Ecological Succession: A Comprehensive Overview
Ecological
succession describes the directional and continuous changes in species
composition and ecosystem processes over time. This blog dives deep into the
types of succession, the underlying mechanisms, the key changes that unfold,
and the concept of climax communities.
1. Types of
Succession
1.1 Primary
Succession
The gradual
colonization and establishment of living communities on substrates that have
never supported soil or vegetation. This process begins with abiotic
surfaces—such as bare rock, fresh lava, or newly exposed glacial till—and
unfolds through a series of biological and physical transformations that create
soil and habitat for progressively complex organisms (Clements, 1916; Chapin,
Matson, & Mooney, 2002).
- Initial Colonizers (Pioneer
Species): These are the first organisms to
arrive and establish on newly exposed or disturbed substrates lacking soil
and vegetation.
- Key Characteristics
- High dispersal ability
and rapid reproductive cycles to exploit open niches
- Tolerance to extreme
abiotic stresses (desiccation, temperature swings, nutrient scarcity)
- Simple structures that
demand minimal resources
- Ecological Roles
- Substrate modification:
lichens and mosses secrete organic acids that chemically weather rock,
initiating soil formation
- Nutrient enrichment:
nitrogen-fixing cyanobacteria and bacteria boost soil fertility, making
conditions viable for later colonists
- Microhabitat creation:
development of a thin organic layer retains moisture and buffers
temperature fluctuations
- Begin soil formation by
secreting organic acids that break down rock (Odum, 1969)
- Successional Mechanism
- Facilitation: pioneer
species alter the environment in ways that allow less hardy,
competitively superior species to establish (Connell & Slatyer’s
facilitation model)
- Examples
- Lichens and cyanobacteria
on glacial till and volcanic lava flows
- Mosses on newly exposed
rock faces
- Nitrogen-fixing bacteria
in barren sandy soils
- Successional Trajectory: The
sequential pathway and rate of ecosystem change characterized by orderly
shifts in species composition, structure, and ecosystem processes over
time. Key Features
- Directional
progression from simple to more complex communities
- Predictable stages:
pioneer, early successional, mid-successional, late-successional, climax
- Influenced by site
conditions, species interactions, disturbance history, and climate
- Underlying Processes
- Colonization and
establishment of new species
- Competitive replacement
and niche partitioning
- Feedback between biotic
communities and abiotic environment (e.g., soil development,
microclimate alteration)
- Ecological Significance
- Reflects ecosystem
resilience and recovery potential after disturbance
- Guides restoration
ecology by identifying reference trajectories for degraded landscapes
- Helps predict carbon
sequestration, nutrient cycling, and biodiversity trends through time
- Examples
- Primary succession on
Surtsey Island, Iceland: bare lava → lichens and mosses → grasses →
shrubs → birch woodlands over ~50 years
- Secondary succession in
abandoned Midwestern U.S. farmlands: herbaceous weeds → grasses and
legumes → shrubs → oak–hickory forest within 80–120 years
- Glacier Bay, Alaska:
Pioneer lichens colonize bare rock; over centuries, spruce–hemlock
forest forms (Chapin, Matson, & Mooney, 2002).
1.2
Secondary Succession
Secondary
succession describes the orderly and predictable series of community changes
that follow a disturbance in an area where soil and much of the original biotic
community remain intact. Unlike primary succession, the substrate already
contains organic matter, seeds, and root systems, allowing recovery to proceed
more rapidly through familiar stages of plant and animal colonization.
therefore, secondary succession takes place in areas where a preexisting
community was removed by disturbance, but soil and seed bank remain (e.g.,
abandoned farmland, burned forest).
- Initial Conditions:
- Soil structure, nutrients
and propagules are largely intact
- Faster recovery compared
to primary succession
- Successional Trajectory:
- Annual weeds and grasses
dominate first year post-disturbance
- Perennial herbs and shrubs
establish over 3–5 years
- Early successional trees
(e.g., birch, poplar) emerge within a decade
- Climax species (e.g., oak,
beech) replace pioneers over several decades
- Example:
- Abandoned agricultural fields in the
northeastern United States transition from grasses to oak–maple woodlands
within 50–100 years (Clements, 1916).
- Post-fire recovery in ponderosa pine
woodlands, where grasses and forbs give way to shrubs and young pines
within two decades
- Floodplain succession along the
Mississippi River, cycling between herbaceous swamps and bottomland
forests following periodic inundation
2.
Mechanisms of Succession
Connell and
Slatyer (1977) identified three primary mechanisms that drive species turnover:
- Facilitation:
- Early colonists modify the
environment, making it more habitable for subsequent species
- Example: Mosses retain
moisture and improve soil fertility, enabling vascular plants to
establish
- Tolerance:
- Later-arriving species are
neither helped nor hindered by pioneers; they simply tolerate existing
conditions better
- Example: Shade-tolerant
tree seedlings germinate under pioneer canopy and outcompete them over
time
- Inhibition:
- Early occupants actively
suppress establishment or growth of newcomers (e.g., through allelopathy
or resource preemption)
- Black locust (Robinia
pseudoacacia) fixes nitrogen and casts dense shade, inhibiting
understory herbs
3. Key
Changes During Succession
Ecological
succession is marked by predictable shifts in abiotic and biotic factors:
- Soil Development:
- Increase in organic
matter, nutrient availability and water-holding capacity (Odum, 1969)
- Species Richness and Diversity:
- Diversity typically rises
rapidly during early stages, peaks at mid-succession, and may decline
slightly as competitive dominants exclude others
- Biomass Accumulation:
- Net primary productivity
increases through mid-succession before leveling off at climax (Odum,
1969)
- Trophic Structure and Interactions:
- Complexity of food webs
and symbiotic relationships (e.g., mycorrhizae, pollinators) intensifies
over time
- Example:
- In abandoned fields, soil
carbon increases by 50–70% in the first 20 years, driving shifts from
herbaceous to woody species (Chapin et al., 2002).
4. Concept
of Climax Community
A climax
community is the stable, self-perpetuating endpoint of ecological succession
under a given set of climatic and edaphic (soil) conditions. At this stage,
species composition reaches a dynamic equilibrium where rates of colonization
and extinction balance, and ecosystem structure and function display minimal
directional change over time. So, A climax community is the endpoint of
successional change under a given climate and soil regime—a relatively stable
assemblage in dynamic equilibrium.
- Classical View (Clements, 1916):
- Succession culminates in a
single, stable climax determined by regional climate (“climatic climax”)
- Modern Perspectives:
- Poly climax Theory: Soil, topography and disturbance regimes create multiple
climax types within a region
- Climax Mosaic: Landscape comprises patches at different successional
stages, continually shifting due to disturbances (Pickett & White,
1985)
- Examples:
- Temperate deciduous forest
climax: oak–maple association in eastern North America
- Chaparral climatic climax: evergreen shrubs adapted to Mediterranean climate patterns
References
Chapin, F. S., Matson, P. A., & Mooney, H.
A. (2002). Principles of terrestrial ecosystem ecology. Springer.
Clements,
F. E. (1916). Plant succession: An analysis of the development of
vegetation. Carnegie Institution of Washington.
Connell, J.
H., & Slatyer, R. O. (1977). Mechanisms of succession in natural
communities and their role in community stability and organization. The
American Naturalist, 111(982), 1119–1144.
Odum, E. P.
(1969). The strategy of ecosystem development. Science, 164(3877),
262–270.
Connell, J.
H., & Slatyer, R. O. (1977). Mechanisms of succession in natural
communities and their role in community stability and organization. The
American Naturalist, 111(982), 1119–1144.
Pickett, S.
T. A., & White, P. S. (Eds.). (1985). The ecology of natural
disturbance and patch dynamics. Academic Press.
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