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

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Transportations <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 />

26 percent, which is considered low by <strong>in</strong>dustry standards. Therefore this analysis<br />

adjusted the EPA estimate to reflect a retail markup factor of 70 percent, which<br />

corresponds closely to the 75 percent factor applied by NREL (U.S. EPA, 2005; Markel<br />

et al., 2006). The f<strong>in</strong>al adjusted <strong>in</strong>cremental vehicle cost is therefore estimated to be $2,000.<br />

Cost estimates of the above technology packages were found <strong>in</strong> the literature, and the<br />

AEO Reference case also provides average LDV costs by year. Incremental technology<br />

cost <strong>in</strong>creases for advanced LDVs were taken from the literature, and the net <strong>in</strong>crease<br />

above the AEO average vehicle price was subtracted for the near- and medium-term<br />

evaluations, provid<strong>in</strong>g the <strong>in</strong>cremental cost of the technology packages relative to the<br />

AEO base case. 14<br />

For the advanced conventional gasol<strong>in</strong>e package, vehicles <strong>in</strong> the near, mid, and long terms<br />

offer a net sav<strong>in</strong>gs over the entire range of costs and benefits. This is due to fuel sav<strong>in</strong>gs<br />

and to the possibility that eng<strong>in</strong>e downsiz<strong>in</strong>g could reduce estimated vehicle costs (as<br />

presented <strong>in</strong> the literature <strong>in</strong> some cases). The cost per tonne of CO2 reduction calculated<br />

us<strong>in</strong>g the above methodology and assumptions is negative, mean<strong>in</strong>g that there would be a<br />

net sav<strong>in</strong>gs over a vehicle’s life, as well as CO2 reductions. In the near term, however, the<br />

cost per tonne range extends <strong>in</strong>to both negative and positive values. The costeffectiveness<br />

values reported <strong>in</strong> the literature <strong>in</strong>clude both negative and positive values as<br />

well, from -$175 to +$161 per tonne. (Bandivadekar et al., 2008; Lutsey, 2009; CARB, 2004;<br />

Fulton and Cazzola, 2008). In general, the literature cost per tonne values were higher<br />

than those calculated <strong>in</strong> this analysis. Although detailed cost assumptions and calculation<br />

methods were not specified <strong>in</strong> all of the sources reviewed, the higher end costeffectiveness<br />

values were likely based on lower assumed gasol<strong>in</strong>e prices than the current<br />

AEO projections. Fuel price assumptions are a driv<strong>in</strong>g factor <strong>in</strong> cost-effectiveness<br />

determ<strong>in</strong>ation, and <strong>in</strong> turn, dollar per tonne estimates should be considered quite<br />

uncerta<strong>in</strong> due to fuel price volatility alone. Nevertheless, there is general agreement that<br />

advanced technologies available for conventional gasol<strong>in</strong>e vehicles will be cost-effective<br />

options for reduc<strong>in</strong>g GHG emissions <strong>in</strong> the long term.<br />

The emission reduction and cost estimates from NHTSA’s f<strong>in</strong>al rulemak<strong>in</strong>g for the 2011<br />

CAFE standards are presented <strong>in</strong> Table 3.2D. The CAFE analysis performed a highly<br />

detailed, bottom-up assessment of the costs and benefits associated with a large number of<br />

possible technologies that could be applied to the LDV market <strong>in</strong> the near term. The<br />

analysis also evaluated the potential <strong>in</strong>teractions among the different technologies and the<br />

development “path” that might be followed, consider<strong>in</strong>g the order <strong>in</strong> which <strong>in</strong>dividual<br />

technologies might be added to <strong>in</strong>creas<strong>in</strong>gly complex packages (NHTSA, 2009b). These<br />

packages do not directly correlate with the gasol<strong>in</strong>e package presented <strong>in</strong> this report,<br />

however, as they <strong>in</strong>cluded different group<strong>in</strong>gs of technologies. While the NHTSA<br />

14 Lifetime per vehicle costs and benefits were calculated for advanced LDVs replac<strong>in</strong>g conventional<br />

gasol<strong>in</strong>e LDVs for the different time frames. Pre-tax fuel prices obta<strong>in</strong>ed from AEO projections<br />

were utilized to estimate fuel sav<strong>in</strong>gs over the life of the advanced vehicle. The specific<br />

assumptions regard<strong>in</strong>g mileage accumulation rates, useful life, and assumed discount rate are<br />

discussed <strong>in</strong> Appendix A.<br />

3-32

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