Daniela Miteva Brian Murray Subhrendu Pattanayak Duke University.

Slides:



Advertisements
Similar presentations
REGRESSION, IV, MATCHING Treatment effect Boualem RABTA Center for World Food Studies (SOW-VU) Vrije Universiteit - Amsterdam.
Advertisements

Active Reading Workbook, pages 71-72
Controlling for Time Dependent Confounding Using Marginal Structural Models in the Case of a Continuous Treatment O Wang 1, T McMullan 2 1 Amgen, Thousand.
Measuring the Impact of the RDP Issues being addressed at an EU level with regards to measuring the impact of the Rural Development programmes B. Schuh.
Evaluation of the impact of the Natural Forest Protection Programme on rural household incomes Katrina Mullan Department of Land Economy University of.
Managed Timber Production Model Shan Ma. Forest Services The services provided by a forest include: –C–Carbon sequestration –W–Water quality regulation.
INTRODUCTION Organogram of DoF My role In the Department of Forestry
Agricultural Land Use and Ecosystem Services in the Canadian Prairies Benjamin S. Rashford Agricultural and Applied Economics University of Wyoming.
Rural Settlement Patterns
The World Bank Human Development Network Spanish Impact Evaluation Fund.
Linking the Science and Economics of Blue Carbon Brian C. Murray Director for Economic Analysis Nicholas Institute, Duke University Oceans Day UNFCCC COP.
The Urban Environment 9. © 2012 John Wiley & Sons, Inc. All rights reserved. Overview of Chapter 9  Population and Urbanization  Characteristics of.
Simulating Future Suburban Development in Connecticut Jason Parent, Daniel Civco, and James Hurd Center for Land Use Education and.
Muddy Brook vs. Alder Brook Stream Geomorphic Assessment: Joe Kelly, Alison Selle, Sarah Stein, Kristin Williams.
Agriregionieuropa Evaluating the CAP Reform as a multiple treatment effect Evidence from Italian farms Roberto Esposti Department of Economics, Università.
The Impacts of Integrated Pest Management (IPM) Farmer Field Schools on Inputs and Output: Evidence from Onion Farmers in the Philippines Santi Sanglestsawai,
Results: Test-run in the Willamette Basin Some areas provide higher levels of services than others. The agriculture and timber maps show dollar values—high.
Eftec Economics for the Environment Consultancy Using ecosystem services for cost benefit analysis of forestry decisions Roundtable on Cost / Benefit of.
The stock is the present accumulated quantity of natural capital. It is a supply accumulated for future use; a store. The natural income is any sustainable.
Modeling the effects of climate change on multiple ecosystem services Marc Conte Stanford University Natural Capital Project Marc Conte, Josh Lawler, Erik.
Sustaining Terrestrial Biodiversity: The Ecosystem Approach Brian Kaestner Saint Mary’s Hall Brian Kaestner Saint Mary’s Hall Thanks to Miller and Clements.
Sediment Retention model
BIODIVERSITY CONSERVATION, AND ADAPTATION ASPECTS IN NATIONAL STRATEGIES ON POVERTY REDUCTION (NS- PR), SOCIO-ECONOMIC DEVELOPMENT PLAN (SEDP)
AGEC/FNR 406 LECTURE 31 Former tropical forest…. TROPICAL FORESTS Located between tropics of Capricorn and Cancer At least 10 percent woody cover Important.
Soil carbon in dynamic land use optimization models Uwe A. Schneider Research Unit Sustainability and Global Change Hamburg University.
ESValue-SWF Valuing Ecosystem Services on Public Lands in Southwest Florida.
InVEST Tier 1 Carbon Model. In the Tier 1 model we estimate carbon stock as a function of land use / land cover. Storage indicates the mass of carbon.
BRINGING ECOSYSTEM SERVICES INTO DECISION-MAKING: A TOOLKIT FOR RAPID ASSESSMENT OF SITES Rob Munroe.
Ecological rationale for determining buffer width Forest Ecosystem Management and Assessment Team (FEMAT) Report.
Land Use & Population Growth in Belize, Central America Modeling Future Impacts on Ecosystems ~Eve Robinson, Dept. of Marine Science.
Guided Notes on the Human Impact on Land Resources
Overview of Economic Methods to Simulate Land Competition Forestry and Agriculture Greenhouse Gas Modeling Forum National Conservation Training Center.
Daniela Miteva & Subhrendu Pattanayak Duke University.
Key Concepts Ch. 23  Human land use  Types and uses of US public lands  Forests and forest management  Implications of deforestation  Management of.
Urban Growth and Land-Use Change: An overview for air quality models Manuel Suárez Instituto de Geografía-UNAM.
Biodiversity Loss. Ecosystems provide humans with many services. Ecosystems supply food, fuel, water, they regulate climate and provide humans with cultural.
Fig. 10-4, p. 193 Support energy flow and chemical cycling Reduce soil erosion Absorb and release water Purify water and air Influence local and regional.
Chapter 8: Land Section 8-2: How We Use Land. As the human population grows, ever-increasing amounts of land and resources are needed to support it.
Evidence. Carbon Dioxide at Mauna Loa, Hawaii Global surface temperature.
RICARDIAN METHOD Purpose: value damages of climate change to agriculture Approach: cross sectional analysis of farm net revenue per hectare across climate.
Land Use Our urban world Forestry management Parks, Reserves, and Wildlands Agricultural land use.
WWF Greater Mekong Programme InVEST Seminar – April 2012 Ecosystem Services in the Greater Mekong Subregion.
The Effects of Agro-clusters on Rural Poverty: A Spatial Perspective for West Java of Indonesia Dadan Wardhana, Rico Ihle, Wim Heijman (Agricultural Economics.
What is deforestation? Deforestation is the removal of trees in forests around the world Many reasons for deforestation More room for agriculture Logging.
Deforestation In Papua New Guinea (PNG)
Randomized Assignment Difference-in-Differences
Biomes Under Pressure Forests and woodlands Tropical forests Oceans
What can a CIE tell us about the origins of negative treatment effects of a training programme Miroslav Štefánik miroslav.stefanik(at)savba.sk INCLUSIVE.
The General Linear Model. Estimation -- The General Linear Model Formula for a straight line y = b 0 + b 1 x x y.
Does Designated Preservation Areas Crowd out the Preservation Effort of Existing Programs? Xiangping Liu NC State University.
Impact of Human Activity on Ecosystems
Commercial Agriculture Development Project Impact Evaluation
The Impacts of Human Industry on Ecosystems
Constructing Propensity score weighted and matched Samples Stacey L
General belief that roads are good for development & living standards
Biophysical Modelling (Levels 1 and 2)
Do now: Describe the following cycles of the tropical rainforest:
Bradford Mills, Virginia Tech
Rodel D. Lasco Professor University of the Philippines
Sustaining Terrestrial Biodiversity: The Ecosystem Approach
Geosphere Basics Chapters: 1.2, 14, 15.2.
Impact evaluation: The quantitative methods with applications
Methods of Economic Investigation Lecture 12
Challenge – Condition accounts
Matching Methods & Propensity Scores
V. Deforestation.
Evaluating Impacts: An Overview of Quantitative Methods
Land Vocabulary.
Land Resources Why is land considered a resource?
Presentation transcript:

Daniela Miteva Brian Murray Subhrendu Pattanayak Duke University

Non-random location of protected areas Tend to be established on rock and ice Spillover effects Extraction activities may be displaced to the buffer zones or other unprotected nearby areas Different levels of protection IUCN categories I-VI Enforcement

Methodology Need to compare protected units with observationally similar unprotected units This yields only an average estimate of the impact Test for heterogeneity of the impact Outcomes Ecosystem structure vs. function

*Indigenous reserves and wetlands excluded

**The study selected 5 % of each countrys PA (treatment) and an area 4 times as large to serve as control

Do the protected areas in Indonesia protect habitats and ecosystem services? Does the impact of protected areas vary with the characteristics of the area? Where do the tradeoffs and complementarities occur in space? This is still very much work in progress…

Biophysical characteristics Location (distance to ports by type; proximity to district capitals, mills and markets; slope, elevation, river length, urban vs. rural) Climate (average temperature & precipitation, aridity index, organic content and pH levels of the soils) Socio-economic (road length, number, area and type of timber concessions, population density, village accessibility) Protected Areas (IUCN categories I-IV)

Provision of multiple ecosystem services Blue carbon sequestration Habitat for species Storm protection Very rapid loss of mangroves in Indonesia Cut for timber Cleared for aquaculture & agriculture Image source: /

Propensity score matching (PSM) to identify observationally similar protected and unprotected villages Does not rely on a specific functional form Reduces the dimensionality of the matching Partial Linear Models (PLM) Sensitivity analysis & robustness checks

Semi-parametric regression of the form Estimated in 2 stages Least squares on m -th order difference to estimate Non-parametric (loess) estimation for Properties Allows some variables to enter non-parametrically Reduces the dimensionality of the problem Consistent estimation for, but the efficiency depends on the order of differencing (m)

Protected areas do not seem to protect forests: ATT=20.91, t=0.47 Hard to match the very high propensity scores The impact varies CovariateCoefficient Organic content in the topsoil *** (5.811) Forest area at baseline 0.076*** (0.007) Distance to the nearest mill (m) ** (0.001) Length of the river network (m) 0.015*** (0.004) *** 1%, ** 5%, *10% R2=0.19, n=2214

Deforestation P<0.01

Protected areas do not seem to protect mangrove patches, either (ATT=-0.14, t=-0.17) Hard to match the very high propensity scores The impact varies CovariateCoefficient Aridity index ** (0.0002) Mangrove baseline *** (0.0137) Average slope (degrees) ** (0.2705) Distance to market w/ permanent structures * (0.0236) *** 1%, ** 5%, *10% R2=0.4, n=139

Mangrove loss P=0.001

Very preliminary results Have not looked at the year the PA was established Have not considered spatial spillovers Numerous ecosystem services still to be analyzed Dealing with decentralization in Indonesia Constant changes of the administrative units at all levels Institutional drivers of change Using geospatial data Raster resolution introduces errors in the dependent & independent variables

Andam, K. S., P. J. Ferraro, et al. (2008). "Measuring the Effectiveness of Protected Area Networks in Reducing Deforestation." Proceedings of the National Academy of Sciences 105(42): Andam, K. S., P. J. Ferraro, et al. (2010). "Protected Areas Reduced Poverty in Costa Rica and Thailand." Proceedings of the National Academy of Sciences 107(22): Chape, S., J. Harrison, et al. (2005). "Measuring the Extent and Effectiveness of Protected Areas as an Indicator for Meeting Global Biodiversity Targets." Philosophical Transactions of the Royal Society B: Biological Sciences 360(1454): Das, S. and J. R. Vincent (2009). "Mangroves protected villages and reduced death toll during Indian super cyclone." Proceedings of the National Academy of Sciences 106(18): Ferraro, P. and M. Hanauer (2011). "Protecting Ecosystems and Alleviating Poverty with Parks and Reserves: WinWin or Tradeoffs?" Environmental and Resource Economics 48(2): Ferarro, P., M. Hanauer and K. Sims (Forthcoming). Conditions associated with protected area success in conservation and poverty alleviation, Proceedings of the National Academy of Sciences Ferraro, P. J. and S. K. Pattanayak (2006). "Money for Nothing? A Call for Empirical Evaluation of Biodiversity Conservation Investments." PLoS Biol 4(4): e105. Joppa, L. and A. Pfaff (2010). "Reassessing the Forest Impacts of Protection." Annals of the New York Academy of Sciences 1185(1): Nagendra, H. (2008). "Do Parks Work? Impact of Protected Areas on Land Cover Clearing." AMBIO: A Journal of the Human Environment 37(5): NaughtonTreves, L., M. B. Holland, et al. (2005). "The Role of Protected Areas in Conserving Biodiversity and Sustaining Local Livelihoods." Annual Review of Environment and Resources 30(1): 21925

Decade IUCN Category Total IaIbIIIIIIV Prior to s s s s s s s s After Total *Only the ones that have been formally designated as such; categories V and VI have also been excluded from the analysis