The Value of the Brazilian Amazon Rainforest. Jon Strand Lecture October 25, 2017

Similar documents
A perspective on capacity and capability in the context of ecosystem accounting 1

10 Facts about Forest Protection

Valuation country experiences. (Level 2)

Valuing Ecosystem Services to Promote Low Emission Development Strategies in the Lower Mekong Region: A Case Study of Khao Yai National Park, Thailand

Valuation Methods. Introduction. Robert MAVSAR EFIMED

Forest Watershed Services on an Old Frontier in the Brazilian Amazon

Amazon. What are the benefits of the Amazon to the Brazilian Economy?

Degradation of of Forest Ecosystems

Rock/ soil type and altitude differences.

Understanding tropical deforestation

Environmental Economics Lecture on topics in valuation of environmental goods. Jon Strand February 15, 2017

Climate Change, Biodiversity and Economic Development. Kei Kabaya Economy and Environment Group Institute for Global Environmental Strategies (IGES)

Agriculture and Climate Change Rural Urban Linkages. Erick Fernandes, Adviser, Agriculture & Rural Development

Forests Goods and Services. Lecture 18

Ecosystem accounting concepts

Valuing Ecosystem Services: InVEST Tools. Adrian L. Vogl, Ph.D. The Natural Capital Project, Stanford University

Why does the Amazon rainforest matter?

PROJECT AND THE ENVIRONMENT

An Introduction to Ecosystem Accounting. 7 September, Prof. Dr Lars Hein, Wageningen University

REDD+ in Cambodia: A Case Study of Deforestation and Opportunity Costs in Koh Kong Province

Biodiversity: Who cares?

Scientific Facts on. Forests

A FOREST POLICY FOR NEW ZEALAND

Conserving Agricultural Biodiversity in China: Lessons from the Millennium Ecosystem Assessment

Chapter 18 Land Resources

Ecosystem services valuation A 15-minute introduction. Thomas Enters, UNEP


Ecosystem Accounting: a Reprise

Section 6.2 Notes. Renewable and Non-Renewable Resources

Services Generation Account (Levels 0, 1 and 2)

USDA FOREST SERVICE International Programs. Land Use Conversion

Measuring and Valuing Natural Assets: Ecosystem Services. Steve Polasky University of Minnesota & Natural Capital Project

Forests. NEW INTERNATIONALIST EASIER ENGLISH Intermediate READY LESSON

Devastating Deforestation

Deforestation and intensive agriculture in Brazil

UNIVERSIDADE FEDERAL DE MINAS GERAIS

Developing the ecosystem accounts / biophysical modelling of ecosystem services. Lars Hein

Impacts of Possible Chinese Protection of 25 Percent on US Soybeans and Other Agricultural Commodities

Rainforests and Tropical Diversity. Gaby Orihuela Visitor Experience Manager

RAINFOREST REVIVAL CRISTINA ALBERS LAUREN DINKA KALYN FRAWLEY. Rainforest Revival Organization. WEBSITE: rainforestrevival.org

Services Supply Account (Levels 1 and 2)

Mapping the Value of Ecosystem Services in Latin America and the Caribbean

Session 1: Ecosystem accounting overview

Overview of the SEEA Experimental Ecosystem Accounting with examples from the Netherlands. Sjoerd Schenau Statistics Netherlands

Overview of the GEF6 Integrated Approach Pilot Programs. Early Lessons from Programming

Overview of the GEF6 Integrated Approach Pilot Programs. Early Lessons from Programming

Table of Contents. Synthesis. DRAFT Landing Page for Feeder Study on Livestock systems

Ecosystems Valuation The Bahamas Experience

The role of remote sensing technologies. climate change adaptation related to forests resources in the Congo Basin

Climate change adaptation and land degradation measures in drylands with focus on Africa

Avoided Deforestation

Biodiversity conservation and forestry is compromise possible?

FOR 414/595: World Forestry

BUILDING A BETTER FUTURE WHERE PEOPLE CAN LIVE AND PROSPER WITH NATURE. All rights reserved 2015 Green World Investments

Understanding tropical deforestation

Exploring challenges to sustainability in the provision of ecosystems services by upland forests in Scotland and Ukraine

Valuing the ecosystem of the Indonesian rainforest

Rainforest management. Jon Strand

Development Research Group. Knowledge in Development Note 9. Tropical Deforestation, Biodiversity, and Development 1 June 2007

Linking water and climate change: a case for Brazil

International Union for Conservation of Nature. Conserving biodiversity Pioneering nature s solutions to global challenges

Rapid estimation and location of past deforestation Use of Global Forest Watch data

Impact of climate change on biodiversity: a challenge to agro-ecosystems in South Asia

FAO and UNEP Meeting on Forests and Climate Change Adaptation in Asia, 26 October, , Bangkok. Regan Suzuki, RECOFTC/ REDD net

The World s Forests. Change in Forest Area. Environmental Issues & Problems ENV 150. State of the Forest. Guillaume Mauger. Current Topic: Depletion

How Humans Influence Ecosystems. Chapter 3.2

Image object Accounting (Available in the free JRC software GuidosToolbox)

Key aspects of sustainable forest management. Herbert Christ, International Forest Policy Programm, GTZ

RESEARCH LETTER. On Forest and Water Interactions

Newest information and knowledge about the world s forests and forestry

Draft Concept Note SEEA-EEA Expert Meeting November 18-20, 2013 New York, NY

Hotel, Kampala, 6 th October Yakobo Moyini, and Moses Masiga Environmental and Natural Resources Economists and Policy Analysts

SAFE GUARDING THE RESOURCE BASE: STATE OF PAPUA NEW GUINEA S FOREST AND LAND

QUANTIFYING THE BENEFITS OF WATERSHED INVESTMENT

Valuing Ecosystem Services and Biodiversity: Experience and Approaches Taken in Georgia

A user-driven approach to Cost-Benefit Analysis in a participatory context

Reproductive Forest Resources as Incentive of Local Community and Role of Forest Ecosystem Services

Eastern part of North America

ADM Commitment to No Deforestation, No Peat and No Exploitation

Environmental Services and Sustainable Use of Forests Programme Strategy Revised Version October 2005

The Montreal Process Criteria and Indicators

The Economics of Ecosystems and Biodiversity TEEB. The Royal Society Foundation Meeting on Valuation of Biodiversity 5 th May, London

PALM PLANET Can we have tropical forests and our palm oil too?

An introduction to incentives for forest-water ecosystem services. Thomas Enters, UNEP

FSC S CONTRIBUTION TO FOREST RESTORATION. Forest Restoration FSC is on board!


28 Protection of the Natural Resources in Marginal Areas and Sustainable Rural Development in Northern Lebanon

ENVIRONMENTAL-ECONOMIC ACCOUNTING 101

Recent development in Swedish Forest Accounts Background

Clean or Dirty Energy? Challenges and Risks Associated to Belo Monte Hydroelectric Dam Complex on Xingu River Basin in the Amazon, Brazil

Center for International Forestry Research

Water and Climate Change. David Coates Secretariat of the Convention on Biological Diversity Montreal Canada

Finance for Forests. Progress on the New York Declaration on Forests. Executive Summary - Goals 8 and 9 Assessment Report

Tropical Forests, Tipping Points, and the Social Cost of Deforestation

COMMODITIES & FORESTS AGENDA 10 PRIORITIES TO REMOVE TROPICAL DEFORESTATION FROM COMMODITY SUPPLY CHAINS

Valuing Ecosystem Services: The U.S. Geological Survey Experience

Click to edit Master title style

Environmental Valuation of Biodiversity in Japan. Koichi Kuriyama (Kyoto University)

Chapter 30. Conserving Earth s Biodiversity

Large-scale opposition among Borneo villagers to deforestation

Transcription:

The Value of the Brazilian Amazon Rainforest Jon Strand Lecture October 25, 2017

Possible forest losses in the Amazon to 2050 2

Analyzing the consequences 2/3 of vegetation cover of 15 ecoregions among 32 would be eliminated 3

What is the value of the Amazon rainforest? We separate between three classes of value: 1) Local and regional values to the population in South America 2) Carbon values: The global benefit from carbon sequestration by keeping the forest 3) Other global values : Willingness to pay in other countries to preserve the Amazon rainforest The project that is mainly discussed here considers elements 1 and 2 only. Parts of element 3 have been subject to separate research in the World Bank. 4

Why is spatial economic valuation of the Amazon particularly useful? Tells us where to most discourage conversion of rainforest to agriculture, by comparing preservation values to local opportunity values. Where to put most effort to prevent illegal logging. Where to prevent forest fires, and how hard to work at this. Where to establish new national parks and indigenous zones. All these issues are crucially important for governments in the Amazon region. Value mapping is helpful for these governments in this work. But far from all resources in the Amazon can easily be valued at a fine spatial scale. One example is biodiversity, another is recreation and tourism. 5

Environmental valuation: Types of value Use value: This is our direct value from the forest (or another environmental good), in terms of products, or services (such as tourism and recreation, health benefits). Option value: The value we put to have the option to use the resource, even if we are currently not using it. Existence or preservation («passive-use») value: This is the value we put to the resource, just because we want it to exist and be preserved, for us now and in the future, and for future generations. 6

3 main groups of goods and services that give rainforests value: 1. Provisioning services: timber, non-timber products, game, fish, bioprospecting. 2. Supporting and regulating services: Carbon sequestration, biodiversity and biological resources, hydrological impacts, watershed protection, erosion prevention, forest fire regulation. 3. Cultural and other human services: Tourism and recreation, human health impacts. 4. My Amazon project values only some of these services, those easiest to map and value in economic terms (timber; NTFPs; carbon; certain hydrological impacts). 7

How do we value environmental goods (including rainforests)? Three types/groups of methods: 1. Using market prices of the outputs produced by the «environmental goods». This is largely what is used in the project presented here. 2. Revealed preference (RP) methods. We look at behavior of individuals in their use of environmental goods, or in revealing their preference for these goods through markets. 3. Stated-preference (SP) methods. This means to ask individuals questions related to how they value environmental goods. This is the most versatile method, which can cover all concepts of environmental value. The method however has problems and must be used with care. Very often for environmental goods, the value is not directly revealed in markets. Then we must use methods of types 2 and 3. Existence or preservation («passive-use») value must always be found using SP. We have two main SP techniques: Contingent valuation: one asks question(s) about the value of the environmental good. Choice experiments: one constructs choice situations that permit one to derive trade-offs between environment and money. 8

The platform for mapping of geographically differentiated ecosystem values of the Brazilian Amazon The valuation platform set up by the Belo Horizonte team, led by Britaldo Soares-Filho The platform is constructed with two layers for each included elements, with pixel resolution 1 km2: 1) Biophysical mapping of resource base or impact 2) Economic valuation of biophysical impacts. 9

The valuation platform (cont.) The platform available interactively at: http://csr.ufmg.br/amazones/ Provides detalied biophysical and economic value maps of local and regional values + carbon values In the platform, thesse values are mapped for the entire Brazilian Amazon, at resolution 1 km2 pixels 10

The project s approach to economic valuation Convert all forest values, for which we have secure and spatially differentiated money values, to a common metric, money. Not all potential values have been possible to monetize (yet). This economic value metric is very conservative. Such a barebones set of values can still be useful in deriving minimal values of the forest: It is often sufficient to make decisions on saving given local forest areas. 11

The valuation platform has 5 main elements: 1. Hydrological impacts of forest losses on main economic activities (agriculture and hydropower) 2. Economic value of sustainable timber and non-timber forest products 3. Biodiversity mapping 4. Carbon emissions when rainforest is lost 5. Forest fire activity, spread and damage in the Amazon are also mapped. 12

Mapping hydrological impacts of forest losses A team at the Federal University of Viçosa, Brazil, led by Marcos Costa, is responsible for the work with this element. See this website: http://www.biosfera.dea.ufv.br/en-us/deforestation-and-rainfall Value mapping here consists in three steps: Impacts of Amazon rainforest losses on rainfall patterns in all of South America, using a global circulation model (CCM3-IBIS) Impacts of rainfall changes on agricultural outputs, and net economic returns from soy, beef and hydropower, in Brazil and Argentina Reverse calculations to ascribe losses for soy, beef and hydropower back to each forest pixel in the Amazon, in US$/ha/year. 13

Digression on soybeans, livestock and hydropower production in South America, and Amazon deforestatoin Soybean production had increased dramatically in South America over the last 20 years, and the region now produces about 175 million tons/year, more than half of the global output. For both Brazil and Argentina, soybeans are the largest export article. This has made the region dependent on soybean productivity, which is heavily affected by regional rainfall. Brazil has the largest number of livestock in the world apart from India (about 220 million), and is the world s largest exporter of beef. Brazil is the world s second largest producer of hydroelectric power (after China). South America/Brazil has three of the five largest installations in the world (Itaipu and Tucurui, and recently Belo Monte). All these activities are highly dependent on regional rainfall, which is heavily affected by Amazon deforestation. 14

Element 2: Mapping economic values of sustainable timber and non-timber forest product (NTFP) extraction Net economic returns from reduced impact logging (RIL) modeled and mapped. RIL not allowed in protected/indigenous areas RIL returns very sensitive to extraction costs (RIL generally not economically viable in remote areas) NTFP more widely viable as extraction costs are relatively lower Economic valuation of sustainable NTFP extraction mapped for two products widely prevalent in the Brazilian Amazon: a) Brazil nut b) Rubber 15

Element 3: Biodiversity mapping We map several aspects/features of biodiversity including endemicity, phylogenetic composition, species composition, species richness, and biodiversity conservation priority areas. No values have been ascribed to spatially explicit, local and regional, economic values of biodiversity in the project. (A pilot stated-preference survey indicates relatively limited valuation of biodiversity in Brazil.) No project internationally has succeeded, nor seriously attempted, at such valuation. We have been working on this from various angles, including using stated preferences. 16

Element 4: Carbon emissions from deforestation Avoiding carbon emissions is a very important part of the value of protecting the Amazon. The spatial carbon emissions map is built into the valuation platform. Average carbon emissions when Amazon rainforest is lost estimated at about 130 ton C/ha (460 ton CO2/ha): but varies a lot across the Amazon. 17

Element 5: Forest fires and forest value This is not a value element. But forest fires have (potentially large) impacts on forest value. Aims of this work: a) To model forest fire occurrence and spread using the FISC model b) To calculate economic costs due to forest fires using the EcoFire model We also aim, in extensions of this project, to create a spatial map of externality impacts of local forest losses, multiplying these losses due to localized forest fragmentation and dryness. 18

Average and marginal forest values Average and marginal values of the rainforest very often differ Marginal rainforest value: What is lost by losing a very small part of the forest, while the rest is intact? Marginal values are often lower than average values: For biodiversity valuation: Losing a small part of the forest does not necessarily lead to biodiversity loss For tourism: Losing a small part of the forest does not necessarily reduce the overall value of the rainforest for tourists, as they may seek other areas. But marginal values can also be higher than average values, as illustrated in the model discussed in the following. 19

Marginal rainforest values can be given an analytical basis using asset equations Forest asset return (undamaged forest): rv (1 L)[ v( D) w( D)] ( L, D)( VF V) ( g ) V Asset return to forest damaged by fire: rv (1 L F)[ v( D) w( D)] ( g ) V F F

Analytical formulation of asset equations (cont.) Forest value (total for a given small unit patch of forest) 1 V 1 L F [ v( D) w( D)] r g r g Marginal forest value (value loss when a small forest amount is lost): dv 1 r g r g V 1 ' ( ) [ '( ) '( )] ' 2 LF 2 DD F v w v D w D D dl r g ( r g ) ( r g ) v w

Average and marginal forest values (cont.) Marginal forest values are in some cases higher than average values This can be due to two externality factors, illustrated by the model on the preceding slides: Losing additional rainforest could increase local fire risk Losing more rainforest makes the remaining forest drier, increasing fire risks, and reducing the value of standing forest. These factors, associated with forest fires, increase marginal forest values (of saving a small piece of forest). This is in spite of forest fires reducing average forest values. The valuation project aims to parameterize these externalities via modeling of forest fire risk. This is not yet done in the platform. 22

Stated-preference work in Brazil to date: 3 pilot surveys in large cities (together 200 interviews), focusing on forest loss, biodiversity loss, and local climate effects (the three issues found important in initial focus group work). Results are stated in WTP/hh/month. (All interviews in social groups A-C) R$ 25 R$ 20 R$ 17,3 R$ 20,4 R$ 15 R$ 10 R$ 7,4 R$ 10,0 R$ 5 R$ 3,0 R$ 0 WTP to avoid 20% forest loss WTP to avoid 10% of species at risk of extinction (not statistically significant) WTP to avoid 20% risk of regional flooding and droughts Combined WTP*: Avoid forest loss and regional flooding and droughts, zero WTP for species extinction Combined WTP**: Avoid forest loss and regional flooding and droughts, estimated mean WTP for species extinction 23

The central valuation platform s aggregate value feature: «Query» facility sums up the economic values of the following impacts: RIL, rubber, Brazil nut, carbon, and net hydrological impacts on soy, beef and hydropower production. Calculates the protection value per hectare per year, across the entire Brazilian Amazon, related to these elements. The user can insert desirable parameter values for the prices of carbon, soy, beef, and electricity. As remarked above, biodiversity values are not (yet) included in the spatially explicit protection value in the platform. Several other value elements are also not (yet) embedded (see below). This makes the platform values overall very conservative. 24

Value elements not (yet) part of the valuation platform: 1.Tourism and recreation 2.Bioprospecting (could be an integrated part of biodiversity values) 3.Health impacts of deforestation (contagious diseases; air pollution) 4.Watershed protection, including avoidance of droughts and flooding impacts 5.Other local products including fishing, hunting and gathering. 25

Mapping opportunity costs 1.Opportunity costs are economic values associated with converting Amazon rainforest land to other uses, such as agriculture. 2.Only when opportunity costs are higher than the true and total value of the protected rainforest (including all value components) should deforestation be allowed. Work to assess opportunity costs for the Amazon will be addressed in follow-up work. 26

This work as basis for cost-benefit analysis on Amazon rainforest protection The total value of protecting the Amazon rainforest has three major components: 1. Local and regional values 2. Carbon values (a global value) 3. Other value related to protecting the Amazon in the rest of the world: People in other countries are also willing to pay to preserve the Amazon forest. The total magnitude of such values is currently unclear. Some such results have however been found in a stated-preference survey in the U.S. and Canada, by the World Bank. 27

Concern among households in U.S. and Canada, related to protecting the Amazon. (Percent of respondents who mention the individual issues.) 45% 34% 22% 26% 29% 14% 17% 15% 13% 8% 8% 8% 5% 7% 5% 4% 4% 8% 4% 3% 8% 2% 2% 6% Biodiversity Ecosystem Oxygen Trees Climate Beauty Medicine Water Athmosphere Indigenous people Other Don't Know/None USA Canada 28

Estimation results, using validated respondents estimation sample (n=849). WTP estimates for a program to reduce by 2050 the area of forest losses by 12 %-points and the number of species at high risk of extinction by 10 %-points is listed on the bottom row. Estimates are in terms of US$ per % point for avoided forest loss and reduced species threats. Model 1: Mixed Logit Model with Correlated Random Parameters Model 1 + Controls for Program Misconceptions Variable Est. t-value p-value Est. t-value p-value Avoided forest loss, WTP in $ per 1 % point Reduced species threats, WTP in $ per 1 % point Mean 5.48 9.75 0.00 Std. dev. 5.57-9.70 0.00 2.49 1.08 0.28 2.53 0.91 0.36 Mean 6.42 6.83 0.00 Std. dev. 7.51 3.42 0.00 6.42-6.87 0.00 7.97 3.28 0.00 L F,S -0.54-2.30 0.02 0.53-1.91 0.06 Program cost Mean -0.53-3.05 0.00-0.51-2.84 0.00 Std. dev. 0.40 5.97 0.00 0.42 5.88 0.00 Status Quo, WTP in $ -109.93-6.43 0.00-100.31 4.10 0.00 SQ+1 0.73 3.88 0.00 0.73 3.92 0.00 Age 30-44 -0.02-0.29 0.77-0.02-0.21 0.84 Age 45-59 -0.22-2.48 0.01-0.21-2.37 0.02 Age 60 or more -0.66-4.70 0.00-0.63-4.55 0.00 High school or less 0.09 1.31 0.19 0.07 1.00 0.32 White, non-hispanic 0.12 1.39 0.17 0.11 1.30 0.19 Black -0.30-2.03 0.04-0.25-1.76 0.08 Hispanic -0.66-3.00 0.00-0.62-2.91 0.00 Female 0.19 3.14 0.00 0.20 3.40 0.00 Self-employed 0.09 0.80 0.42 0.10 0.94 0.35 Retired 0.15 1.10 0.27 0.11 0.82 0.41 29

Calculation of total WTP in U.S. and Canada, for saving 12% of the Amazon forest, and 10% of the species: $5.50/hh/year per % point forest saved = $66/hh/year for 12% points $6.40/hh/year per % point species saved = $64/hh/year for 10% points With 140 million households in the two countries: $9.24 billion/year for saving Amazon rainforests as such $8.96 billion/year for protecting the species in the Amazon Total WTP/year in U.S.+ Canada for protecting the forest and species = $18.2 billion Per-hectare value (given 12 % of 500 million has = 60 million has) = $303/ha/year With 5% discounting (high) this is eqivalent to more than $5,000/ha up to 2050. 30

Value components in Amazon rainforest valuation (cont.) Values 1-2 are the objectives the spatial World Bank project. For carbon values, 100-160 tons of carbon (360-550 tons of CO2) are assumed to be released on average per ha of rainforest deforested. With a (global) social cost of carbon = $30 per ton CO2, this is equivalent to a deforestation cost of about $10,000-16,000 per hectare, as the carbon value of preventing deforestation. For category 3 values, we find from the U.S./Canada survey a protection value of at least about $5,000 per hectare of saved rainforest in the Amazon. (This is, presumably, non-carbon.) 31

Value components in Amazon rainforest valuation (cont.) Consider adding all value components 1-3 up to an integrated, spatially explicit and differentiated, value of the Brazilian Amazon rainforest. These benefits can be compared to program costs, for an overall evaluation in economic terms, of programs for Amazon protection. (Note again that outside of South America only carbon values, plus other values for U.S./Canada, are included. Several local/regional elements are also not included.) 32