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two scenarios of alternate stable states
1: community 1 and 2 branch off from initiating disturbance; 2: community 1 branches from initiating disturbance and community 2 branches off community 1
two alternate stable states for low elevation chihuahuan desert
state 1 historic: black grama grassland state 2 degraded: woody shrubland
alternate stable states
occur when an ecosystem can exist in 2 or more configurations under same environmental conditions
even with grazers removed from the community
does not return to desert grassland
why do we need to manage reserves example
kirtland’s warbler
kirtland’s warbler
rare; nests only in early successional jack pine forests
minumum dynamic area
smallest area large enough to encompass patches in different stages of succession following disturbance
first important question for managing disturbance regimes in reserves
how far back in time do we need to go to simulate a natural disturbance regime?
second important question for managing disturbance regimes in reserves
how can we determine the intensity, frequency and spatial extent of natural disturbances?
tree ring fire scar analysis
allows re-construction of historical fire regimes in forest, woodland, and savanna communities
historical record is limited by
tree lifespan
first potential conflicting goal of livestock raising vs grassland biodiversity conservation
dealing with disturbances in grasslands: fire and drought
second potential conflicting goal of livestock raising vs grassland biodiversity conservation
predator control/eradication
third potential conflicting goal of livestock raising vs grassland biodiversity conservation
maximizing livestock biomass production vs avoiding overgrazing
overgrazing
grazing at an intensity that causes undesirable changes in the species composition of the plant community and reduced productivity of the ecosystem
ice cream plant
first plants to experience population declines when a site is grazed; often legumes high N content
decreasers
plants that tend to decrease in abundance with greater grazing pressure; often tall perennial grasses and forbs
increasers
plants that tend to increase in abundance with greater grazing pressure; often short grasses and annuals
invaders
species do not establish in ungrazed areas, but do establish under heavy grazing; often chemically or mechanically defended against herbivores
will removal of grazing allow and overgrazed pasture to return to high species biodiversity and high productivity?
probably not but there may be alternate stable states
first way in which cattle grazing does not simulate effects of native grazing mammals, and can produce over-grazing
different needs for water-degredation of riparian zones
solution for different needs for water-degredation of riparian zones
raise native grazers, establish water tanks in uplands, fence livestock out of riparian zones
second way in which cattle grazing does not simulate effects of native grazing mammals, and can produce over-grazing
unusually high herbivore densities
solution to unusually high herbivore densities
maintain lower stocking densities
third way in which cattle grazing does not simulate effects of native grazing mammals, and can produce over-grazing
livestock not allowed to migrate
solution to livestock not being allowed to migrate
rotate livestock among pastures, ensure that the rotation avoids individual pastures always being grazed in the same season