Hypoxia and acidification are commonly coupled in eutrophic
aquatic
environments because aerobic respiration is usually dominant in bottom
waters and can lower dissolved oxygen (DO) and pH simultaneously.
However, the degree of coupling, which can be weakened by non-aerobic
respiration and CaCO3 cycling, has not been adequately
assessed. In this study, we applied a box model to 20 years of water
quality monitoring data to explore the relationship between hypoxia
and acidification along the mainstem of Chesapeake Bay. In the early
summer, dissolved inorganic carbon (DIC) production in mid-bay bottom
waters was dominated by aerobic respiration, contributing to DO and
pH declines. In contrast, late-summer DIC production was higher than
that expected from aerobic respiration, suggesting potential buffering
processes, such as calcium carbonate dissolution, which would elevate
pH in hypoxic waters. These findings are consistent with contrasting
seasonal relationships between riverine nitrogen (N) loads and hypoxic
and acidified volumes. The N loads were associated with increased
hypoxic and acidified volumes in June, but only increased hypoxic
volumes in August, when acidified volume declines instead. Our study
reveals that the magnitude of this decoupling varies interannually
with watershed nutrient inputs, which has implications for the management
of co-stressors in estuarine systems.