As temperatures rise in late spring, river water pH often increases during daylight hours. The main driver is enhanced photosynthetic activity of aquatic plants and phytoplankton.
Warmer water and longer days boost algal growth, which consumes more dissolved carbon dioxide (CO₂) from the water. Since CO₂ forms carbonic acid, removing it shifts the carbonate‑bicarbonate equilibrium toward hydroxide ions, raising pH values – sometimes above 9.0 in eutrophic rivers.
However, at night or on cloudy days, respiration releases CO₂, temporarily lowering pH. The overall diurnal pH swing becomes more pronounced with warming. Additionally, higher temperatures reduce CO₂ solubility, further contributing to a slight long‑term rise in pH, though buffer systems (e.g., bicarbonates) may dampen the effect.
In rivers with heavy organic pollution, temperature‑induced microbial decomposition can produce organic acids, potentially lowering pH locally.
Therefore, the net effect depends on nutrient levels, flow rate, and biological activity. For most healthy, slow‑flowing rivers, late‑spring warming leads to detectable daily pH peaks – a useful indicator for water quality monitoring.

