The growing demand for fossil-free energy makes hydroelectric power generation an important technology for flexible and renewable energy (Ashraf et al., 2018). Hydropower plants alter the natural flow regime of up-and downstream river reaches, however, with potential negative effects on aquatic organisms (Kuriqi et al., 2021;Poff et al., 1997). Particularly when electricity is generated to meet sub-daily fluctuations in energy demand, rapid changes in discharge downstream of hydropower plants can be extreme (Carolli et al., 2015;Cushman, 1985); these hydropeaking flow regimes, which result in rapid changes in stream flow patterns, have been shown to severely affect riverine biota (Moreira et al., 2019;Smokorowski et al., 2011;Zimmerman et al., 2010). The ecological effects of hydropeaking on riverine organisms are linked to alterations in the natural river hydrology, morphology (e.g. river depth, width, velocity, riverbed material and grain size) and water quality (e.g. temperature and turbidity) (Charmasson & Zinke, 2011;Hauer et al., 2014). Specific to fish and their instream habitat, alterations in river depths, velocity and water temperature are the major sources