Equity, Heterogeneity and International Environmental Agreements Charles D. Kolstad University of California, Santa Barbara and RfF and NBER 1 IEAs • Groups of countries voluntarily band together to abate pollution • No overarching authority to enforce • With global public good, often better to be on the outside looking in (better in fringe) • Some theoretical literature on forming IEAs • Some experimental literature on voluntary coalitions to provide environmental goods 2 Typical Questions • How big will an IEA be (# participants)? • How much better off is everyone as a result of IEA (as opposed to no cooperation)? • How can IEAs be structured to strengthen and increase welfare? • Does uncertainty undermine or strengthen IEAs? • How can lessons be brought to bear on real IEAs, such as Kyoto/FCCC? 3 Motivation for Today’s Talk • We are gathered here to consider ―Distributional Aspects of Energy and Climate Policy‖ • Internationally, does the unequal distribution of benefits and costs of climate policy matter? • [Homogeneity = equity; heterogeneity = unequal.] • Do differences among countries (heterogeneity of countries) promote or retard the formation of IEAs? • Does heterogeneity promote global welfare in presence of IEAs? • Can theoretical results be brought to bear on real problems? 4 Some prior results • i=1,…,N countries • Payoff: Πi = qi – γQ – Where: qi = emissions (0 or 1); Q = total emissions by all countries; γ = marginal damage from emissions relative to abatement costs (costs normalized to 1) (γ < 1) • Two-stage game: countries play a IEA membership game followed by an emissions game • Unique IEA with n*=1/γ members [higher γ smaller IEA] • Aggregate payoff with IEA = - (Nγ - 1)2/γ [higher γ lower payoff] • IEA size and payoff inversely related 5 Uncertainty and Heterogeneity • Hypothesis: if you are a country, not knowing your γ can facilitate cooperation (Young) • Three stage game – Membership game (uncertain about type) – Uncertainty resolved – Emissions game (certainty about type) • Theory: Uncertainty ambiguous – can increase size of an IEA or can be neutral, depending on parameter values 6 Experiments (from Burger & Kolstad, 2009) 8 7 Coalition Size 6 5 Coalition (MPCR = 0.6) Coal. w /uncert. (MPCR = 0.6) 4 Coalition (MPCR = 0.3) Coal. w /uncert (MPCR = 0.3) 3 2 1 0 0 5 10 Period 15 20 7 Experiments (from Burger & Kolstad, 2009) 8 Theory tells us higher MPCR (γ) leads to smaller coalitions 7 Coalition Size 6 5 Coalition (MPCR = 0.6) Coal. w /uncert. (MPCR = 0.6) 4 Coalition (MPCR = 0.3) Coal. w /uncert (MPCR = 0.3) 3 2 1 0 0 5 10 Period 15 20 8 Simple Theoretical Model of Heterogeneity • Two types of countries, 1 and 2 – γ1 < γ2 – Number of countries: N1, N2 with N=N1+N2 • Coalition: (n1,n2) • Coalition emission decision: – Abate: W=-n1[γ1(N-n1-n2)] – n2[γ2(N-n1-n2)] = -(n1γ1 + n2γ2) (N-n1-n2) – Pollute: W= (n1+n2) – n1γ1N– n2γ2N • Abate weakly preferred iff n1γ1 + n2γ2 ≥ 1 • Stable coalitions where n1γ1 + n2γ2 = 1 • Fringe always pollutes 9 Graphically n1γ1 + n2γ2 = 1 (locus of stable coalitions) n2 Optimal for coalition to abate and for individual countries to defect to fringe. Optimal for coalition to pollute n1 10 Equilibrium Refinement • Too many possible coalitions • Focus on the one which gives the greatest overall welfare (in aggregate for all countries)—not a trivial refinement! • W = - (N-n1-n2) (N1γ1 + N2γ2 - 1) • Maximize subject to n1γ1 + n2γ2 = 1 • n1 as large as possible; typically, n2=0 • n1 = 1/γ1 11 Add heterogeneity • Assume γ1 = γ – δ/N1 γ2 = γ + δ/N2 • For δ≥0, N1 γ1 + N2 γ2 = N γ • ie, we can adjust the heterogeneity (δ), keeping the weighted average γ constant • Question: what happens as δ is increased from 0? 12 Comparative Statics • Assume case that coalition is only type 1 countries • Increase in δ increases size of IEA • Welfare W = [N-1/(γ - δ/N1)] (Nγ - 1) • Differentiate W wrt δ and dW/dδ >0 • increased heterogeneity leads to: – Increased IEA size – Increased aggregate welfare for society 13 An ―Application‖ • US Govt Proposed Fuel Economy Reg – Social cost of carbon = $20/ton, global; $1.20 per ton for US • EPA analyses of GHG legislation is US Congress yields $13/ton marginal cost of abatement • γ =0.09 n*=11 14 Reality doesn’t fit the theory but… • Think of two sets of countries – Developed and developing • Developing countries – Lower abatement cost – Lower marginal damage – γ? • Suggestion of theory is that we are better off having two blocs of countries rather than a set of homogeneous countries with same average γ 15 Conclusions • Heterogeneity does seem to matter to formation of IEAs • Heterogeneity appears to favor larger IEAs and higher welfare • Further work needs to be done – Refining theoretical model – Developing empirical implications – Testing theory (experimentally?) 16