Indirect fuel use change (IFUC) and the lifecycle environmental impact of biofuel policies

A common assumption in lifecycle assessment (LCA) based estimates of greenhouse gas (GHG) benefits (or costs) of renewable fuel such as biofuel is that it simply replaces an energy-equivalent amount of fossil fuel and that total fuel consumption remains unchanged. However, the adoption of renewable fuels will affect the price of fuel and therefore affect total fuel consumption which, may increase or decrease depending on the policy regime and market conditions. Using a representative two-region model of the global oil market in which, one region implements a domestic biofuel mandate and the other does not, we show that the net change in global fuel consumption due to the policy, which we term indirect fuel use change (IFUC), can have a significant impact on the net GHG emissions associated with biofuel. If LCA-based regulations are designed to account for indirect emissions such as indirect land use change, then we argue that IFUC emissions cannot be ignored. Our work also shows how different policies can affect the environmental impact from adopting a given clean technology differently.

[1]  David Zilberman,et al.  The Effect of Biofuels on Crude Oil Markets , 2010 .

[2]  D. Graham,et al.  The Demand for Automobile Fuel A Survey of Elasticities , 2002 .

[3]  David Zilberman,et al.  Model estimates food-versus-biofuel trade-off , 2009 .

[4]  David Zilberman,et al.  Challenge of biofuel: filling the tank without emptying the stomach? , 2007 .

[5]  S. Joshi Product Environmental Life‐Cycle Assessment Using Input‐Output Techniques , 1999 .

[6]  M. Delucchi,et al.  Impacts of biofuels on climate change, water use, and land use , 2010, Annals of the New York Academy of Sciences.

[7]  Noureddine Krichene,et al.  World crude oil and natural gas: a demand and supply model , 2002 .

[8]  C. Fischer,et al.  Renewable Portfolio Standards: When Do They Lower Energy Prices? , 2010 .

[9]  Alissa Kendall,et al.  Proper accounting for time increases crop-based biofuels’ greenhouse gas deficit versus petroleum , 2009 .

[10]  Dileep K. Birur,et al.  Land Use Changes and Consequent CO2 Emissions due to US Corn Ethanol Production: A Comprehensive Analysis , 2010 .

[11]  D. Pimentel,et al.  Ethanol Production Using Corn, Switchgrass, and Wood; Biodiesel Production Using Soybean and Sunflower , 2005 .

[12]  John C. B. Cooper Price Elasticity of Demand for Crude Oil: Estimates for 23 Countries , 2003 .

[13]  Deepak Rajagopal,et al.  Economics of Lifecycle analysis and greenhouse gas regulations , 2009 .

[14]  J. Tinbergen On the Theory of Economic Policy , 1954 .

[15]  Andrew D. Jones,et al.  Supporting Online Material for: Ethanol Can Contribute To Energy and Environmental Goals , 2006 .

[16]  D. Just,et al.  The Welfare Economics of a Biofuel Tax Credit and the Interaction Effects with Price Contingent Farm Subsidies , 2009 .

[17]  Jacinto F. Fabiosa,et al.  Use of U.S. Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land-Use Change , 2008, Science.

[18]  Andrew D. Jones,et al.  Effects of US Maize Ethanol on Global Land Use and Greenhouse Gas Emissions: Estimating Market-Mediated Responses , 2010 .

[19]  Mark A. Delucchi,et al.  Incorporating the Effect of Price Changes on CO2-Equivalent Emissions From Alternative-Fuel Lifecycles: Scoping the Issues , 2005 .

[20]  John Sheehan,et al.  An Overview of Biodiesel and Petroleum Diesel Life Cycles , 2000 .

[21]  J. Fava,et al.  Life‐Cycle Assessment Practitioner Survey: Summary of Results , 2006 .