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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 />

close to 30 years (ORNL, 2008, Table 3.12). Therefore substantial penetration of new OEM<br />

technologies can take several years after commercialization.<br />

On the other hand, OEM strategies should have a disproportionately large impact on fuel<br />

consumption s<strong>in</strong>ce older vehicles travel significantly less on average than new vehicles. A<br />

10-year-old truck travels only about 40 percent of the distance annually of a new truck,<br />

and a 20-year-old truck less than 20 percent. 44<br />

In addition to advancements related to vehicle efficiency, diesel HDVs are <strong>in</strong> the process<br />

of adopt<strong>in</strong>g control technologies <strong>in</strong> order to meet <strong>in</strong>creas<strong>in</strong>gly str<strong>in</strong>gent NOx and PM<br />

emission standards. The latest EPA heavy diesel standards require 90 percent reductions<br />

<strong>in</strong> PM <strong>in</strong> 2007 and 90 percent NOx reductions by 2010 relative to prior emission standards<br />

(U.S. EPA, 2006). The technologies used to meet these standards, such as particulate filters<br />

and NOx absorbers, have their own energy requirements, and add weight to the vehicles.<br />

As such, these technologies may reduce fuel efficiency <strong>in</strong> some cases by about one percent<br />

for particulate filters, and roughly five percent for NOx control us<strong>in</strong>g exhaust gas<br />

recirculation, and other recent strategies (U.S. DOE, 2009b; Greszler, 2008). Newer<br />

emission control technologies may <strong>in</strong>crease fuel efficiency to the extent that they allow the<br />

diesel eng<strong>in</strong>e to operate more efficiently.<br />

3-60<br />

The effectiveness of different efficiency<br />

strategies also will vary with vehicle age due to the fact that vehicles may change<br />

operators and duty-cycles after a number of years. For example, Class 8 trucks commonly<br />

spend the first four to six years of their life <strong>in</strong> long-haul service, which entails higher<br />

speed operation (and greater mileage accumulation) than other service types (Lutsey,<br />

2008). After this time, these trucks are often moved <strong>in</strong>to lower mileage, urban/short-haul<br />

applications. These different service types and operation modes obta<strong>in</strong> substantially<br />

different benefits from different efficiency technologies. For example, aerodynamic and<br />

roll<strong>in</strong>g resistance strategies obta<strong>in</strong> their maximum benefit at highway speeds, while<br />

hybrid technologies are best suited for lower speed urban drive cycles.<br />

The follow<strong>in</strong>g sections discuss resistance reduction strategies, weight reduction, eng<strong>in</strong>e<br />

improvements (<strong>in</strong>clud<strong>in</strong>g hybrid power systems), and strategies to reduce vehicle<br />

accessory loads. (Alternative fuel and fuel cell strategies are discussed <strong>in</strong> tandem with<br />

their associated fuel type <strong>in</strong> Section 2.0.) The basel<strong>in</strong>e emission estimates used below are<br />

based on the AEO Reference case for 2030, which estimates fleet average fuel efficiency on<br />

an annual basis. Annual <strong>in</strong>cremental emission reductions and total costs for each<br />

technology option are based on a variety of projections found <strong>in</strong> the literature. The costeffectiveness<br />

of packages of multiple technology strategies (e.g., hybrid electric vehicles<br />

with advanced aerodynamics) are discussed separately at the end of the HDV section.<br />

44 Based on mileage accumulation data from EPA’s MOBILE6 emission factor model.

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