erosionally resistant points associated with wood accumulations can increase channel-floodplain hydrologic and sediment connectivity, as well as altering channel migration rate and floodplain turnover time (