Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
MTA has 794 buses available for service and the total vehicle miles in FFY 2001 were 21,774,843. (21,774,843 miles / 794 buses * 142 Buses = 3,894,241 overhaul bus miles) |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | NA |
Southwestern Research and MTA data indicates that each gram per brake horsepower-hour (g/bhp-hr) is equal to 1.5 tons of PM per 100,000 bus-miles. (3,894,241 overhaul bus miles / 100,000 miles * 1.5 tons = 58.41 tons of PM per g/bhp-hr) Data provided by the Engelhard Automotive Emissions Systems indicates that depending on the age of a bus and engine type, the PM can be reduced between 0.46 and 0.05 g/bhp-hr. The average will vary around 0.255 g/bhp-hr of PM. 0.255 g/bhp-hr x 58.41 (conversion of g/bhp-hr to tons)= 14.9 tons of PM per year 14.9 tons of PM per year * 2.4837895 conversion factor = kilograms / day |
Δ CO | NA | |
Δ PM10 | NA | |
Δ PM2.5 | - 34.77 kg/day | |
Δ Total | NA |
Project life: 7 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $5.458 M | $17.578 M | $23.036 M |
The total cost budgeted for the MTA fleet is $23.036 million; funds requested from the CMAQ program total $5.458 million, or 23.69 % of the total cost. Cost-effectiveness was not provided by the project sponsor. |
|
Adm/oper | $0 | $0 | $0 | ||
Total | $5.458 M | $17.578 M | $23.036 M | ||
Total annualized public cost | $5,095,000 | ||||
Annual revenues | None | ||||
Net public cost | $23.036 M | ||||
Annual private cost | NA | ||||
Total net cost | $23.036 M |
NOTE: The CMAQ funding portion listed in the CMAQ database for this project is $4,366,000.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
Orion buses travel 10,944 weekday miles and 9,784 weekend miles. Neoplan buses travel 7,056 weekday miles and 9,500 weekend miles. This schedule reflects peak vehicle use and includes both revenue miles and dead-head miles provided by the Westchester DOT and the service contractor. Assume 254 weekdays per year and 104 weekend days per year. |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 2.96 kg/day | METHODOLOGY/ASSUMPTIONS: | ||||||||||||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Δ NOx | + 14.64 kg/day* |
Emissions reductions were calculated from emissions with the retrofits provided by the Transit Resource Center and existing emissions from tailpipe testing. The average speed from testing Bee-Line bus duty cycle is 20 mph.
Total emissions reduced = (Number of Orion buses x Orion Bus VMT x (Existing emissions rate retrofit emissions rate)) + (Number of Neoplan buses x Neoplan Bus VMT x (Existing emissions rate retrofit emissions rate)) | ||||||||||||||||||||||||||||||||||||||
Δ CO | - 45.94 kg/day | |||||||||||||||||||||||||||||||||||||||
Δ PM10 | NA | |||||||||||||||||||||||||||||||||||||||
Δ PM2.5 | NA | |||||||||||||||||||||||||||||||||||||||
Δ Total | NA |
Project life: 7 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $1.2 M | $300,000 | $1.5 M | ||
Adm/oper | $0 | $0 | $0 | ||
Total | $1.2 M | $300,000 | $1.5 M | ||
Total annualized public cost | $311,000 | ||||
Annual revenues | None | ||||
Net public cost | $1.5 M | ||||
Annual private cost | NA | ||||
Total net cost | $1.5 M |
NOTE: The project sponsor noted that the increase in NOx emissions found is highly unusual, and it is widely accepted that this technology will have no impact on NOx. The other reductions also do not match with EPA's estimates: 60% reduction in HC, CO, and PM; no impact on NOx. The project sponsor did not calculate PM emissions reductions, but the cost-effectiveness analysis determined these values should be (2.3 kg/day reduced) The CMAQ funding portion listed in the CMAQ database for this project is $4,366,000.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
The average annual vehicle revenue miles for each of the 235 buses is 27,207 miles, with a deadhead factor of 1.15, and an average bus speed of 13.5 mph. Assumes each bus operates an average of 250 days per year. |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | -7.33 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | NA |
The EPA has certified this device to reduce HC and CO emissions by 60%, with no impact on NOx. Emissions reductions were calculated by multiplying the total emissions for the 1999 and 2000 buses using MOBILE6 emissions factors and then multiplying the VOC and CO emissions by 0.60. |
Δ CO | -111.22 kg/day | |
Δ PM10 | NA | |
Δ PM2.5 | NA | |
Δ Total | -7.33 kg/day (0.008 tpd) |
Project life: 7-8 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $1,793,520 | $449,000 | $2,242,520 |
Selected through the 2002 DVRPC Competitive CMAQ Program by the MPO, for funding in 2004. Cost-effectiveness was not provided by sponsor. |
|
Adm/oper | $0 | $0 | $0 | ||
Total | $1,793,520 | $449,000 | $2,242,520 | ||
Total annualized public cost | NA | ||||
Annual revenues | None | ||||
Net public cost | $2,242,520 | ||||
Annual private cost | NA | ||||
Total net cost | $2,242,520 |
NOTE: Emissions reductions provided by the State sponsor do not match those reported in the CMAQ database. Reported values are 0.77 VOC, - 6.29 CO, and - 0.57 NOx. EPA reports a 60% reduction in PM emissions, which are included in the cost-effectiveness calculations as 6.5 kg/day PM10 reduction and 5.7 kg/day PM2.5.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
Rogue Disposal's fleet of eighteen diesel-powered trash collection trucks consume over 400,000 gallons of fuel per year, emit a total of 2.13 tons of CO, 0.86 tons of VOCs, and 0.2 tons of PM, and travel up to 855,000 total miles annually. |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 1.43 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | NA |
The Rogue Valley MPO provided Mobile6 inputs for EPA's Retrofit Calculator. Based on the manufacturer's report, the following manual calculations were used:
|
Δ CO | - 2.49 kg/day | |
Δ PM10 | - 0.28 kg/day | |
Δ PM2.5 | NA | |
Δ Total | -1.7 kg/day |
Project life: 7 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $49,692 | $12,423 | $62,115 |
The project received an increase in funds to retrofit nine additional vehicles in July 2007. The grand total of this project has been amended to $124,615. CMAQ is funding 80% of this project, $99,692. |
|
Adm/oper | $0 | $0 | $0 | ||
Total | $49,692 | $12,423 | $62,115 | ||
Total annualized public cost | $12,457 | ||||
Annual revenues | None | ||||
Net public cost | $62,115 | ||||
Annual private cost | NA | ||||
Total net cost | $62,115 |
NOTE: Emissions reductions calculated above slightly differ from values reported in the CMAQ database (VOC: 1.39 kg/day, CO: 2.31 kg/day, PM10: 0.28 kg/day). EPA's retrofit calculator has since been replaced by new modeling tools: the Diesel Emissions Quantifier and the National Mobile Inventory Model (NMIM).
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
None |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 9.96 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | - 132.1 kg/day |
Baseline NOx emissions are calculated using the USEPA emissions standard for a Tier 0 switch engine. Baseline PM and VOC emissions are conservatively calculated using the lower uncontrolled USEPA emissions factors of 0.44 g/bhp-hr PM and 1.01 g/bhp-hr VOC in lieu of the Tier 0 standards of 0.72 g/bhp-hr PM and 2.1 g/bhp-hr VOC. Conventional switcher fuel use is 60,000 gal/yr. According to USEPA, the Brake-Specific Fuel Consumption (BSFC) is 20.8 bhp-hr/gal. GENSET locomotive emissions factors are based on Tier 3 nonroad engine standards (grams/bhp-hr) since the locomotive is powered by these engines. NMHC has the same meaning as VOC and HC. The GENSET fuel use is 25% less than a conventional switcher (45,000 gal/yr). The Brake-Specific Fuel Consumption (BSFC) for a GENSET engine is reported as 19.5 bhp-hr/gal.
Calculation also assumes 86% reduction in ozone precursors and 76% reduction in PM. |
Δ CO | NA | |
Δ PM10 | NA | |
Δ PM2.5 | - 3.68 kg/day | |
Δ Total | NA |
Project life: 5 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $3.36 M | $840,000 | $4.2 M |
|
|
Adm/oper | $0 | $0 | $0 | ||
Total | $3.36 M | $840,000 | $4.2 M | ||
Total annualized public cost | $1,042,000 | ||||
Annual revenues | None | ||||
Net public cost | $4.2 M | ||||
Annual private cost | NA | ||||
Total net cost | $4.2 M |
NOTE: The VOC and PM1.5 emissions reductions were calculated using similar methods as the NOx calculation shown.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
This project will retrofit approximately 53 on-road diesel powered vehicles and heavy duty equipment:
|
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 0.44 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | NA |
Emissions reductions calculated using Mobile6, EPA, and CARB emissions factors for a variety of heavy duty vehicles traveling at 23 mph for 4.43 miles per day for 305 days/year with and without the retrofits. The assumed speed, operating days, and travel distance was reported by Rockland County Highway Dept. as an average of their fleet vehicles equipped with GPS technology. |
Δ CO | -1.71 kg/day | |
Δ PM10 | - 0.18 kg/day | |
Δ PM2.5 | - 0.14 kg/day | |
Δ Total | NA |
Project life: 7 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $424,000 | $106,000 | $530,000 |
|
|
Adm/oper | $0 | $0 | $0 | ||
Total | $424,000 | $106,000 | $530,000 | ||
Total annualized public cost | $100,100 | ||||
Annual revenues | None | ||||
Net public cost | $530,000 | ||||
Annual private cost | NA | ||||
Total net cost | $530,000 |
NOTE: Benefits were estimated for 7 years (2011-2017). The calculation only assumes the vehicles travel 4.43 miles per day per vehicle, which sounds conservative.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA | |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 140.33 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | NA |
Emissions reductions calculated using Mobile6, EPA, and CARB emissions factors for a variety of vehicle types traveling at posted speeds. The assumed speed, operating days, and travel distance was reported by Rockland County Highway Dept. as an average of their fleet vehicles equipped with GPS technology. |
Δ CO | - 969.84 kg/day | |
Δ PM10 | - 138.35 kg/day | |
Δ PM2.5 | - 125.88 kg/day | |
Δ Total | NA |
Project life: 7-15 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $1.368 M | $342,000 | $1.71 M |
|
|
Adm/oper | $0 | $0 | $0 | ||
Total | $1.368 M | $342,000 | $1.71 M | ||
Total annualized public cost | $323,000 | ||||
Annual revenues | None | ||||
Net public cost | $1.71 M | ||||
Annual private cost | NA | ||||
Total net cost | $1.71 M |
NOTE: The cost-effectiveness analysis used in this study accounts for a stream of benefits over 7 years.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA |
None |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | - 4.47 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | - 60.4 kg/day |
Emissions reductions were calculated using a truck idle emissions factor from MOBILE6. Emissions for one truck idling for 10 hours each day are estimated to be removed by each IdleAire unit, as reported by the IdleAire company.
|
Δ CO | NA | |
Δ PM10 | NA | |
Δ PM2.5 | NA | |
Δ Total | - 64.87 kg/day |
Project life: 10 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $1.0 M | $0 | $1.0 M |
Cost-effectiveness was not provided by the project sponsor. |
|
Adm/oper | $0 | $0 | $0 | ||
Total | $1.0 M | $0 | $1.0 M | ||
Total annualized public cost | $163,300 | ||||
Annual revenues | None | ||||
Net public cost | $1,000,000 | ||||
Annual private cost | NA | ||||
Total net cost | $1,000,000 |
NOTE: When the figures were recalculated using EPA's current guidance on long duration truck idling; this results in a 135.0 kg/day reduction of NOx and 3.68 kg/day reduction of PM.
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA | |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | -6.68 kg/day | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | -110.17 kg/day |
The emission factors for CO and VOC come from EPA's Mobile6 Emissions Model to estimate the emissions from idling trucks. NOx and PM factors are calculated based on 2004 EPA Guidance. Emissions Reduction = Emission Factor (g/unit) x 50 units / 1000 (g to kg conversion factor) = Emissions Reduction (kg/day). An IdleAire utilization rate of 10 hours per day / 365 days per year is assumed. |
Δ CO | - 46.74 kg/day | |
Δ PM10 | NA | |
Δ PM2.5 | NA | |
Δ Total | NA |
Project life: 15-20 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $500,000 | $355,000 | $835,000 |
The CMAQ funds will satisfy the capital needs of the initial installation of these units. The IdleAire Corp will pay for the on-going operational costs. |
|
Adm/oper | $0 | $0 | $0 | ||
Total | $500,000 | $355,000 | $835,000 | ||
Total annualized public cost | NA | ||||
Annual revenues | None | ||||
Net public cost | $835,000 | ||||
Annual private cost | NA | ||||
Total net cost | $835,000 |
Δ Vehicle trips | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ VMT | NA | None. |
Δ Speed | NA | |
Δ Delay | NA | |
Δ SOV | NA | |
Δ CP/VP | NA | |
Δ Transit | NA | |
Δ Walk | NA | |
Δ Bike | NA |
Δ VOC | NA | METHODOLOGY/ASSUMPTIONS: |
---|---|---|
Δ NOx | -79.65 kg/day |
Idle emissions factors for trucks are taken from the EPA guidance document "Guidance for Quantifying and Using Long Duration Truck Idling Emissions Reductions in State Implementation Plans and Transportation Conformity." Emissions for one truck idling for 10 hours each day are estimated to be removed by each IdleAire unit, as reported by the IdleAire company.
|
Δ CO | NA | |
Δ PM10 | NA | |
Δ PM2.5 | - 2.17 kg/day | |
Δ Total | - 81.8 kg/day |
Project life: 10 yrs | Interest rate: 7% | ||||
CMAQ | NON-CMAQ | TOTAL | METHODOLOGY/ASSUMPTIONS: | ||
---|---|---|---|---|---|
Capital | $788,240 | $197,060 | $985,300 |
Cost-effectiveness was not provided by the project sponsor.
|
|
Adm/oper | $0 | $0 | $0 | ||
Total | $788,240 | $197,060 | $985,300 | ||
Total annualized public cost | $146,900 | ||||
Annual revenues | None | ||||
Net public cost | $985,300 | ||||
Annual private cost | NA | ||||
Total net cost | $985,300 |
NOTE: Assume that these facilities would be demanded all days of the year, consistent with Interstate trucking activity.