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Transportation's Role in Reducing U.S. Greenhouse Gas Emissions ...

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Transportation’s <strong>Role</strong> <strong>in</strong> Reduc<strong>in</strong>g U.S. <strong>Greenhouse</strong> <strong>Gas</strong> <strong>Emissions</strong>: Volume 2<br />

can match a vehicle technology with a variety of different fuel options. In fact,<br />

GREET <strong>in</strong>cludes more than 100 fuel production pathways and more than 70<br />

vehicle systems. The GREET model is based solely on fuel type and vehicle<br />

technology, whereas other transportation models (such as TAFV, M<strong>in</strong>iCam, and<br />

NEMS) project transportation emissions based on an expected economic<br />

situation and/or likely consumer behavior.<br />

This analysis uses the default values found <strong>in</strong> GREET <strong>in</strong> order to assess the<br />

lifecycle impacts of alternative fuels relative to conventional gasol<strong>in</strong>e and diesel.<br />

The grams per vehicle mile traveled values <strong>in</strong> Table A.1 account for key GHGs,<br />

converted to CO 2 equivalents us<strong>in</strong>g a 100 year (default) global warm<strong>in</strong>g<br />

potential (GWP). Results from the model vary significantly depend<strong>in</strong>g on<br />

various assumptions related to fuel production technology and end-use. In<br />

addition, GREET does not account for <strong>in</strong>direct land use changes or other<br />

<strong>in</strong>direct effects that may significantly impact f<strong>in</strong>al results for biofuels <strong>in</strong><br />

particular. Other key limitations of GREET’s “direct attributional approach”<br />

<strong>in</strong>clude (U.S. EPA, 2009a):<br />

• The economic impact of biofuel coproducts on other sectors, such as<br />

livestock feed markets and associated <strong>in</strong>direct GHG impacts, were not<br />

adequately assessed;<br />

• Specific policy measures could not be evaluated <strong>in</strong> detail as a function of<br />

different production targets, especially with regard to agricultural sector<br />

impacts;<br />

• Fuel replacement impacts were assessed on an average gallon of fuel basis,<br />

rather than evaluat<strong>in</strong>g the specific alternative fuel production and<br />

conventional fuel replacement emissions at the marg<strong>in</strong>; and<br />

• The RFS1 evaluation methodology did not account for the effects of fall<strong>in</strong>g<br />

U.S. petroleum demand on world fuel prices, and subsequent <strong>in</strong>creases <strong>in</strong><br />

<strong>in</strong>ternational petroleum consumption.<br />

Depend<strong>in</strong>g upon the nature of the analysis, GREET grams per mile outputs<br />

were frequently converted to equivalent grams per gallon values, <strong>in</strong> order to<br />

compare the potential GHG impacts of alternative fuels compared with<br />

conventional gasol<strong>in</strong>e and diesel. In this way the impact of chang<strong>in</strong>g fuel<br />

efficiencies over time could be accounted for without hav<strong>in</strong>g to re-run the<br />

GREET model for each time period of <strong>in</strong>terest. In addition, <strong>in</strong> most cases this<br />

analysis assumes that alternative fuel vehicles accrue fuel efficiency<br />

improvements at the same rate over time as the comparable conventional<br />

basel<strong>in</strong>e vehicle. This simplify<strong>in</strong>g assumption is not made for fuel cell and<br />

battery electric vehicles, as the source of motive power and drive tra<strong>in</strong><br />

configurations can be fundamentally different than conventional <strong>in</strong>ternal<br />

combustion eng<strong>in</strong>e vehicles.<br />

A-7

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