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The Congestion Mitigation and Air Quality Improvement Program
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| Proposal Category | Number of Proposals Funded | Proposals with Emissions Benefits Reported | Percent with Benefits Reported |
|---|---|---|---|
| Transit | 246 | 183 | 74% |
| Traffic Flow | 401 | 300 | 75% |
| Shared Ride | 98 | 76 | 76% |
| Other TCM & I/M | 92 | 54 | 59% |
| Ped/Bike | 82 | 58 | 71% |
| Demand Management | 68 | 43 | 63% |
| Total | 987 | 714 | 72% |
As shown in Figures 3 through 6, the majority of proposals submitted under the CMAQ program have less than 5 kg/day emission reduction potential based on estimates provided by States in their annual CMAQ reports. Approximately half of VOC emission estimates provided by States (331 of 649 reporting VOC emissions reductions), yield 5 kg/day or less, and 91 percent yield less than 100 kg/day. However (as shown in Figure 4) a substantial number of CMAQ-funded proposals submitted with emission estimates for CO (23 percent) target emissions reductions in the 100 to 1000 kg/day emissions range, due primarily to the larger amount of CO emitted from the tailpipe relative to VOC or NOx emissions.
A summary (Table 4) provides an overview of the four major transportation-related pollutants in terms of the number of analyses, as well as minimum, maximum, and median ranges of emission reduction estimates provided by States in their FY 1999 annual reports. The range of minimum, maximum, and median emissions estimates are consistent with those estimates reported in previous CMAQ annual reports.
| Emission Type | Number1 | Minimum | Median2 | Maximum |
|---|---|---|---|---|
| VOC | 653 | -3 | 5 | 40,814 |
| CO | 345 | -4 | 30 | 8,111 |
| NOx | 575 | -93 | 3 | 37,113 |
| PM-10 | 52 | 0 | 3 | 3,758 |
| Total Estimates | 1,625 | |||
| NOTES: 1The number of projects submitted with VOC, CO, PM-10 and/or NOx emissions analysis respectively. 2The median, rather than the mean, is a better representation of average effectiveness because the mean is unduly influenced by relatively few projects with large emissions reductions. The median is the point above or below which 50 percent of all observations lie when ranked highest to lowest. Emissions reductions are provided without comment as to their accuracy. |
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Table 5 (below) provides VOC emission information gathered from State CMAQ annual reports that suggests that the greatest median air quality emissions reductions occur in the demand management category. The lowest level of benefits reported is in the pedestrian/bicycle category. However, the emission reductions of these projects is comparable to others on average, and these are also the least expensive projects reported. Out of the 653 CMAQ proposals submitted with VOC emission reductions estimates, the traffic flow improvement category has the largest single share of projects (285) with quantitative estimates (median value of 4 kg/day VOC emissions removed from the atmosphere). The largest amount of VOC emissions reductions are associated with the "Other TCMs" category (e.g., enhanced I/M programs, etc.) as noted in previous CMAQ annual reports.
| Type of Project | Number1 | Minimum | Median | Maximum |
|---|---|---|---|---|
| Transit | 173 | -3 | 4 | 1,403 |
| Traffic Flow | 285 | 0 | 5 | 1,423 |
| Shared Ride | 72 | 0 | 7 | 972 |
| Other TCMs | 34 | 0 | 4 | 40,814 |
| Ped/Bike | 48 | 0 | 3 | 481 |
| Demand Mgmt | 41 | 1 | 27 | 529 |
| Total | 653 | |||
| NOTES: 1The number of projects submitted with VOC emissions analysis respectively. |
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Table 6 (below) shows the emissions benefits of 345 CMAQ-funded proposals in kg/day of CO removed from the atmosphere. The category of demand management is shown to have the highest median value for CO (202 kg/day) significantly higher than the median estimates of CO reductions for other categories.
| Type of Project | Number1 | Minimum | Median | Maximum |
|---|---|---|---|---|
| Transit | 90 | -4 | 30 | 8,101 |
| Traffic Flow | 138 | 0 | 19 | 8,111 |
| Shared Ride | 35 | 0 | 49 | 7,599 |
| Other TCMs | 28 | 1 | 30 | 1,100 |
| Ped/Bike | 26 | 0 | 20 | 217 |
| Demand Mgmt | 28 | 2 | 202 | 3,701 |
| Total | 345 | |||
| NOTES: 1The number of projects submitted with CO emissions analysis respectively. |
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Table 7 (below) shows the minimum, median, and maximum emissions benefits for NOx based on data provided by States in their FY 1999 annual reports. Out of 575 CMAQ proposals submitted with NOx emissions reductions estimates, the category of projects with the most NOx emissions reductions estimates is again shown to be traffic flow improvements.
| Type of Project | Number1 | Minimum | Median | Maximum |
|---|---|---|---|---|
| Transit | 162 | -20 | 5 | 1,390 |
| Traffic Flow | 235 | -93 | 1 | 790 |
| Shared Ride | 71 | -3 | 10 | 2,149 |
| Other TCMs | 33 | 0 | 5 | 37,113 |
| Ped/Bike | 40 | 0 | 3 | 472 |
| Demand Mgmt | 34 | -20 | 20 | 868 |
| Total | 575 | |||
| NOTES: 1The number of projects submitted with NOx emissions analysis respectively. |
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However, the highest median value of NOx emission reductions potential (20 kg/day) is again shown to be in the demand management category. In fact, the demand management category accounted for the highest median values in all three pollutant types shown in Tables 5-7, although the number of projects in this category is small compared to the others.
Table 8 (below) shows the emissions benefits of 52 CMAQ-funded proposals in kg/day of PM-10 removed from the atmosphere. The category of demand management is shown to have the highest median value for PM-10 (406 kg/day), but this should be discounted heavily since there was only one demand management project with a PM-10 estimate.
| Type of Project | Number1 | Minimum | Median | Maximum |
|---|---|---|---|---|
| Transit | 17 | 0 | 2 | 232 |
| Traffic Flow | 3 | 0 | 0 | 1 |
| Shared Ride | 6 | 1 | 15 | 486 |
| Other TCMs | 18 | 1 | 123 | 3,758 |
| Ped/Bike | 7 | 0 | 0 | 140 |
| Demand Mgmt | 1 | 406 | 406 | 406 |
| TOTAL | 52 | |||
| NOTES: 1The number of projects submitted with PM-10 emissions analysis respectively. |
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Table 9 (below) summarizes the top CMAQ-funded proposals with at least 500 kg/day VOC emission reduction potential based on data provided by States in their annual reports. As shown in this table the two projects resulting in the greatest VOC reductions were the same as reported in the FY 1998 report, which were related to enhanced I/M programs. The total number of CMAQ-funded proposals with at least 500 kg/day VOC emission reductions was found to be 13 for 1999, up one from FY 1998 and down three from FY 1997.
| Project Description | Project Type | State | Emissions Benefits(kg/day) |
|---|---|---|---|
| Statewide Enhanced Vehicle Inspection and Maintenance programs | I/M and Other TCMs | New Jersey | 40,814 |
| FY 1999 Enhanced Emissions Testing Program | I/M and Other TCMs | Connecticut | 33,303 |
| Maintenance and Engineering for traffic operations center - Oakland county | Traffic Flow Improvements | Michigan | 1,423 |
| Detroit-SEMCOG Nonattainment Area Ozone Action Program | Transit | Michigan | 1,403 |
| TANK-Clean Air Fare | Transit | Kentucky | 1,343 |
| Metro pool Rideshare Programs | Shared Ride | New York | 972 |
| TARC-Ozone Buster Fares | Transit | Kentucky | 958 |
| Tampa Traffic Signal Control | Traffic Flow Improvements | Florida | 575 |
| Bi-State Development Agency Bus Replacement | Transit | Missouri | 573 |
| Los Angeles County - Light Rail-Red Line | Transit | California | 568 |
| MTA Harlem Third Track | Transit | New York | 560 |
| Advanced Transportation Management System Design Group I | Traffic Flow Improvements | Florida | 548 |
| Regional Center Signal System - Marion County | Traffic Flow Improvements | Indiana | 548 |
Based on review of the State annual reports submitted for FY 1999, the following areas will need additional improvement as the CMAQ program evolves throughout its existence under the TEA-21. As found in previous reviews of State annual reports, additional efforts to provide more than minimal project descriptions would assist FHWA and FTA in the future. In some cases, project descriptions were found to be inadequate, and thus required follow up phone conversations to State and local officials to better identify the CMAQ projects and their potential air quality benefits. Also, the estimates of emissions benefits that were used to determine CMAQ eligibility for the projects should be submitted in the State reports.
This information is gathered to respond to Congressional inquiries and to support briefings to higher ranking Administration officials, and other major stakeholders which are routinely performed by FHWA/FTA. The basis for information provided is often derived from annual CMAQ reports submitted by States.
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