Species Dominance Calculators
0 calculators tagged with “Species Dominance”
All Calculators
No calculators found for this topic.
Measuring Dominance
Berger-Parker Dominance Index: d = N_max / N_total (relative abundance of the most common species). d = 1.0 if one species has all individuals; d = 1/S if perfectly even.
Simpson's D: D = Σpᵢ² (probability that two random individuals are the same species). High D = high dominance = low diversity.
Importance Value (IV) in plant ecology: IV = (relative density + relative frequency + relative basal area) / 3. Maximum IV = 100/S for a perfectly even community; dominant tree species typically have IV = 30–70 in temperate forests.
Dominant vs. Keystone Species
Dominant species: high abundance or biomass; controls community by its own sheer numbers (e.g., black spruce in boreal forest; bluegrass in grasslands). Keystone species: has disproportionate effect on community structure RELATIVE TO its abundance — often a predator or engineer (sea otter, gray wolf, beaver). A dominant species may or may not be a keystone species; they are distinct concepts.
Ecological Role of Dominant Species
Dominant species set the physical environment (canopy species control light to understory), dominate nutrient cycling (high-biomass species contribute most litter), and can suppress less competitive species. Loss of a dominant species can dramatically restructure communities (chestnut blight eliminated American chestnut dominance in eastern US forests in the 20th century).
Glossary
Frequently Asked Questions
Species dominance is the degree to which one or a few species dominate a community in abundance, biomass, or importance. Key measures: (1) Berger-Parker index d = N_max/N_total (proportion of individuals in the most common species; ranges 1/S to 1). (2) Simpson's D = Σpᵢ² (probability of two random individuals being the same species; high D = high dominance). (3) Importance value (IV) in forestry = (relative density + relative frequency + relative basal area)/3; ranges 0–100 for each species in a community. High dominance means low diversity and high community dependence on one species.
A dominant species has high relative abundance or biomass — it controls the community by sheer numbers and the physical/chemical environment it creates. Examples: spruce and fir in boreal forests; Sphagnum moss in bogs; Spartina grass in salt marshes. A keystone species has a disproportionately large effect on community structure relative to its abundance — often a predator that controls prey populations. Examples: sea otters (control sea urchins → protect kelp forests); wolves (trophic cascade in Yellowstone); fig trees (provide fruit year-round supporting many frugivores). A dominant species can be a keystone species, but many dominants are not keystones, and many keystones are not numerically dominant.
Importance value (IV) = (relative density + relative frequency + relative basal area)/3, or sometimes the sum (not divided by 3) depending on the source. Each component is expressed as a percentage: relative density = (species count / total count) × 100; relative frequency = (plots where species occurs / total plots) × 100; relative basal area = (species BA / total BA) × 100. When summed: total IV for all species = 300; when averaged: 100. A tree species with IV = 50 is highly dominant. IV was developed by Curtis and McIntosh (1951) for characterizing forest communities and is widely used in plant community surveys globally.
Dominant species disproportionately drive ecosystem processes: litter production and quality (dominant tree species contribute most litter and determine decomposition rates and N cycling); canopy structure (dominant overstory species set light regimes for understory organisms); soil chemistry (root exudates and mycorrhizal associations of dominant species influence soil microbial communities); and productivity (dominant species often have the highest biomass and photosynthesis rates). Loss of dominant species can be ecologically catastrophic — the near-elimination of American chestnut from eastern US forests by chestnut blight dramatically altered forest structure and the wildlife depending on chestnut mast (acorn-like fruit).