Earth's oxidation state and climate are both a cause and consequence of biogeochemical element cycles. As the sixth most abundant element present in both the geosphere and biosphere (Brychkova et al., 2007;Mandeville, 2010;Torres et al., 2014) in variable oxidation states, sulfur plays a major role in shaping Earth's surface environments (Berner & Raiswell, 1983;Fike et al., 2015). Terrestrial environments form a critical part of the global sulfur cycle as continental weathering provides the primary source of sulfate to the ocean, overwhelming magmatic inputs (Holser et al., 1989). Recently, increasing attention has turned toward possible feedback loops among atmospheric CO 2 , glaciation, and oxidative weathering of pyrite exposed on land (Bufe et al., 2021;Calmels et al., 2007;Torres et al., 2014Torres et al., , 2017. Quantitative models calculating pyrite-derived sulfate fluxes in rivers often assume conservative mixing of isotopically distinct sources (Chillrud et al., 1994;Szynkiewicz et al., 2015); however, catchment-scale studies report deviations from simple isotope mass balance (Finley et al., 1995;Turchyn et al., 2013). More importantly, the rate of global pyrite oxidation on land, estimated assuming conservative mixing between terrestrial end-members, does not balance with that of marine pyrite burial (Burke et al., 2018). These discrepancies, notwithstanding inherent uncertainties in calculations using a single isotope-mass balance model, suggest that weathering alone fails to capture the complex nature of the terrestrial sulfur cycle, jeopardizing our understanding of the global redox budget.To address this gap, we revisit the role of terrestrial environments in the biogeochemical sulfur cycle at both local and global scales. In the fluvial system downstream of the Jostedal Glacier, Norway (Figure 1), we examine the limitations of a conservative mixing model, using the sulfur isotope compositions of a range of geologic and