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Plant Succession

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SUCCESSION
Virtually all plant communities experience, from time to time, disturbances that remove all or some of the plant biomass. Thus, diversity is influenced heavily by disturbance

=is the directional change in community composition and structure over time.

• "begins" when a disturbance is followed by colonization or re-growth of the disturbed site by plants

• Natural, gradual changes in the types of species that live in an area; can be primary or secondary • The gradual replacement of one plant community by another through natural processes over time
Causes of Plant Succession • Autogenic succession (2 types) can be brought by changes in the soil caused by the organisms there. These changes include accumulation of organic matter in litter or humic layer, alteration of soil nutrients, change in pH of soil by plants growing there. The structure of the plants themselves can also alter the community. For example, when larger species like trees mature, they produce shade on to the developing forest floor that tends to exclude light-requiring species. Shade-tolerant species will invade the area. • Allogenic changes are caused by external environmental influences and not by the vegetation. For example soil changes due to erosion, leaching or the deposition of silt and clays can alter the nutrient content and water relationships in the ecosystems. Animals also play an important role in allogenic changes as they are pollinators, seed dispersers and herbivores. They can also increase nutrient content of the soil in certain areas, or shift soil about (as termites, ants, and moles do) creating patches in the habitat. This may create regeneration sites that favor certain species.

2 main types of Autogenic successions • Primary Succession: The process of creating life in an area where no life previously existed. • an area in which a community has never lived before, would be a new lava or rock from a volcano that makes a new island • Secondary Succession: The process of re-stabilization that follows a disturbance in an area where life has formed an ecosystem. • in habitats where communities were entirely or partially destroyed by some kind of damaging event. • When an existing community has been cleared by a disturbance such as a fire, tornado, etc...and the soil remains intact, the area begins to return to its natural community. Because these habitats previously supported life, secondary succession, unlike primary succession, begins on substrates that already bear soil. In addition, the soil contains a native seed bank. • Since the soil is already in place, secondary succession can take place five to ten times faster than primary succession. • Circle of life: disturbance(grasses(shrubs(small trees(climax forest • The Climax Community • A climax community is a mature, stable community that is the final stage of ecological succession. In an ecosystem with a climax community, the conditions continue to be suitable for all the members of the community. • Any particular region has its own set of climax species, which are the plants that are best adapted for the area and will persist after succession has finished, until another disturbance clears the area.
Species Traits determine the course of succession
Absence of disturbance
-late successional sp eventually outcompete by reducing resources (light and nutrients) beneath the level required by early sp
4 Underlying Mechanisms Early species persists: 1. Competition-colonization trade off Dispersal ability, high fecundity(colonize and establish in recently disturbed sites b4 late sp can arrive; OR 2. Successional niche Rapid growth in unshaded conditions allows them to temporarily outcompete late sp even if these arrive at same time ; conditions suit partic sp b/c of their niche reqm’t Facilitation -some early sp change abiotic enviro by providing shades or improving soil quality -that make it easier for late sp to estab and thrive -a factor that induce sp switches during many successions Enemy-interaction theory -herbivory can slow or stop a successional sequence in its tracks -predation on seeds/mature vegetation can slow or stop a successional niche and facilitation

Intermediate Disturbance Hypothesis

=proposes that biodiversity is highest when disturbance is neither too rare nor too frequent.
- A)highest diversity of species in an ecosystem is maintained by a level of disturbance intermediate between frequent and rare disturbance
- B)If disturbance is frequent the succession may fail to develop beyond the pioneer phase.
-C)If disturbance is rare, the climax will be established and diversity reduced according to the competitive exclusion principle.
-D)At intermediate levels of disturbance, the arrival of new species will increase diversity in proportion to the interval between disturbances.

RESTORATION FOR PLANTS
Diagram of dynamics of a patch of prairie in a shifting mosaic landscape
-where each patch experiences similar but out-of-phase dynamics
Oval=key factors
Squares=communities within a single patch in relation to time since fire disturbance
Solid arrow=positive/negative feedbacks in which plant community struc is influencing probab of fire & grazing

Shifting prairie mosaic
-probab of fire greatest where a large biomass has accumulated during a period without fire
-recently burned patches w/ dominant tallgrass vegetation, tend to attract grazing animals (eg. Bison) that reduce grass biomass, increase amt of bare ground, shift plant community towards non-grass herbaceous sp
(these changes reduce likelihood of fire and of further grazing (b/c animals now move to more recently burnt areas)
-patch then shifts back to a tall grass succesional stage, again increasing likelihood of fres + grazing, together produce a shifting a mosaic across landscape, enhacing heterogeneity + promoting biodiversity

Goal of restoration
-a relatively stable + homogenous successional stage
Aim: to restore land previously under agriculture, human need not intervene (+ wait for natural succession)
Eg. Abandoned rice fields: annual grass(forbs(rushes, willows(species rich and stable alder woodland (10-50 yrs)

RESTORATION FOR ANIMALS
Tidal Salt Marshes = between land and salty water, dominated by dense stands of halophytic (salt-tolerant) plants such as herbs, grasses or low shrubs -These plants are essential to the stability of the salt marsh in trapping and binding sediments. -Salt marshes play a large role in the aquatic food web and the exporting of nutrients to coastal waters. - provide support to terrestrial animals such as migrating birds as well as providing coastal protection
-much rarer now b/c many have been drained for agriculture or b/c of tidal cycles have been obstructed by tide gates, culverts and dykes
-restoration of tidal action: links between marshes + coastal system leads to recovery of salt marshes vegetation (allogenic succession); salt marsh animals follow a comparable timetable
-can be speed up by actively planting salt marsh sp, but certain ecosystem properties (C, N content of marsh soil) don’t recover as quickly as others (deposition of fine sediment) -Hydrology: (sedimentation/rates of C, N accum in soil) quickly restored -rate of production of biomass + decomposition: slower recovery -soil development (total amt of C, N in soil): slowest recovery of all

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