In principle: all organisms living in a particular place
Spatially explicit & different spatial scales
More generally: restricted to a subset of organisms such as taxonomy or trophic level.
Main Aims of Community Ecology
Explaining and predicting the distribution and abundance of species in time and space.
Considering abiotic and biotic factors and underlying mechanisms
Quantifying patterns and looking for general results (e.g., species-area relationships).
Studying dynamics of communities and response to disturbance.
Why is it Important?
Common approach in ecological research from m2 to km2. Species interactions are key, so studying multiple species is important.
Much ecological theory has been developed at this scale.
Important for conservation and habitat management, classification, biomonitoring, and diagnostics (e.g., National Vegetation Classification (NVC), River Invertebrate Prediction and Classification System (RIVPACS)).
Criticism of the Community Concept
Most research is at a single scale: ‘local community’.
Implicit assumption that the community is closed with arbitrary boundaries.
Reflects differences expressed by Clements (community is discrete) and Gleason (individualistic view).
In reality, different processes act at different scales, and local communities are affected by processes at larger scales.
The Meta-Community
A set of communities linked by dispersal, with multiple interacting species.
Recognizes that processes occur at different scales.
Analogous to population vs. meta-population.
The community is viewed in the regional context, considering neighboring communities and a regional species pool from which species can immigrate.
Local dynamics are affected by dispersal among communities.
Describing Communities
Ecological networks
Temporal change
Diversity, composition…
Environmental change, community response, resilience & stability
Assembly rules
Describing Communities: Four Basic Properties
Abundance distributions
Evenness and dominance
Richness
Composition
Evenness and Dominance
Describe how total abundance is distributed among species.
More even = ‘more diverse’.
Many diversity indices (e.g., Shannon-Weiner) combine evenness with species richness.
Simpson’s evenness ranges from 0 to 1, where 0 indicates low evenness (one/few species dominate) and 1 indicates high evenness (species equally abundant).
Richness
Number of species in a community.
Simplest concept but most challenging to measure. Most species in a community are rare (low abundance) = low detection probability.
More individuals in a sample (or more samples) → more species likely to be found.
Difficult to separate the role of sampling effort and greater abundance.
Richness – Three Strategies
Use 'species density'
Estimators of total richness (e.g. Chao indices)
Rarefy the data
Comparing Communities
Compare richness, evenness, etc.
Summarise overall differences in composition using Ordination methods (e.g., NMDS - 'Non-metric multidimensional scaling').
Comparing Communities: Process
Start with a species x site matrix.
Calculate a distance matrix to summarise differences in the abundance of all taxa between each site pair.
Use Bray-Curtis or Jaccard dissimilarity metrics (0 = identical, 1 = no species in common).