How to Calculate Beta Diversity and Interpret the Results

Understanding Beta Diversity

Biodiversity, the variety of life on Earth, is a fundamental concept in ecological studies. While alpha diversity measures the species richness within a single location, and gamma diversity represents the total species richness of a broad region, beta diversity offers a distinct perspective. It focuses on the differences in species composition between different sites or communities.

Beta diversity quantifies how species composition changes across space or over time, revealing the dissimilarity between ecological communities. It measures the extent of species turnover, indicating how many species are replaced by different species as one moves from one habitat to another. This ecological metric helps researchers understand patterns of species distribution and the factors that influence them.

The study of beta diversity is valuable for understanding environmental gradients, such as changes in elevation or soil type, which often lead to shifts in species composition. It also provides insights into the impacts of habitat fragmentation, where isolated patches of habitat may develop unique species assemblages. Furthermore, beta diversity can help assess the effects of disturbances, like wildfires or pollution, by revealing how communities change following such events.

Common Beta Diversity Metrics

When quantifying beta diversity, ecologists employ various metrics. These metrics broadly fall into two categories: those based on species presence or absence and those that incorporate species abundance data. The choice of metric depends on the specific research question and the nature of the ecological data.

Presence-absence based metrics consider only whether a species is present or absent in a given site. The Jaccard index, for example, measures dissimilarity by focusing on species unique to one site compared to the total number of species found across both sites. A higher Jaccard dissimilarity indicates fewer shared species between the two communities.

Another common presence-absence metric is the Sørensen index, which gives more weight to shared species than to species found only in one community. Both Jaccard and Sørensen are useful for understanding fundamental species turnover, irrespective of population sizes.

Abundance-based metrics, in contrast, consider not only the presence or absence of species but also their relative abundances within each community. The Bray-Curtis dissimilarity is a widely used abundance-based metric that quantifies differences in species composition by comparing the number of individuals of each species present in two sites. This metric reflects both species turnover and variations in species dominance. A high Bray-Curtis value suggests substantial differences in both the types and quantities of species between communities.

Step-by-Step Calculation Process

Calculating beta diversity typically involves a systematic workflow, beginning with the organization of ecological data. The first step requires compiling species data into a species-by-sample matrix, often called a community matrix. In this matrix, rows usually represent different species, columns represent individual samples or sites, and the cells contain either presence/absence information (e.g., 0 or 1) or the abundance of each species in each sample.

Following data preparation, the next important decision is selecting the appropriate beta diversity metric, as discussed previously. This choice is guided by the research question and whether the focus is on simple species turnover or also on differences in species abundances. For instance, if understanding changes in overall community structure, including dominant species, is important, an abundance-based metric would be more suitable.

Once the metric is chosen, beta diversity is calculated as a pairwise comparison between every possible pair of samples or sites. This means that if you have multiple sites, the calculation will determine the dissimilarity between each site and every other site until all unique pairs have been compared. Each comparison yields a single dissimilarity value.

These calculations are rarely performed manually due to their complexity and the large number of comparisons often involved. Instead, specialized software and programming environments are commonly employed. Tools such as R, with packages like ‘vegan’, and commercial software like Primer-E, automate the calculations.

The output of these calculations is typically a dissimilarity matrix. This square matrix displays the beta diversity value for each pairwise comparison, with rows and columns representing the different samples or sites. The values within this matrix quantify the ecological distance or dissimilarity between each pair of communities, forming the basis for subsequent analyses and interpretations.

Interpreting Beta Diversity Results

After the beta diversity values have been calculated, understanding their meaning is the next step in drawing ecological conclusions. The numerical output from beta diversity metrics directly reflects the degree of compositional difference between communities. Generally, a higher beta diversity value indicates greater dissimilarity or more significant species turnover between the two compared sites.

Conversely, lower beta diversity values suggest that the communities being compared are more similar in their species composition. This similarity might stem from shared environmental conditions, historical connections, or a lack of dispersal barriers. Interpreting these values helps ecologists determine how unique or similar different habitats or regions are in terms of their biological communities.

The dissimilarity matrix, containing all the pairwise beta diversity values, often serves as the input for further analytical techniques. Researchers frequently use ordination plots, such as Non-metric Multidimensional Scaling (NMDS), to visually represent these relationships. In such plots, sites that are ecologically similar appear closer together, while dissimilar sites are plotted further apart, providing a spatial understanding of community differences. These visualizations, along with clustering analyses, help identify similar community groups and the environmental or spatial factors driving beta diversity patterns.