Lecture 33: Community Change

expedln.gif (193 bytes)

Reading:  Economy of Nature, pp. 521-545.

expedln.gif (193 bytes)

Community Change

Cyclical: Seasonal
Temporal: Succession
Spatial: Environmental Gradients

 

Seasonality

Terrestrial Communities

Cold - Warm
Wet - Dry
Leaf drop (deciduous plants) in the adverse climatic season Flowering Times: Biological seasons, non-overlapping flowering times may be driven by competition between plants for pollinators (a limited resource).

Aquatic or Marine Communities

Nutrient Rich - Poor
Cold - Warm

 

Succession

Succession is directional change in community species composition in ecological time (102 years maximum time span).

Primary: Starting from bare rock, simultaneous formation of soil with community development and change.

Factors:

climate, time, topography, organisms available, parent (rock) substrate

Abiotic and biotic weathering: erosion of parent material

Soil formation involves accumulation of organic matter along with weathering of the parent substrate.

Soil types and vegetation types (community formations)

Close parallels except among forests and rain forests

Secondary: Starting with soil already present, results when existing vegetation is destroyed leaving soil intact.

In either type of succession, vegetation changes until a stage of equilibrium is reached, the climax stage, which is the final stage of succession at a given site.

 

Successional equilibrium or Climax Community

Self-perpetuating, stable community

Monoclimax: Climate alone important, a given area has only one climax type, so similar sites in a given area will have similar climax communities.

Polyclimax: Different climax communities possible in a given area, soil moisture, nutrients, and biotic factors determine the kind of climax community at a given site in addition to climate.

Climate is not a constant, so succession can be viewed as a constant process.

Mechanisms of successional change

Facilitation (Monoclimax) Relay Floristics

  • Species replace one another due to sequential modification of the environment. The environment is changed by resident species making it less suitable for residents and more suitable for colonists.
  • Fixed orderly sequence of replacements
  • Competition with dominants (new colonists) prevailing
  • Early succession necessary for later succession
  • Facilitation applies best to primary succession.

Tolerance (Monoclimax)

  • Early successional species are not necessary to start the successional sequence. Any species (for community type) can start succession), but some species are competitively dominant to others. The dominant species predominate in the climax community.
  • Species replaced by others more tolerant to limiting resources
  • Species replacement not a function of present residents
  • Residents tolerate colonists

Tolerance applies best to secondary succession, large scale (old field, clear-cut, forest fire recovery).

Inhibition (Polyclimax)

  • Species replacements are not orderly as residents attempt to exclude new colonists. Succession depends on which species arrive and become established first.
  • Species replacements result from residents being damaged or killed
  • Any replacement is possible
  • Succession is generally from short lived to long lived species

Inhibition applies best to secondary succession, small scale (tree fall in a mature forest, small patch colonization in a rain forest).

General trends in plant communities in early and late successional stages (after Ricklefs, 1996, p 537, Table 23.2).

Characteristic

Early Succession

Late Succession

Number of seeds

many

few

Seed size

small

large

Seed dispersal

wind, stuck to animals

gravity, eaten by animals

Seed viability

long

short

Root:shoot ratio

small

large

Growth rate

rapid

slow

Mature size

small

large

Shade tolerance

low

high

Species richness

low

high

Abundance uniformity

low

high

Spatial heterogeneity

low

high

Specialization

little

much

Production

"quantity" (r)

"quality" (K)

Community stability

low

high

expedln.gif (193 bytes)

Copyright 1999 Northern Arizona University
ALL RIGHTS RESERVED