CTPS CENTRAL TRANSPORTATION PLANNING STAFF Staff to the Boston Region Metropolitan Planning Organization CENTRAL TRANSPORTATION PLANNING STAFF TECHNICAL MEMORANDUM DATE: July 25, 2014 TO: David Mohler, Executive Director, Office of Transportation Planning (MassDOT) FROM: Ben Dowling, Central Transportation Planning Staff (CTPS) RE: Air-Quality Interim Offset Measures Results and Methodology This memorandum presents the results of air-quality interim offset measures (interim offsets) in compliance with the State Implementation Plan (SIP), Transportation Control Measures (TCM), and the methodologies employed to estimate interim offset measures. 1. BACKGROUND The Green Line Extension (GLX) is one of the outstanding TCM commitments currently listed in the SIP. According to title 310 CMR 7.36, the Commonwealth requires this project to be built by December 31, 2014 as an air-quality mitigation measure for the Central Artery/Third Harbor Tunnel (CA/T) project. Construction must be complete and operations must have commenced on the GLX’s two branches—between Lechmere Station and Medford Hillside, and between Lechmere Station and Union Square—by this date in order to meet this legal deadline. However, given the complexity of the project and the length of time required for construction, the Massachusetts Department of Transportation (MassDOT) currently estimates that the Green Line Extension project may not be completed until 2018 to 2020. A provision of 320 CMR 7.36 allows for TCM project delays if interim offset measures are implemented that result in emission reductions in non-methane hydrocarbons (NMHC) carbon monoxide (CO), and nitrogen oxides (NOx) equal to or greater than the emission reductions that would have been achieved had the required GLX project not been delayed. Volatile organic compounds (VOC) have traditionally been deemed to be equivalent to NMHC. The MBTA and previously MassDOT, in consultation with CTPS, developed a list of projects, programs, and measures for interim offsets; and through a process of testing, have identified a suite of interim offsets that realize air-quality improvements, which in 2015, would be greater than what would be achieved by constructing the GLX. State Transportation Building • Ten Park Plaza, Suite 2150 • Boston, MA 02116-3968 • (617) 973-7100 • Fax (617) 973-8855 • TTY (617) 973-7089 • ctps@ctps.org Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 FIGURE 1 Boston Metropolitan Planning Organization Region 1.1 The GLX Emissions “Budget” Before testing interim offset measures, the emissions reductions associated with constructing the GLX alone were established for the forecast year 2015, which is when the GLX originally was scheduled to begin service. The emissions reductions were estimated for the Boston Metropolitan Planning Organization (MPO) region of 101 cities and towns (shown in Figure 1 above).The CTPS travel demand forecast model and spreadsheet tools were used to estimate air-quality benefits that would be realized from auto diversions resulting from construction of the GLX. Based on an analysis from November 2011, the GLX should result in 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 2 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 an average daily reduction in 46,500 vehicle-miles traveled (VMT) in the Boston MPO region, which translates to a GLX “budget” of 13.5 kilograms (kg) of VOC, 22.4 kg of NO x , and 459.2 kg of CO. The stationary source emissions that would be produced by additional Green Line service were not subtracted from the budget. 1.2 Interim Offset Measures In collaboration with CTPS, MassDOT has identified the following measures whose emissions savings collectively would exceed the savings anticipated from completion of the GLX project. 1. Twenty percent increase in off-peak vehicle trips per hour for all Green Line services 2. Twenty percent increase in off-peak vehicle trips per hour for MBTA bus routes 80, 88, 91, 94, and 96 3. Purchase of 142 Ford Fusion Hybrid vehicles for MBTA THE RIDE service to replace older Crown Victoria vehicles 4. Addition of 374 parking spaces at the Salem commuter rail parking garage and 378 more parking spaces at the Beverly commuter rail parking garage Off-Peak Green Line and Bus Schedules A twenty percent increase in off-peak vehicle trips per hour on an average weekday is proposed for all Green Line branches, B, C, D, and E, between 9:00 AM and 3:00 PM and between 6:00 PM and 6:00 AM—Tuesday, Wednesday, and Thursday qualify as average weekdays. (Extended late-night weekend service was not included in this analysis.) A twenty percent increase in the number of vehicle trips per hour also is proposed for five MBTA bus routes, Routes 80, 88, 91, 94 and 96, during the same average weekday off-peak periods. More frequent transit service would cause a mode shift from auto to transit, which in turn would result in air-quality improvement. Table 1 below displays what the potential change would look like in terms of improved headways (minutes) for the Green Line; and Table 2 presents the potential improvement in weekday off-peak bus headways. 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 3 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 TABLE 1 Existing and Proposed Headways (Minutes) for Green Line Branches Green Line Branch Green Line B Branch between Boston College and Government Center Green Line C Branch between Cleveland Circle and North Station Green Line D Branch between Riverside and Government Center Green Line E Branch between Heath Street Lechmere Station Existing Midday Service Headways Proposed Midday Service Headways Existing Night time Service Headways Proposed Night time Service Headways 9.0 7.5 10.0 8.3 10.0 8.3 7.0 5.8 11.0 9.2 10.0 8.3 8.0 6.7 10.0 8.3 TABLE 2 Existing and Proposed Headways (Minutes) for MBTA Bus Routes Route Route 80 between Arlington Center and Lechmere Station−Inbound Route 80 between Arlington Center and Lechmere Station−Outbound Route 88 between Clarendon Hill and Lechmere Station−Inbound Route 88 between Clarendon Hill and Lechmere Station−Outbound Route 91 between Sullivan Square Station and Central Square Cambridge−Inbound Route 91 between Sullivan Square Station and Central Square Cambridge−Outbound Route 94 between Medford Square and Davis Square Station−Inbound Route 94 between Medford Square and Davis Square Station−Outbound Route 96 between Medford Square and Harvard Station−Inbound Route 96 between Medford Square and Harvard Station−Outbound Existing Midday Service Headways Proposed Midday Service Headways Existing Night time Service Headways Proposed Night time Service Headways 33.0 27.3 51.0 42.9 33.0 27.3 40.0 33.3 26.0 21.4 30.0 25.0 28.0 23.1 33.0 27.3 26.0 21.4 60.0 50.0 26.0 21.4 51.0 42.9 45.0 37.5 45.0 31.5 45.0 37.5 40.0 33.3 45.0 37.5 36.0 30.0 45.0 37.5 33.0 27.3 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 4 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 MBTA THE RIDE Fleet Replacement The MBTA’s paratransit service, THE RIDE, currently utilizes Ford Crown Victoria model cars for part of its fleet, and almost exclusively for its fleet that serves the GLX study area (Somerville, Medford, and Cambridge). THE RIDE is proposed to replace 142 of the Ford Crown Victoria vehicles with 142 Ford Fusion Hybrid vehicles, which would be assigned to operate in the study area. The Ford Fusion vehicles use less gasoline, hence resulting in an air-quality benefit. Additional Commuter Rail Parking Spaces The MBTA is building additional parking spaces for both the Salem and the Beverly commuter rail parking garages. The Salem garage will add 374 spaces and the Beverly garage will add 378 parking. Increased parking capacity would induce a mode shift from auto to commuter rail transit, which in turn would result in improved air quality. 2. RESULTS Table 3 below presents the estimated emissions reductions associated with the above-described interim offset measures. These three strategies identified by the MBTA—transit service headway improvements, THE RIDE fleet replacement, and more parking at Beverly and Salem—would collectively exceed the budget, that is the emission reductions anticipated from construction of the GLX project. Note that the stationary-source emissions produced by additional Green Line service were not considered in this analysis. 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 5 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 TABLE 3 Emission Targets and Emissions from Interim Offset Measures Using MOBILE 6.2 Year-2015 Factors Emissions Reductions Goal and Strategies Target Emission Reduction Goal (Emissions Reductions from Auto Diversions from Building GLX) the budget2 Emission Reduction from Added Garage Capacity at Beverly and Salem3,4 Emission Reduction from MBTA THE RIDE Replacements3,5 Emission Reductions from 20% more Vehicles per Hour for All Green Line and Five Selected Bus Routes2,6, Less New Emissions from Bus Routes Emission Reductions Subtotal CO NO X VOC VMT1 459.2 22.4 13.5 46,529 286.0 12.2 8.3 30,732 125.2 5.3 3.6 0 167.2 578.4kg 8.2 25.7kg 4.8 16.8kg 16,899 47,631kg 1VMT reductions include highway diversions from transit improvements and added garage spaces. 2Emissions estimates derived from CTPS travel forecasting model. 3Emission estimates derived from spreadsheet. 4Added parking capacity at Salem (374 additional spaces) and Beverly (378 additional spaces) with an assumed utilization rate of 80%. 5 Ford Crown Victoria vehicles assumed to consume 17 miles per gallon (mpg), Hybrid Ford Fusions assumed to consume 47 mpg. 6Off-peak headway improvement for all MBTA Green Line branches (B,C,D,E) as well as MBTA bus routes 80, 88, 91, 94, and 96. CO = carbon monoxide. GLX = Green Line Extension. Kg = kilograms. MOBILE 6.2 = US Environmental Protection Agency (EPA). Vehicle-emissions modeling software. NOX = nitrogen oxides. VOC = Volatile organic compounds. VMT = vehicle-miles traveled. 2.1 Methodology CTPS used a combination of methodologies to estimate the air-quality savings that would result from implementing the above-listed suite of interim offset measures. The primary estimating tool was the CTPS regional travel demand model, in conjunction with the US Environmental Protection Agency vehicleemissions modeling software MOBILE 6.2; and CTPS used spreadsheet-based models to estimate emissions benefits from fleet replacement and constructing new parking spaces. CTPS Travel Demand Model and MOBILE 6.2 CTPS used its travel demand model in conjunction with MOBILE 6.2 to estimate the air-quality impacts associated with mode shifts from auto to transit based on improvements in Green Line and bus service. 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 6 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 The CTPS model is a four-step trip-based demand model that represents the highway and transit networks in eastern Massachusetts. The model is comprised of 2,727 transportation analysis zones (TAZs) and is capable of estimating mode and route choices. Each of the four steps of the model describes a particular aspect of trip making in eastern Massachusetts. The model generates trips based on land use and demographic data, and distributes those trips according to the relative attractiveness of the TAZs within the model. The model assigns each trip to a particular mode based on the utility of that mode in terms of cost, time, and distance. Finally, the model assigns each trip to a mode-specific network, choosing between various route options based on congestion and travel time information. The routing information derived from the highway assignment portion of the CTPS model is processed by MOBILE 6.2 to estimate mobile emissions from vehicles. Pairing the routing information of CTPS’s regional model with MOBILE software to produce mobile vehicle emissions is a methodology that CTPS has used many times to analyze the mobile emissions of SIP projects. This approach was used for the initial testing of the SIP project package in 2006, the subsequent testing of the SIP project revisions accepted by the EPA (and detailed in the Federal Register of July 31,2008), and for testing new SIP project packages in 2009, 2010, and 2011. Spreadsheet-Based Emissions Estimates Staff used spreadsheet models to estimate the emission benefits as a result of fleet replacement for the MBTA THE RIDE service, and construction of new parking spaces at Beverly and Salem garages. Staff chose this methodology because 1) the CTPS travel demand model does not represent non-fixed-route paratransit service such as THE RIDE, and 2) staff had used spreadsheet models in the past to analyze mobile-emissions impacts of new park-and-ride lots. CTPS obtained from the MBTA the average annual VMT data for THE RIDE vehicles, which was used to calculate daily fuel usage for both existing THE RIDE vehicles as well as the proposed fleet replacement vehicles. 1 CTPS then estimated the daily fuel usage for an average MOBILE 6.2 fleet vehicle. 2 A grams-per-gallon emission factor was then calculated for the MOBILE 6.2 fleet vehicle. This grams-per-gallon factor was then applied to the fuel-usage estimates for the existing and proposed THE RIDE fleet vehicles to estimate the 1 The daily fuel-usage calculation assumed a 17 mpg fuel efficiency for the Ford Crown Victoria and 47 mpg fuel efficiency for the Ford Fusion Hybrid. 2 The average fuel efficiency of a MOBILE 6.2 fleet vehicle is 24.1 mpg. 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 7 of 8 Air-Quality Interim Offset Measures Results and Methodology July 25, 2014 savings that would result from replacing Ford Crown Victoria vehicles with Ford Fusion Hybrid vehicles. To estimate emissions improvements from the additional parking spaces at the Salem and Beverly garages, staff used trip distance and speed data 3 from the regional travel demand model in conjunction with MOBILE 6.2 emissions rates, and assumed a utilization factor of eighty percent for the new parking spaces. Each newly utilized parking space was assumed to capture a single-occupancy vehicle (SOV) trip that otherwise would have driven all the way into downtown Boston from Beverly or Salem. The associated emissions for these previously made SOV trips were summed together to compile emissions reductions for this measure. 3. CONCLUSION The three-pronged package of interim offset strategies—1) increasing off-peak Green Line and bus services, 2) replacing MBTA THE RIDE fleet vehicles, 3) and adding parking spaces at the Beverly and Salem commuter rail parking garages—would provide more emission reductions than would implementing GLX service. SAP/BD/BK/bd 3 CTPS assumed one-way trip lengths of 28.4 miles and 25.7 miles from Beverly to Boston and Salem to Boston, respectively; and assumed average speeds of 23 miles per hour between these origins and destinations. 2014-04-17 Air-Quality Interim Offset Measures MEM BD 7a Page 8 of 8