Lake Classification Calculators
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Trophic State Classification
Carlson's TSI: TSI < 40 = oligotrophic; 40–60 = mesotrophic; 60–80 = eutrophic; > 80 = hypereutrophic.
- Oligotrophic: Deep, clear, cold; low nutrients (TP < 10 μg/L); high oxygen to bottom; low algae; trout fisheries; Lake Tahoe, Lake Baikal
- Mesotrophic: Moderate nutrients; moderate clarity; some algal blooms possible
- Eutrophic: High nutrients (TP > 35 μg/L); algal blooms; hypolimnion may be anoxic in summer; cyanobacteria dominant; walleye/bass fisheries
- Hypereutrophic: Extreme nutrients; dense algal scum; severe oxygen depletion; foul taste/odor
Lake Mixing Types
- Dimictic: Mixes twice per year (spring and fall overturn); temperate deep lakes; stratified in summer and under ice in winter
- Monomictic (warm): Mixes once (winter); never freezes; subtropical and warm temperate lakes
- Polymictic: Mixes frequently (wind-driven); shallow lakes; no stable stratification
- Meromictic: Never completely mixes; dense saline bottom layer (monimolimnion) permanently isolated; e.g., Mono Lake (CA), some fjords
Lake Origins
Glacial (most common temperate lakes — moraines, kettles, cirques); tectonic (rift lakes — Lake Baikal, East African Great Lakes); volcanic (crater lakes); oxbow (meander cutoffs); coastal/lagoon; reservoirs (human-made).
Glossary
Frequently Asked Questions
Carlson's TSI classifies lakes on a 0–100 scale: TSI < 40 = oligotrophic (clear, nutrient-poor, high oxygen, cold-water fish like trout); TSI 40–60 = mesotrophic (moderate nutrients and productivity); TSI 60–80 = eutrophic (algal blooms, low Secchi depth, possible hypolimnetic anoxia); TSI > 80 = hypereutrophic (severe algal scum, oxygen depletion, fish kills). TSI can be calculated from Secchi depth, chlorophyll-a, or total phosphorus — ideally all three should agree; divergence indicates non-algal turbidity or internal loading.
Oligotrophic lakes: low nutrients (total phosphorus < 10 μg/L); clear water (Secchi depth > 6 m); high dissolved oxygen throughout the water column; dominated by cold-water species (trout, cisco); low algal biomass; deep. Eutrophic lakes: high nutrients (TP > 35 μg/L); turbid (Secchi depth < 2 m); hypolimnion anoxic in summer stratification; warm-water fish (bass, carp, catfish); frequent algal blooms with cyanobacteria dominance; shallower. The transition from oligotrophic to eutrophic (cultural eutrophication) is driven primarily by agricultural runoff and sewage nutrient loading.
A meromictic lake never completely mixes because the bottom layer (monimolimnion) has higher density than the surface water — usually due to dissolved salts, mineral inputs, or seawater intrusion. Unlike normal (holomictic) lakes that fully mix at least once per year, the deep water of meromictic lakes remains permanently stagnant, anoxic, and chemically distinct. Examples: Mono Lake (California) — high salinity from volcanic inputs; Lake Kivu (Rwanda/DRC) — deep CO₂ and methane accumulation from volcanic activity creates explosion risk; some Antarctic fjords. Meromictic conditions preserve unique microbial communities and sediment records.
Thermal stratification: solar heating warms the surface water in spring/summer, making it less dense than the cold bottom water. This creates a warm, less-dense epilimnion floating above the cold, dense hypolimnion, separated by the thermocline. Wind cannot mix across the large density difference. Fall overturn: as air temperature falls, surface water cools and density increases until surface and bottom water reach the same temperature (~4°C at maximum density) — wind can then mix the entire water column. This fall overturn reoxygenates the hypolimnion and redistributes nutrients. Dimictic lakes repeat this: fall overturn, ice cover (mixes under ice in spring), spring overturn, summer stratification.