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(1)

Bruno Locatelli (1,2), Sandra Lavorel (3), Ulrike Tappeiner (4), Sean Sloan (5),

Davide Geneletti (6)

Dynamics of ecosystem services driven by changes

in land-use intensity in mountains

(1) CIRAD France, (2) CIFOR Peru, (3) CNRS France, (4) U Innsbruck, Austria,  (5) James Cook U, Australia, (6) U Trento, Italy

(2)

 Tradeoffs between ES occur in space and time

(Anderson et al., 2009; Raudsepp-Hearne et al., 2010)

 Understanding temporal dimension of multiple

ES in a landscape (Bennett et al., 2009)

 Land intensification

– A major change in land management in the

last 50 years

– Rapid increases in agricultural yields but

decreases in biodiversity (Lambin et al., 2000)

– Major consequences on ES (Tscharntke et al., 2005)

– Knowledge is still limited on these

consequences (Swift et al., 2004)

ES dynamics and land

intensification

(3)

 Previous stylized models of ES supply as a function of

land management

– applied in global or regional ES assessments

(Burkhard et al., 2009; Schneiders et al., 2012)

 Example (by Braat and Ten Brink, 2008 and De Groot et al., 2010)

– variations of four types of ES

– along gradient of land-use intensity with 6 classes

(4)

Analyzing how temporal changes in

land-use intensity influence the

supply of multiple ES and the

tradeoffs among them, using

mountain landscapes as examples

– review case studies of ecosystem

services dynamics in mountain landscapes

– summarize their findings in a stylized

model of ES supply and tradeoffs along a gradient of land-use intensity

(5)

 Search in ISI Web of Knowledge

– papers quantifying multiple ecosystem services – in mountainous landscapes

– at two or more times.

 Only 18 selected publications, after rejecting studies with: – No quantitative data,

– No described land-use change,

– Small spatial scales (e.g. forest plot) – One single ecosystem service

(6)

Unused

grassland Grassland with recreational use or collection of wild  products Managed and  harvested  grassland Extensive  cropland or  pasture Intensive  cropland or  pasture Unused

forest Forest with recreational use or collection of non‐timber  forest products

Managed and  harvested natural 

forest

Extensive tree 

plantation Intensive tree plantation

Tr ee ‐dominat ed   land  uses Grass ‐dominat ed   land  uses G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Land‐use intensity

A typology of land uses needed for comparing cases.  

Differentiation between land uses dominated either by trees or grass 

(as in de Groot et al., 2010)

(7)

Results

 Case studies classified into 3 groups of land intensification

(“stories”)

– Story 1: Agricultural intensification (n=4) – Story 2: Forest intensification (n=3)

– Story 3: Extensification (n=11)

(8)

Story 1: Agricultural intensification

 Conversion of natural or

semi-natural ecosystems to croplands or pastures

 Often driven by food demand  Often in developing countries  Similar to the first phase of the

forest transition framework

 “Agricultural frontiers” First phase

(9)

Story 1: Agricultural intensification

Agricultur al   in te nsific at ion Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Temporal evolution of  land‐use intensity Food Timber ↑ ↓ Other prod Soil, water ↓ ↓ Carbon ? Spiritual ↓ Recreation Heritage ? ? Temporal evolution of  ecosystem services

(10)

Story 2: Forest intensification

 Expansion of forest plantations,

often intensively managed

 Examples in Chile, Ecuador, China  Drivers: forest or environmental

policies, wood market, carbon demand

(11)

Story 2: Forest intensification

Temporal evolution of  land‐use intensity Temporal evolution of  ecosystem services Fo re st   in te nsific at ion Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Food Timber ↓ ↑ Other prod Soil, water ? ↓ Carbon ? Spiritual ↑ Recreation Heritage ? ?

(12)

Story 3: Extensification

 Abandonment, rewilding and transformation to

multifunctional landscapes

 Drivers: More demand for regulation and cultural services

(water, recreation, landscape beauty), less demand for food (agricultural and trade policies)

(13)

Ext e nsific at ion Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Food Timber ↓ ↑? Other prod Soil, water ? ↑ Carbon ↑ Spiritual ↑ Recreation Heritage ↑ ↓? Temporal evolution of  land‐use intensity Temporal evolution of  ecosystem services

Story 3: Extensification

(14)

Agricultur al   in te nsific at ion Fo re st   in te nsific at ion Ext e nsific at ion Food Timber ↑ ↓ Other prod Soil, water ↓ ↓ Carbon ? Spiritual ↓ Recreation Heritage ? ? Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Tr ee Grass G0 G1 G2 G3 G4 T0 T1 T2 T3 T4 Intensity Temporal evolution of  land‐use intensity Temporal evolution of  ecosystem services Food Timber ↓ ↑ Other prod Soil, water ? ↓ Carbon ? Spiritual ↑ Recreation Heritage ? ? Food Timber ↓ ↑? Other prod Soil, water ? ↑ Carbon ↑ Spiritual ↑ Recreation Heritage ↑ ↓?

(15)

Evolution of ES in:

Tree‐dominated land Grass‐dominated land All land uses

(16)

AI AI AI AI AI Evolution of ES in: Tree‐dominated land Grass‐dominated land All land uses Changes in land‐use intensity: AI: Agricultural intensification

(17)

AI FI E E AI FI E AI E AI FI FI AI E E AI FI E AI FI AI E FI Evolution of ES in: Tree‐dominated land Grass‐dominated land All land uses Changes in land‐use intensity: AI: Agricultural intensification FI: Forest intensification E: Extensification FI

(18)

Conclusions

 Most common trade-offs:

– Increases in desired ES following intensification (food or timber) and declines in other ES

 Limitations

– Few studies, diverse approaches, different ES

 Simple stylized model

– Can be used in global modeling works – Communication tool on trade-offs

– Starting point in specific studies: what explains

divergence from the simple model?

– Could be tested in non-mountain areas

 Issue of scale and landscape heterogeneity

– E.g., agricultural intensification in some places

may coincide with, if not encourage, rewilding in others

(19)

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