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Mapping the supply and demand of ecosystem services: a first step towards multifunctional land management in eastern Amazonia 1 Farming Systems Ecology, Wageningen University and Research, The Netherlands 2 Centre de Cooperation Internationale en Recherche Agronomique pour le Développement, CIRAD, UPR AIDA, Montpellier, France. SupAgro, Univ Montpellier, Montpellier, France 3 National Institute of Agricultural Research (INTA), Modesta Victoria 4450, CC277, San Carlos de Bariloche, Argentina 4 Núcleo de Apoio a Pesquisa e Transferência de Tecnologias, NAPT Belém/Brasília, Embrapa Amazônia Oriental, Paragominas,PA Brasil. Paragominas is one of the oldest forest frontiers in eastern Amazonia. Forest clearing is now banned in the region prompting a transition towards land-use intensification. It is not clear, what the landscape configurations are that can reconcile ecosystem services with agricultural production for commodities. Conclusions Undisturbed forests fulfil the demand for C storage while pastures and secondary forests have the potential to meet the demand for C sequestration under the proper management. Assessing supply of habitat for biodiversity shows that even when complying with legislation, biodiversity can still decrease due to forest degradation and fragmentation. Most cleared areas available for production are located in sandy soils where intensification is more difficult and costly. Trade-offs could emerge in clayey soils covered by undisturbed forests if these are degraded and eventually converted to arable land. A bottom-up approach is needed to establish whether or not policies are representative of local demands to set concrete municipal targets for each soil function. This requires further research at the farm level that could inform a zoning process aiming at multi-functional landscapes that optimize soil functions in Paragominas. The aim of this study is to spatially assess the supply and demand of three soil-based ecosystem services (soil functions) to identify mismatches and trade-offs. We assessed the supply and demand for commodity production, habitat for biodiversity, and carbon cycling and storage based on the Functional Land Management framework. Supply was assessed based on a literature review for the various combinations of land use and pedo-morphological conditions. Indicators for supply included: i) carbon stocks (Mg C/ha), ii) species richness (α-biodiversity), and iii) export (US$ FOB, 2017) and local revenues (R$). Environmental policy targets were taken as proxy indicators of societal demands for the three soil functions in question. Wageningen University and Research P.O. Box 123, 6700 AB Wageningen Contact: [email protected] M +31 (0)6 29 16 03 40 www.wageningenUR.nl Objective & Method Daniel Pinillos 1, 2 , Felix Bianchi 1 ,René Poccard 2 , Marc Corbeels 2 , Pablo Tittonell 3 , Mário Rodrigo de Oliveira 4 , Rogier Schulte 1 Fig.3 Indicative maps of the Supply (top row) and Demand (bottom row) for Carbon Cycling and Storage, Habitat for biodiversity and Commodity production Undisturbed forests have the highest C stocks in above ground biomass, dead wood, litter and soil (Fig 3a). An area- based estimate of the mitigation potential for Paragominas during the 2010-2020 period, is 1 million Mg CO 2 eq, in order to reach the national target (Fig 3b). Supply of habitat for biodiversity is higher in areas with less forest fragmentation and disturbance (Fig.3c). Demand framed by policy mandates maintaining 50-80% forest coverage in all rural properties including riparian forests (Fig. 3d). Intensified production occurs mostly on clayey soils located in proximity to the road (Fig. 3e). Production targets are a 15-18% and 2-4% yearly increase for soybean and livestock production, respectively until 2030 (Fig. 3f). Introduction Results Acknowledgements This study is part of the project: Enhancing landscape eco-efficiencies through optimization of multiple ecosystem services along an Amazonian forest frontier in Paragominas, Brazil. Collaboration between CIRAD, Montpellier SupAgro and Farming Systems Ecology group in Wageningen University as part of the Erasmus Mundus program Agricultural Transformation by Innovation (AgTraIn). Fig.1 Landscape in Paragominas: a mosaic of abandoned pastures, crops, riparian forest and degraded forest. Fig.2 Erosion and degraded forest (a) and intensified areas of soybean production on a plateau of clayey soils (b) and beef production on sandy soils (c). Hotspots for C storage in undisturbed forest located on clayey soils Species richness varies with forest patch size, shape and fragmentation 50% - 80% forest coverage, zero deforestation and registration in the Rural Environmental Registry (CAR) is required for each rural property Most intensification occurs on clayey soils with easy access, but most available land is on sandy soils away from the road Soy concentrates in clay soil less than 20 km away from the road and beef production in sandy valleys located within 2 hours traveling time to the city. Carbon Cycling and Storage Habitat for biodiversity Commodity production a b c a b c d e f

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Page 1: ‘Mapping the supply and demand of ecosystems services: a ...€¦ · Daniel Pinillos 1, 2, Felix Bianchi 1,René Poccard 2, Marc Corbeels 2, Pablo Tittonell 3, Mário Rodrigo de

Mapping the supply and demand of ecosystem services: a first step towards multifunctional land

management in eastern Amazonia1Farming Systems Ecology, Wageningen University and Research, The Netherlands2 Centre de Cooperation Internationale en Recherche Agronomique pour le Développement, CIRAD, UPR AIDA, Montpellier, France. SupAgro, Univ Montpellier, Montpellier, France3 National Institute of Agricultural Research (INTA), Modesta Victoria 4450, CC277, San Carlos de Bariloche, Argentina4 Núcleo de Apoio a Pesquisa e Transferência de Tecnologias, NAPT Belém/Brasília, Embrapa Amazônia Oriental, Paragominas,PA Brasil.

• Paragominas is one of the oldest forest frontiers in easternAmazonia. Forest clearing is now banned in the regionprompting a transition towards land-use intensification.

• It is not clear, what the landscape configurations are thatcan reconcile ecosystem services with agriculturalproduction for commodities.

Conclusions• Undisturbed forests fulfil the demand for C storage while pastures and secondary forests have the potential to meet the demand for C sequestration under the

proper management.

• Assessing supply of habitat for biodiversity shows that even when complying with legislation, biodiversity can still decrease due to forest degradation andfragmentation.

• Most cleared areas available for production are located in sandy soils where intensification is more difficult and costly. Trade-offs could emerge in clayey soilscovered by undisturbed forests if these are degraded and eventually converted to arable land.

A bottom-up approach is needed to establish whether or not policies are representative of local demands to set concrete municipal targets for each soilfunction. This requires further research at the farm level that could inform a zoning process aiming at multi-functional landscapes that optimize soil functions inParagominas.

• The aim of this study is to spatiallyassess the supply and demand ofthree soil-based ecosystemservices (soil functions) to identifymismatches and trade-offs.

• We assessed the supply anddemand for commodity production,habitat for biodiversity, and carboncycling and storage based on theFunctional Land Managementframework.

• Supply was assessed based on aliterature review for the variouscombinations of land use andpedo-morphological conditions.

• Indicators for supply included: i)carbon stocks (Mg C/ha), ii)species richness (α-biodiversity),and iii) export (US$ FOB, 2017)and local revenues (R$).

• Environmental policy targets weretaken as proxy indicators ofsocietal demands for the three soilfunctions in question.

Wageningen University and Research P.O. Box 123, 6700 AB WageningenContact: [email protected] +31 (0)6 29 16 03 40

www.wageningenUR.nl

Objective & Method

Daniel Pinillos 1, 2, Felix Bianchi1 ,René Poccard2, Marc Corbeels2, Pablo Tittonell3, Mário Rodrigo de Oliveira4, Rogier Schulte1

Fig.3 Indicative maps of the Supply (top row) and Demand (bottom row) for Carbon Cycling and Storage, Habitat for biodiversity and Commodity production

• Undisturbed forests have the highest Cstocks in above ground biomass, deadwood, litter and soil (Fig 3a). An area-based estimate of the mitigation potentialfor Paragominas during the 2010-2020period, is 1 million Mg CO2eq, in order toreach the national target (Fig 3b).

• Supply of habitat for biodiversity is higherin areas with less forest fragmentation anddisturbance (Fig.3c). Demand framed bypolicy mandates maintaining 50-80%forest coverage in all rural propertiesincluding riparian forests (Fig. 3d).

• Intensified production occurs mostly onclayey soils located in proximity to the road(Fig. 3e). Production targets are a 15-18%and 2-4% yearly increase for soybean andlivestock production, respectively until2030 (Fig. 3f).

Introduction Results

AcknowledgementsThis study is part of the project: Enhancing landscape eco-efficiencies through optimization of multiple ecosystem services along an Amazonian forest frontier in Paragominas, Brazil. Collaboration between

CIRAD, Montpellier SupAgro and Farming Systems Ecology group in Wageningen University as part of the Erasmus Mundus program Agricultural Transformation by Innovation (AgTraIn).

Fig.1 Landscape in Paragominas: a mosaic of abandoned pastures, crops, riparian forest and degraded forest. Fig.2 Erosion and degraded forest (a) and intensified areas of

soybean production on a plateau of clayey soils (b) and beef production on sandy soils (c).

Hotspots for Cstorage inundisturbed forestlocated on clayeysoils

Species richness varies with forest patch size, shape and fragmentation

50% - 80% forest coverage, zero deforestation and registration in the Rural Environmental Registry (CAR) is required for each rural property

Most intensification occurs on clayey soils with easy access, but most available land is on sandy soils away from the road

Soy concentrates in clay soil less than 20 km away from the road and beef production in sandy valleys located within 2 hours traveling time to the city.

Carbon Cycling and Storage Habitat for biodiversity Commodity production

a

b c

a

b

c

d

e

f