Summer high temperatures affect water turbidity through a combination of physical, chemical, and biological processes, generally leading to an overall increase in turbidity in natural water bodies. However, the magnitude and pattern of this change depend on waterbody type, hydrological conditions, and ecological status.
The most prominent biological effect is the rapid proliferation of phytoplankton, especially algae. Most algae thrive at 20–30 °C. Under sustained summer heat and ample sunlight, algal cells multiply rapidly, forming dense suspensions. These cells scatter light efficiently, directly elevating turbidity. In eutrophic rivers, lakes, or reservoirs, summer algal blooms can raise turbidity several‑fold. Moreover, dead algal cells release colloidal organic debris and promote bacterial growth, further increasing fine particulate loads.
Thermal stratification is another important physical process. In stagnant or slow‑flowing waters, warm surface water forms a stable thermocline that suppresses vertical mixing. The bottom layer often becomes hypoxic or anoxic; accumulated metabolic gases (methane, hydrogen sulfide) bubble up, entraining sediment particles into the water column and causing sudden turbidity spikes. Benthic fish activity, which increases in warm seasons, also resuspends bottom sediments.
Summer is also the season for intense convective rainstorms. Heavy rainfall erodes soil and washes mineral particles, organic debris, and attached pollutants into rivers, producing high‑turbidity runoff. In urban areas, initial stormwater runoff can reach hundreds of NTU. Simultaneously, rising water levels and flow velocities resuspend riverbed deposits, leading to sharp short‑term turbidity increases. Typically, turbidity peaks several hours to a day after a storm and then gradually declines, though alternating hot sunny days and heavy rains cause periodic large fluctuations.
Physicochemical changes also play a role. Water viscosity decreases with rising temperature, which theoretically speeds particle settling. However, accelerated decomposition of organic matter under heat produces dissolved extracellular polymeric substances. These compounds adsorb onto particle surfaces, enhancing colloidal stability through steric or electrostatic effects and inhibiting aggregation and sedimentation. Thus, the net effect often prolongs elevated turbidity, especially in organically polluted reaches.
In summary, summer high temperatures primarily raise natural water turbidity by triggering algal blooms, enhancing sediment resuspension, introducing turbid stormwater runoff, and altering particle surface chemistry. For drinking water sources, scenic rivers, and fishery waters, monitoring frequency should be increased during summer.

