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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 />

overall costs and cost-effectiveness for BEVs. First, electricity costs vary across the United<br />

States depend<strong>in</strong>g on location, type of generation, and time of use. The average cost of<br />

residential electricity <strong>in</strong> 2010 is estimated at 9.8 cents per kWh, projected to <strong>in</strong>crease to 11.8<br />

cents per kWh by 2030. 42 A charg<strong>in</strong>g price of 10 cents per kWh is used for this analysis<br />

(Kammen). The additional electricity demand from charg<strong>in</strong>g of BEVs <strong>in</strong> the near term is<br />

not expected to have a significant impact on overall electricity use or prices. 43<br />

Assum<strong>in</strong>g 10 cents per kWh, and a 0.26 kWh/mi efficiency, BEV operation costs would be<br />

approximately 2 cents per mile, compared to a conventional gasol<strong>in</strong>e LDV <strong>in</strong> 2010 at about<br />

8 cents per mile (or 12.2 cents per mile <strong>in</strong> 2030 pretax, us<strong>in</strong>g AEO Reference case<br />

assumptions). The result<strong>in</strong>g cost differentials are used to develop the estimated cost and<br />

cost-effectiveness estimates for BEVs, as shown <strong>in</strong> 2.15. Due to the extremely high<br />

<strong>in</strong>cremental costs associated with current BEVs, a near-term scenario is not considered.<br />

This analysis also assumes that battery replacement will not be required over the useful<br />

life of the BEV.<br />

2-72<br />

Details<br />

regard<strong>in</strong>g potential impacts of <strong>in</strong>creased charg<strong>in</strong>g demand on electricity generation <strong>in</strong> the<br />

medium to long term are discussed <strong>in</strong> Section 3.2.4.<br />

Table 2.15 BEV per Vehicle Cost and Cost-Effectiveness Range<br />

2030<br />

Lifetime Discounted Net Avg. GHG<br />

Range Incremental kWh/ Gallons Fuel Discounted Reduction Dollars/Tonne<br />

(Mile) Vehicle Cost mi Saved Sav<strong>in</strong>gsa Cost/Sav<strong>in</strong>gs (Tonnes/Year) Calculated Literature<br />

100 $6,000 0.26 6,500 $11,300 -$3,500 3.1-3.7 -$90 to -<br />

$106<br />

200 $10,200 0.26 6,500 $11,300 -$1,100 3.1-3.7 -$19 to -<br />

$22<br />

$100 to<br />

$343<br />

a Us<strong>in</strong>g pretax AEO price projections for gasol<strong>in</strong>e and typical electricity estimate – $3.43 and 10 cents/kWh,<br />

respectively.<br />

The above cost-effectiveness assessment is not consistent with the values found <strong>in</strong> the<br />

literature. Estimates from Bandivadekar et al. (which utilize the same <strong>in</strong>cremental vehicle<br />

cost ranges, but higher gasol<strong>in</strong>e costs and lower BEV efficiency assumptions), estimated<br />

42 AEO Table 8.<br />

43 For example, an <strong>in</strong>crease of 10,000 BEVs <strong>in</strong> California would only result <strong>in</strong> an <strong>in</strong>crease of roughly<br />

0.06 percent of the state’s total power demand (CARB, 2003).

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