Abandoned pastures above the treeline often return directly to a vegetation similar
to the natural state without a sequence of intermediate plant communities. But it may take a very
long time for the vegetation of a fertilized pasture to return to a condition resembling the natural
vegetation.
On less productive, steep slopes, exclusion of livestock may be advantageous in reducing erosion
and increasing species richness. Yet, on other habitats, exclosure of cattle may lead to reduced
above-ground biomass and reduced abundance of rare forbs.
Below the treeline, succession generally passes through different stages before climax
vegetation is reached. Abandonment of grazing is usually followed by a stage of tall grasses and
forbs. This vegetation may enhance a particular type of erosion: this occurs in winter when snow
freezes to the long plants and uproots them as the snow-pack creeps downslope (turf-erosion).
During the next stage, characterised by scrub encroachment, there may also be an increased risk of
avalanches as a result of thicker snow accumulations on the upper slopes.
The risky transition period back to a more stable ecosystem
without domestic livestock may take at least half a century, but sensitivity varies greatly with
slope and vegetation type.
When alder, dwarf shrubs and young trees overgrow pastures, a general stabilisation
of the terrain occurs. Total runoff during an artificial rainfall experiment on an abandoned pasture
covered by a dense stand of green alder was only about 16%, whereas it was between 35 and 71% on an
adjacent, intensively managed pasture.
Complete abandonment would lead to a reduction in vegetation types
and species richness.
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