Study on the role of zooplankton within freshwater ecosystems, specifically focusing on their interactions and relationships with other aquatic organisms, such as phytoplankton.
Zooplankton communities are influenced by various factors affecting their distribution in both space and time.
Spring: Diatoms
Summer: Green algae, B-g algae
Autumn: Diatoms, Rotifers & Cladocera, copepods
The changes in phytoplankton influence zooplankton succession, raising questions about causality (Cause or Effect?).
Abundance Impact: High abundance of food leads to increased zooplankton populations.
Herbivory: Zooplankton herbivory reduces algal abundance.
Nutrient Recycling: Phosphorous recycling boosts algal growth.
Algal Susceptibility: Varies by size, shape (single-celled, colonial, filamentous) & presence of toxins.
Selective Feeding: Zooplankton can avoid feeding on protected individuals.
Influenced by various physical factors and nutrients.
Phytoplankton populations cycle seasonally, with variance due to grazing interactions.
Studies show that in enclosures without predators, mesozooplankton (0.2-20 mm) presence can reduce phytoplankton abundance, indicating a significant predatory impact.
Effect size varies, being stronger for larger phytoplankton (those >30 μm).
Increased zooplankton populations correlate with improved phytoplankton growth conditions (nutrient addition).
Observed declines in zooplankton follow reductions in available phytoplankton, hinting at strong food availability impacts in predator-free environments.
Types:
Invertebrate: Copepoda, insect larvae
Vertebrate: white fish, fish fry, Amphibia
Population growth can be modeled using Nt = N0ert where r = b - d, based on population size changes.
Example Predators:
Leptodora kindtii: A predatory water flea.
Daphnia schødleri: Grows up to 18 mm length.
Observations made under varying light conditions in different lakes (clear vs turbid) documented differences in overall zooplankton biomass.
Increased turbidity linked to lower light levels which translated to less zooplankton growth.
Behavior induced by visual predation from fish.
Hypotheses include physiological reasons (e.g. UV avoidance) and adaptive responses related to food availability.
Many multivoltine zooplankton species exhibit changes in morphology in response to predation threats, aiding in survival.
Example Species: Daphnia pulex, Keratella sp.
Introduction of species like Alosa may alter community dynamics, reducing the size of dominant zooplankton species as part of ecological interactions.
Larger grazers tend to outcompete smaller ones, impacting food particle size, metabolic efficiency, and predator detection rates.
Key comparison in detection between Copepods (5-100 µm) and Cladocera (1-50 µm).
Bottom-up:
Dependent on nutrient and light availability leading to algal productivity.
Top-down:
Involves planktivores controlling herbivore populations through trophic cascades.
Clear vs Turbid waters are defined by factors such as nutrient levels and macrophyte presence, impacting light penetration and overall aquatic health.
Example shift observed in Lake Tåkern where high precipitation altered phytoplankton biomass which in turn affected water clarity.
Clear water stability favors macrophytes improving nutrient uptake and providing habitats for grazers.
Turbid states lead to shading of macrophyte shoots and a decline in herbivore refuges, prompting shifts in zooplankton community compositions.