What if? prospects based on Corilis Alex Oulton, Manuel Winograd Ronan Uhel & Jean-Louis Weber LAND QUICK SCAN INTERFACE: Challenges and needs Internal.

Slides:



Advertisements
Similar presentations
Applications jlw, 17 February INDEXES OF TEMPERATURE IN NATURA 2000 SITES.
Advertisements

Overview at the European scale of potential impacts of TEN-T axes on core areas of nature protection and landscape connectivity – neighbourhood analysis.
Workshop on Climatic Analysis and Mapping for Agriculture
Building of Research Team in the Field of Environmental Modeling and the Use of Geoinformation Systems with the Consequence in Participation in International.
Spatial analysis tools for biodiversity indicators on habitats and ecosystems Expert meeting on multi-scales mapping and integrated analysis of landscape.
What if? Agro-fuel scenario Case of fallow land/set aside at risk of re-intensification Version 0.01 _ zoom on Czech Republic What if? modelling.
Marta Pérez-Soba Han Naeff Janneke Roos Wim Nieuwenhuizen Alterra, The Netherlands Haarlem, 22nd March 2002 Use of national data to improve the localisation.
Raster Based GIS Analysis
Mapping the future Converting storylines to maps Nasser Olwero GMP, Bangkok April
1 REGIO gis The use of geostatistics for the analysis of Europe’s regions Hugo Poelman European Commission – DG Regional Policy
Eurosion and Conscience projects - brief overview Tom Bucx (Deltares) 9 June 2011 EEA Expert meeting Methods and tools for assessing.
Experimental Ecosystems/Natural Capital Accounts for Mauritius, 2000 – 2010 Collection of maps Jean-Louis Weber, Nov
Center for Watershed Protection USDA Forest Service, Northeastern Area, State and Private Forestry How to estimate future forest cover in a watershed.
MARS Geodatabase (5.1.1): and Pressure data Ljubljana.
Spatial data for integrated assessment of urban areas Andrus Meiner European Forum for Geostatistics 12 October 2011, Lisbon.
ESPON seminar on May 2005 Luxembourg EEA’s contribution to spatial assessments: CORINE land cover 2000 & Land Accounts Stefan Kleeschulte, Project.
Efficient/ non efficient use of ecosystem resources: first results from ecosystem capital accounts Jean-Louis Weber & Emil Ivanov.
The Implementation of Land and Ecosystem Accounts in Europe Towards integrated land and ecosystem accounting Roy Haines-Young, University of Nottingham.
Changes in Floods and Droughts in an Elevated CO 2 Climate Anthony M. DeAngelis Dr. Anthony J. Broccoli.
1 Expert workshop on components of EEA Ecosystem Capital Accounts (ECA) Focus on biomass carbon and biodiversity data 24/03/2015.
1 Expert workshop on components of EEA Ecosystem Capital Accounts Focus on biomass carbon and biodiversity data 24/03/2015.
Session ‘Governing effective land use using environ. accounting approaches’ Harmonised geo-spatial information for improved land governance Geertrui.
Corine land cover, Land accounts and scenario development An introduction Jean-Louis Weber & Ferràn Paramo 26 February 2003.
Resource efficiency indicators: material resource use and ecosystem capital maintenance Jean-Louis Weber Special Adviser Economic-Environmental Accounting.
Presentation of Land Accounts JLW. LEAC Home Introduction to land accounts Nomenclatures and definitions Spatial Assessments Builder Methodology, bibliography.
Introduction to Spatial Calculation Estimation of Areas Susceptible to Flood and Soil Loss.
The Natural Capital/Ecosystem Capital Accounting (ECA) project for Mauritius Implementation of SEEA-Ecosystem Capital Accounts in Mauritius Methodology.
EEA 2006 Accounts Update Tables. PART 1 Table 1.1: Classifying land cover and land cover change for land accounting.
Integrating biodiversity measurements, assessments and policy responses in an ecosystem capital accounting framework. J-L Weber, R. Spyropoulou, A.T. Peterson.
JRC-AL – Bonn on Disaggregation of CAPRI results Renate Köble Adrian Leip.
Review of the ecosystem condition account
European Environment Agency Land and Ecosystem Accounting 2008 Demonstration of Agro-Fuel and Urban Intensification Modelling Scenarios using Existing.
1 Land accounts in Europe – current state and outlook Land accounts 01/10/2015 Daniel Desaulty
Technical Details of Network Assessment Methodology: Concentration Estimation Uncertainty Area of Station Sampling Zone Population in Station Sampling.
The Natural Capital/Ecosystem Capital Accounting (ECA) project for Mauritius Production of the urban areas land cover layer from high resolution data on.
Remote Sensing Theory & Background III GEOG370 Instructor: Yang Shao.
Slides on land accounts of Ireland prepared for Bridging The Gap Dublin April 2004 JLW.
Downscaling of European land use projections for the ALARM toolkit Joint work between UCL : Nicolas Dendoncker, Mark Rounsevell, Patrick Bogaert BioSS:
NERI Roskilde Tuesday, May 18 th 2004 EEA activities and projects on spatial analysis and land accounting Jean-Louis Weber, EEA LANDSCAPE EUROPE Seminar.
Implementation of Simplified Ecosystem Capital Accounts for Europe Jean-Louis Weber Adviser to the European Environment Agency on Economic-Environmental.
Accounting for ecosystems & biodiversity at the EEA Jean-Louis Weber Environmental accounting / Spatial analysis.
Land accounts at the EEA Jean-Louis Weber & Ferràn Paramo 3 February 2004.
The concept of the integrated spatial platform for land, water and biodiversity Ronan Uhel.
Modelling with CORILIS Change in land cover patterns, landscape ecological potential & “temperatures” on N2000, river basins and UMZ Wire frame and examples.
Land Use and Spatial Planning in Biodiversity 2020 Strategy EIONET Interest Group on Land Use and Spatial Planning Sep Markus Erhard, European.
Markus Erhard European Environment Agency (EEA) 1. Introduction:
1 Ecological landscape connectivity (corridors) Gebhard Banko EEA: Jean-Louis Weber ETC/TE: Ferran Paramo, Oscar Gomez, Stefan Kleeschulte Alterra: Sander.
Achievements in Wildland Fire Risk Mapping
Felix Müller, Ingo Zasada, Regine Berges (ZALF) Klaus Müller, Armin Werner, Verena Toussaint, Annette Piorr Linking European Land Use Change and Landscape.
CLC land cover, land use accounts and agri-environment (policy) analysis Jan-Erik Petersen.
Environmental Intelligence Platform – Monitoring Nutrients Pollution with Earth Observation Data for Sustainable Agriculture and Clean Waters Blue.
Land accounts at the EEA
Jean-Louis Weber & Emil Ivanov
Markus Erhard European Environment Agency (EEA) 1. Introduction:
Paraguay Landscape Analysis
Landscape Indicators using EU wide datasets
By Lewis Dijkstra, PhD Deputy Head of the Economic Analysis Unit,
Selected maps of land cover change in Europe produced from land accounts based on Corine land cover Vol.1: Trends in agriculture and urban.
Pan-European Assessment of Riparian Zones
Emil Ivanov, Centre for Environmental Management,
Paraguay Landscape Analysis
Mandate of the EEA To provide the Community and Member States with:
Land and Ecosystems Accounts (LEAC) &
What if? modelling with CLC/LEAC/CORILIS Attempt at mapping areas prone to agriculture intensification (What if? Agro-fuel scenario) Case of fallow land/set.
Land Use Modelling Group, Sustainability Assessment Unit (DG JRC)
What if? prospects based on Corilis
Outline The 2010 Baseline – Rubicode matrix
Corine Land Cover and Land & Ecosystem Accounting tools
Institute for Protection and Security of the Citizen
Recent spatial analysis work for the 4th Cohesion Report
Presentation transcript:

What if? prospects based on Corilis Alex Oulton, Manuel Winograd Ronan Uhel & Jean-Louis Weber LAND QUICK SCAN INTERFACE: Challenges and needs Internal workshop EEA, Fontana Room, 8 July 2009

What if? prospects based on Corilis Dialogue on impacts/options based on common representations; versatile tool; incremental/ –‘Urgent’ questions, quick overview Highlight (scan, prospect, map, quantify) consequences of various assumptions  ideally defined with users No “real” scenario, 3 to 5 assumptions at a time, maximum Shows what it doesn’t deliver as well as what it delivers  formulation of variants, requirement for adjustments Use of Corilis (smoothed Corine, fuzzy sets) properties: –Potentials in a neighbourhood  no need of complex topological analysis (no need to tell which pasture will be converted, probabilities of conversion instead…) –Additive layers  simple calculations possible (additions, subtractions, ratios…)

From Corine land cover to Corilis Ref.: EEA 2006, Land accounts for Europe

CLC Urban areas and N2000 sites

Processing urban areas in a grid…

Smoothing CLC values, accounting for urban surface inside each cell + within a radius of 5 km (values of urban surface decreasing with the square of the distance to the centre of the grid cell) ‏

Urban “temperature” or “radiation” over N2000 (habitats) sites

Note that not all the “temperature” is coming from large cities (here, agglomerations of pop> hab are in purple) ‏

An index of urban “temperature” of N2000 sites can be computed. Here, MEAN value per site, radius of 5 km

CORILIS map of artificial land cover 2000

What if? prospect: when urban sprawl takes place in the neighbouring countryside… Baseline Data: Corilis / Urban Temperature 2000, scale of // Average increase : 5%, even over Europe Prospect 1: a constant of 5 points is added up to Corilis values > 5 (below 5 corresponds to remote countryside) Urban temperature 2000Urban temperature 2010 – prospect 1

points +5 points +10 points Corilis 2000 What if? Prospect: when urban sprawl takes place in the countryside

What if? Prospect: when urban sprawl takes place in the countryside

Next on urban Validation with Corilis time-series Comparisons between What ifs? constant values increase (as in the example), % increase, others (change smoothing radius of Corilis…) Test attraction effects of transport infrastructures Change in UMZ green quality of life (as sum of Green Landscape Index at 1ha and Green Urban Areas); effect of urban sprawl, agriculture intensification… New What ifs? (exposure to flood risk… ) Compare results to existing land use models, scenarios…

Areas prone to agriculture intensification (driven by agro-fuel demand) b a Assessment based on Corilis, the computation in a regular grid of CLC values in and in the neighbourhood of each cell (in the application: radius of 5km) Broad pattern intensive agriculturePasture and agriculture mosaics

What if? prospect: where conversion to broad pattern intensive agriculture may take place? Analysis of Corilis values of classes 2a and 2b –2a = broad pattern intensive agriculture (clc21, ) –2b = pastures and mosaics (clc231, 242, 243 & 244) Each cell of the grid is given a value of: Ι (2a-2b) Ι *(2a+2b) Positive values (more broad pattern intensive agriculture) are brown, negative values (more pasture and mosaics) are green, yellow meaning transition areas Assumption 1: 2a+2b = UAA is constant (e.g. no deforestation)  Map of change in overall potential: the share of 2a within 2a-2b increases of 5, 10, 20 and 50% Assumption 2: change may take place only when polarity 20%  Map of areas prone to conversion according to the demand for arable land

Highest potential of conversion to cropland [1] Landscape polarity: pixels in dark GREEN and dark BROWN are NOT prone to more change, as well as pixels in light YELLOW (urban, forests, lakes…) XX X

Effect of agriculture intensification over landscape polarity

Highest potential of conversion to cropland [2] RED: within transition areas dominated by arable land 10 40

Highest potential of conversion to cropland [3] BLUE: within transition areas dominated by pasture & mosaics 10 40

Highest potential of conversion to cropland [4] As of

Highest potential of conversion to cropland [4] As of % increase of arable land

Highest potential of conversion to cropland [4] As of % increase of arable land

Highest potential of conversion to cropland [5] As of % increase of arable land

Highest potential of conversion to cropland [6] As of % increase of arable land

Highest potential of conversion to cropland [7] And Natura2000 sites: distribution

Highest potential of conversion to cropland [8] And Natura2000 sites: a first indicator PCZ = “Prone to Conversion Zones”

Risks of soil erosion: The PESERA map by JRC

Highest potential of conversion to cropland [9] And soil erosion risks (PESERA)

Highest potential of conversion to cropland [10] NUTS2/3 prone to conversion

Case of fallow land/set aside at risk of re-intensification, 1st test maps: Areas prone to intensification (in GREY) Fallow land / set aside mapped from land cover flow LEAC lcf41 (in GREEN). Fallow land/set aside at risk of re-intensification are in RED. (RED = GREY+GREEN) At this stage, this is a distribution map, not yet a statistical quantification

Areas prone to intensification (in GREY) AND fallow land set aside mapped from land cover flow LEAC lcf41 (in GREEN).

Fallow land/set aside at risk of re-intensification are in RED. (RED = GREY+GREEN)

Potential impact on Natura2000 sites

The European view

Next on agriculture intensification: Validate assumptions; differentiation according to countries, regions (e.g. important conversion of pasture is taking place in Ireland…) Test new assumptions (taking into account roads, farming practices…), new scenarios Work on change coefficients Cross-check methodology and results with other land use models; integrate? Prepare an interactive tool for users dialogue