Download Land use change trends and Impact on Mountain

Survey
yes no Was this document useful for you?
   Thank you for your participation!

* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project

Document related concepts
no text concepts found
Transcript
Land use change trends and Impact on
Mountain Biodiversity:
a global perspective
Eva Spehn
Global Mountain Biodiversity Assessment
of DIVERSITAS
Land use change & Mountain biodiversity
Most wide spread utilization of mountain terrain:
• Upland grazing,
• often facilitated by fire management
• often followed by erosion and enhanced risk for valley and foreland
environments.
Most land use changes reduce mountain biodiversity, especially:
• Cultivation of formerly pristine areas
• Intensification of agriculture/husbandry in montane areas
• Abandonment of formerly grazed montane & alpine grasslands
Biodiversity in the
European Alps
Intensification
Two opposite trends:
Abandonment
Stöcklin J, Bosshard A, Klaus G, RudmannRudmann-Maurer K, Fischer M (2006)
Land cover change
-> consequences for
biodiversity
© Silvia Vananderoye
Stöcklin J, Bosshard A, Klaus G, RudmannRudmann-Maurer K, Fischer M (2006)
Land use change and mountain biodiversity
Focus: (sub)tropical mountains
•
•
•
•
2 Workshops: Moshi,Tanzania 2002 & La Paz, Bolivia 2003
Research Agenda (2005)
Synthesis book (2006)
Network of
field experiments 20052005-
Financed by
• Swiss Agency for Dev. and Cooperation SDC,
• Food and Agricultural Organisation FAO
• Swiss National Science Fondation
GMBA Moshi-La Paz Research Agenda (2005)
Providing priority research questions on land use effects on
mountain biodiversity, specifically on :
• The use of highland vegetation and husbandry systems (food)
• Fire ecology
• Highland cropping, hunting and gathering, and medicinal plants
• Regeneration and re-vegetation outside forests
• Upper montane forest and high elevation treelines (fiber and fuel)
• Cross cutting research issues: Hydrology and erosion, interactions
of land use with climate change, indigenous knowledge
Land use change & Mountain biodiversity
Synthesis book:
Studies of fire and grazing effects on mountain
biodiversity in:
Andes (Argentina, Bolivia, Colombia, Peru,
Venezuela)
African Mountains (Tanzania, Uganda,
Madagascar, South-Africa)
Alps, Caucasus, Pamir, Himalaya, Snowy
Mountains
How does fire intensity or fire frequency in mountains
affect biodiversity?
Increase of Fire frequency at Kilimadjaro:
from
Podocarpus forest
to Erica bushes:
the loss of a life form (trees)
(Hemp 2006, in Spehn, Liberman & Körner: Land use change and mountain biodiversity)
Fire effects on mountain biodiversity:
• Burnt areas are commonly poorer in species than unburnt
areas (especially in uniform plots and if unburnt control
contains forest)
• Fire leads to degradation (e.g. of Paramo tussocks) if the
regeneration takes longer than the burning frequency.
• Woody components become eliminated or very uniform (Erica
(Erica
shrub in African mountains)
• Moderate fires do not necessarily reduce plant cover and
diversity, but induce a change in ecosystem functioning (e.g.
Kilimanjaro: lost of cloud water trapping by destruction of Erica
forest)
How do changes in grazing regime in mountains
affect biodiversity?
• How does grazing and the pace of land use changes in
mountains enhance or reduce biodiversity?
Grazing effects on mountain biodiversity
• Moderate grazing increases plant species diversity at local
scale, as herbivory increases the competitive ability of other
taxa ((Intermediate
Intermediate disturbance hypothesis)
hypothesis)
• Grazing of high elevation grassland with a long history of
ungulate presence commonly has little impact on biodiversity
as long as stocking rates do not cause highly palatable species
to disappear
(Sarmiento et al; Bustamante et al; Rawat & Adhikari 2006,
in Spehn, Liberman & Körner: Land use change and mountain biodiversity)
Sustainable grazing management in subtropical highlands
Appropriate stocking rates:
• Best indicator is the abundance of lessless-palatable dominants vs.
highlyhighly-palatable subdominants (robust vs. nutritious species)
• Key role of marshmarsh-type meadows (dry parts of Inner
Inner--Himalaya;
bofedales in the Andes) during dry periods: their capacity
determines the total stocking rate of a region.
Appropriate animal selection:
• “Picky animals” (cattle, sheep, alpaca) have much stronger
impact on diversity and pasture quality than species with a
broad food selection (e.g. llama).
(Bustamante et al; Alzerreca et al., Molinillo & Monasterio 2006,
in Spehn, Liberman & Körner: Land use change and mountain biodiversity)
Interaction effects of fire and grazing on biodiversity
Joint Research Projects established on
Land use, mountain biodiversity and
ecosystem services:
services:
European Alps (Switzerland, Austria, and France)
Caucasus (Georgia)
Andes (Altiplano/Bolivia)
Himalayas (Tibet/China)
www.gmba.unibas.ch