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On the Trade-Offs of Regulating Multiple Unpriced Externalities with a Single Instrument: Evidence from the Renewable Fuel Standard. Antonio M. Bento and Joel R. Landry Environmental Economics and Energy Policy Program Dyson School of Applied Economics and Management Cornell University.
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On the Trade-Offs of Regulating Multiple Unpriced Externalities with a Single Instrument:Evidence from the Renewable Fuel Standard Antonio M. Bento and Joel R. Landry Environmental Economics and Energy Policy Program Dyson School of Applied Economics and Management Cornell University
Motivation • Tinbergen (1952): In order to restore economic efficiency when multiple market failures are present we require a separate policy instrument to address each market failure. • Despite this, policymakers frequently use a single policy instrument to address multiple unpriced externalities. • The Energy Independence and Security Act of 2007 (EISA) was passed to address two objectives: • Reduce energy dependence • Reduce GHG emissions • Our knowledge of the potential trade-offs between these two objectives is limited.
Overview of the Renewable Fuel Standard (Energy Independence and Security Act, 2007) 36 billion gallons of total bio-fuels, 21 billion gallons advanced, by 2022 Billions of gallons
Key Questions • What are the economy-wide costs and benefits of the Renewable Fuel Standard (RFS) for conventional biofuels? • What are the trade-offs between the environmental and oil dependency related external benefits of the RFS? • What would policymakers implied value of oil dependency have to be in order for the RFS to pass a benefit-cost test?
Overview of the Model • The domestic agents in the model are: • Households • Producers of Agricultural Crops • Producers of Ethanol • Refiners of Regular Gasoline • Suppliers of Blended Fuel • Producers of Food • Government • Trade with the Rest Of the World: • Crude Oil Imports • Crop Exports
Welfare Formula • Change in welfare due to RFS is given by: • Consists of six components: • Primary Costs, dWPC • Subsidy Interaction Effect, dWE • Blended Fuel Output Effect, dWF • Oil Premium Effect, dWP • CRP Interaction Effect, dWN • Change in Trade Balance, dWB
Model Dynamics • Yields, domestic income and ROW demand for crops are allowed to adjust following the USDA’s Long-Term Projections for 2009. • Crude oil and energy prices follow the central price path of the EIA’s Annual Energy Outlook 2010. • Corn and energy requirements for ethanol follow RFS2 assumptions. • Fuel economy adjusts per National Research Council’s 2002 report. • CRP rental rates increase by 2% a year.
Monte Carlo • Use Monte Carlo methods to quantify uncertainty with respect to our welfare analysis. • For each category of external benefits (GHG emissions, oil dependency related, CRP benefits, local air pollution, accidents, and congestion), we fit separate independent gamma distributions to match: • The a mean of our central parameter estimate, • The 10th percentile to equal our lower bound parameter estimate, and • The 90th percentile to equal our upper bound parameter estimate.
How Do Environmental Benefits Trade-off with Oil Dependency Benefits?
Implications if Policymakers Intended to Replace VEETC with RFS
Implications if Policymakers Intended to Replace VEETC with RFS
Conclusions • Excluding the change in the trade balance, the RFS for conventional biofuels fails a benefit-cost test with costs exceeding benefits by 3:1. • Result is robust, with passage of benefit-cost test occurring only 0.01% of the time. • Net costs per EGG of ethanol added by RFS is $0.64-$0.79. • With respect to the change in trade balance, if only a quarter of the welfare gain from the change in terms of trade is realized then the RFS will pass a benefit-cost test.
Conclusions • Policymakers trade-off oil dependency benefits from the RFS with additional environmental costs almost dollar for dollar. • In order for RFS to pass a benefit-cost test, policymakers would have to have external costs of oil-dependency that are 3 to 5 times greater than our central value of the external costs of oil dependency.
Conclusions • When RFS replaces VEETC, • The ratio of benefits to costs improves to 0.9 and net costs per EGG fall to $0.36 to $0.19. • Instead of a trade-off, we have instead a simultaneous welfare improvement in environmental benefits and oil dependency, with each dollar benefit in oil dependency complemented with a $1-2 gain in environmental benefits. • The implied value of oil dependency needed for RFS to pass a benefit-cost test would still have to be1.5-2 times greater than our central parameter estimate.
Acknowledgements • ( • Cornell University Agricultural Experiment Station • Cornell Center for a Sustainable Future Cornell Institute for Computational Sustainability