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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 />

Table 5.5 Average Annual Capital Requirement, 2006-2026<br />

Billions of Dollars<br />

Needs Component<br />

5-40<br />

Replacement/<br />

Rehabilitation of<br />

Exist<strong>in</strong>g Assets<br />

Ma<strong>in</strong>ta<strong>in</strong> Physical Conditions, Improve Service Performance<br />

Total Includ<strong>in</strong>g Expansion and Modernization of Assets<br />

to Accommodate Annual Ridership Growth at:<br />

2.4% 3.5% 4.6%<br />

Urbanized Area Total $13.9 $40.8 $53.9 $69.9<br />

Rural/Small Urban $0.8 $1.5 $1.5 $1.5<br />

Total Needs $14.7 $42.4 $55.4 $71.4<br />

Source: AASHTO, 2009.<br />

The Mov<strong>in</strong>g Cooler study used these estimates of capital <strong>in</strong>vestment needs, <strong>in</strong> conjunction<br />

with estimates of future annual operat<strong>in</strong>g costs, to estimate total cost-effectiveness <strong>in</strong> terms<br />

of GHG reduced for transit system expansion. 21 Consider<strong>in</strong>g direct implementation<br />

(capital and operat<strong>in</strong>g) costs only, cost-effectiveness to meet the three ridership growth<br />

rates is estimated to be about $1,800 to $2,000 per tonne for urban transit expansion and<br />

$1,200 to $3,000 per tonne for level of service <strong>in</strong>creases. Includ<strong>in</strong>g vehicle operat<strong>in</strong>g cost<br />

sav<strong>in</strong>gs to private vehicle owners as a result of a reduction <strong>in</strong> VMT, cost-effectiveness<br />

ranges from $800 to $1,000 per tonne for system expansion and -$260 to +$130 per tonne<br />

for service improvements. Direct cost-effectiveness is not estimated for transit fare<br />

reductions, as the change <strong>in</strong> fare is simply a revenue transfer from the public sector to the<br />

transit rider; vehicle operat<strong>in</strong>g cost sav<strong>in</strong>gs would provide a net sav<strong>in</strong>gs of about -$900 per<br />

tonne (Cambridge Systematics, 2009).<br />

Cobenefits<br />

A significant co-benefit associated with transit is its ability to reduce the relative degree<br />

that those who choose not to drive, or who do not own vehicles, are disadvantaged<br />

compared with drivers (VTPI, 2008d). Transit <strong>in</strong>creases accessibility to economic and<br />

social opportunities, and helps achieve equity objectives, such as help<strong>in</strong>g physically and<br />

economically disadvantaged people access public services, education, and employment.<br />

Transit will result <strong>in</strong> reductions of some criteria pollutant emissions, but may cause<br />

<strong>in</strong>creases <strong>in</strong> others. The relative emissions impacts will depend upon the vehicle type<br />

(small bus, 40-foot bus, light rail, locomotive, etc.); fuel source (diesel, natural gas, electric);<br />

electricity generation source (for electric rail or trolley bus systems); vehicle emissions<br />

control technology; and operat<strong>in</strong>g characteristics of the vehicle (e.g., average speed, time<br />

21 Exclud<strong>in</strong>g paratransit services, the estimate for operat<strong>in</strong>g costs per unl<strong>in</strong>ked transit trip <strong>in</strong> 2007 is<br />

$2.61 (FTA, 2008). The cost per unl<strong>in</strong>ked trip is assumed to <strong>in</strong>crease with <strong>in</strong>flation through 2050.

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