| Health Factors: | Environmental Quality |
|---|---|
| Decision Makers: | ![]() ![]() ![]() ![]() Businesses & Employers, Government - Local, Government - State, Government - Federal, Schools |
| Evidence Rating: | |
| Population Reach: | 100% of WI's population |
| Impact on Disparities: |
Is this program or policy in use in your community? Tell us about it.
Retrofitting diesel busses involves installing control devices such as diesel particulate filters (DPF), diesel oxidation catalysts (DOC), and closed crankcase ventilation systems (CCV) on diesel powered engines in order to reduce exhaust emissions.
Decreased emissions
Improved air quality
There is strong evidence that retrofitting diesel busses decreases environmental exhaust emissions (US EPA-Transportation 2006, Zhang 2011, Barone 2010). Retrofitting diesel busses has also been shown to improve in-cabin air quality by decreasing particulate matter, organic carbon, and elemental carbon in some circumstances (Borak 2007, Trenbath 2009, Barone 2010).
Decreases in emissions associated with retrofitting diesel busses appear to have positive effects on riders' health. A Washington-based study found reductions in bronchitis, asthma, and pneumonia in children in school districts with retrofitted busses (Beatty 2011). Retrofitting may also decrease the costs associated with respiratory disease-related hospitalizations and treatment (Beatty 2011).
A Washington-based cost-benefit analysis finds that school bus retrofitting has positive net benefits (Beatty 2011).
The majority of states have either mandatory or voluntary diesel retrofit, repower, and replacement policies in place (CATF-Diesel 2010).
The Wisconsin DNR and the Wisconsin Clean Diesel Coalition encourage diesel emission reduction strategies. Additionally, Wisconsin Partners for Clean Air (WPCA-cleaner school buses), with support from a federal Congestion Mitigation and Air Quality (US DOT-CMAQ) grant, administers a diesel retrofit program that includes school buses, municipal busses, and off-road equipment in Wisconsin's ozone non-attainment areas, (Door, Kenosha, Kewaunee, Manitowoc, Milwaukee, Ozaukee, Racine, Sheboygan, Washington, and Waukesha counties).
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Social & Economic Factors |
Physical Environment |
Level of effectiveness based on a scan of academic literature and key recommendations of leading organizations.
Although many policies and programs are recommended by credible groups, we apply the rating ‘expert opinion’ only when policies are recommended but limited scientific evidence of effectiveness is available.
* The American Heritage Dictionary defines credible as 'capable of being believed; plausible.' and 'worthy of confidence; reliable.' To be considered an 'expert recommendation,' policies and programs must be recommended by one or more organizations that are recognized for their impartial expertise in the area of interest and have limited evidence available.
Portion of Wisconsin's population likely to be reached by a policy or program if implemented statewide, based on its characteristics (e.g., target population(s), geographic limitations, and potential implementers).
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<1% | ![]() |
20-49% | |
![]() |
1-9% | ![]() |
50-99% | |
![]() |
10-19% | ![]() |
100% |
Portion of Wisconsin's population likely to be reached by a policy or program if implemented statewide, based on its characteristics (e.g., target population(s), geographic limitations, and potential implementers).
![]() |
<1% | ![]() |
20-49% | |
![]() |
1-9% | ![]() |
50-99% | |
![]() |
10-19% | ![]() |
100% |
Likely impact of a given policy or program on racial/ethnic, socioeconomic, geographic or other disparities in Wisconsin based on its characteristics (e.g., target audience, mode of delivery, etc.) and best available evidence related to disparities.