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Cost Effectiveness Comparisons

Cost Effectiveness Comparisons For Various CMAQ-Eligible Emissions Reduction Programs

Diesel retrofits are one of the most cost-effective emissions reductions strategies eligible for funding under the Congestion Mitigation and Air Quality Improvement (CMAQ) program. The following chart compares cost-effectiveness data from specific diesel retrofit projects with data collected by both the Washington (DC) Council of Governments and the Transportation Research Board measuring the cost-effectiveness of other typical CMAQ-eligible projects.

Cost Per Ton of Nitrogen Oxides (NOX) Reduced

 



  1. Data collected by government agencies overseeing specific diesel retrofit projects. Cost-effectiveness for each project depends on factors including: age and type of equipment being retrofit; off-road vs. on-road applications; Tier 0, 1, or 2 technologies; and other factors. Readers are encouraged to review source materials for assumptions.

    Examples cited are:

    Repower Lumber Loaders – South Coast Air Quality Management District project repowering 15 self-propelled lumber loaders (Los Angeles)

    Retrofit Transit Buses – Metropolitan Transportation Commission project retrofitting 1100 transit buses with Cleaire Longview ฎ (San Francisco Bay Area)

    Repower Off-Road Engines – California Air Resources Board project repowering off-road engines, such as graders and forklifts (nonattainment areas statewide)

    Repower Construction Equipment – South Coast Air Quality Management District project repowering 18 heavy-duty construction equipment engines (Los Angeles)

    Replace Older Trucks – Gateway Cities COG project replacing 250 pre-1983 heavy-duty diesel trucks with 1994 and newer trucks (southeast Los Angeles County)

  2. Median cost-effectiveness estimate from the Transportation Research Board’s (TRB) 2002 study The Congestion Mitigation and Air Quality Improvement Program: Assessing 10 Years of Experience, page 341. Cost-effectiveness depends on numerous factors including participation levels, capital and operating costs, transit ridership, and other factors. See TRB report for methodologies and assumptions.

  3. Cost-effectiveness calculations made by the Washington (DC) Council of Governments for specific projects. All projects shown in cost per ton of NOx using 2005 emissions factors. Details on projects include:

    Speed Limit Enforcement – 95 miles of enforcement in Northern Virginia

    Taxicab Replacement with CNG – Project replaced 100 cabs

    Bike Racks on Transit Buses – Bike racks on all buses

    Bus Replacement with CNG – Calculation made on 100 CNG buses
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