George Noel and Dr. Roger Wayson

Slides:



Advertisements
Similar presentations
Statistical evaluation of model uncertainties in Copert III, by I. Kioutsioukis & S. Tarantola (JRC, I)
Advertisements

Getting on the MOVES: Using Dynameq and the US EPA MOVES Model to Measure the Air Pollution Emissions TRPC – Smart Corridors Project Chris Breiland Fehr.
Determining the Free-Flow Speeds in a Regional Travel Demand Model based on the Highway Capacity Manual Chao Wang Joseph Huegy Institute for Transportation.
Case Study 2 New York State Route 146 Corridor. This case study is about a Traffic Impact Assessment for a proposed site development in Clifton Park,
1 Travel Model Application for Highway Vehicle Emission Estimation Ho-Chuan Chen, Ph.D., P.E. King County Department of Transportation Seattle, Washington.
2/27/06Michael Dixon1 CE 578 Highway Traffic Operations Lecture 16: Freeways Basic Sections.
Chapter 241 Chapter 25: Analysis of Arterial Performance Know how arterial LOS is defined Be able to determine arterial classes Know how to determine arterial.
A Heavy-Duty Vehicle Visual Classification Scheme: Heavy-Duty Vehicle Reclassification Method for Mobile Source Emissions Inventory Development Prepared.
The Composition of the Vehicle Fleet in the Metropolitan Washington Region Results of Applying a Vehicle Identification Number (VIN) Decoder to July 1,
Transportation leadership you can trust. presented to TRB Planning Applications Conference presented by Vamsee Modugula and Maren Outwater Cambridge Systematics,
COG DTP/DEP Staff Eulalie Lucas and Erin Morrow DTP Sunil Kumar DEP Testing of EPA’S MOVES Model Travel Management Subcommittee May 26, 2009 MOVES: Motor.
Unrestricted © Siemens AG 2015 All rights reserved.Answers for infrastructure and cities. Data collection for city baseline and projections for Helsinki.
BPAC. “Congestion management is the application of strategies to improve transportation system performance and reliability by reducing the adverse impacts.
4-1 Model Input Dollar Value  Dollar value of time  Accident costs  Fuel costs  Emission costs.
Transit Priority Strategies for Multiple Routes under Headway-based Operations Shandong University, China & University of Maryland at College Park, USA.
Mike Johnsen, FMCSA, sponsor Doug Lee, Volpe Center, PI Garrett Hagemann, Economist Kent Hymel, Economist Adam Klauber, Environmental Engr George Noel,
Igor Trpevski University of St. Cyril and Methodius Skopje,
David B. Roden, Senior Consulting Manager Analysis of Transportation Projects in Northern Virginia TRB Transportation Planning Applications Conference.
Major Transportation Corridor Studies Using an EMME/2 Travel Demand Forecasting Model: The Trans-Lake Washington Study Carlos Espindola, Youssef Dehghani.
1 Potential User Benefits and Costs of Rising Fuel Prices in the Puget Sound Region TRB Planning Applications Conference May 18, 2009 By Maren Outwater.
CO 2 Emissions from Cars, Trucks & Buses in the Metropolitan Washington Region Presentation to the National Capital Region Transportation Planning Board.
Introduction to Transport
It’s Easy to Quantify Changes in GHG Emissions from Cars and Light Trucks – Right? Presented to: SACOG Panel Discussion April 16, 2009 Presented by: Bob.
FY Commuter Connections TERM Analysis Results TBP Technical Committee December 5, 2014 ITEM #8.
EPA’s Development, Community and Environment Division: T ools for Evaluating Smart Growth and Climate Change February 28, 2002 Ilana Preuss.
Transportation leadership you can trust. presented to Safety Data Analysis Tools Workshop presented by Krista Jeannotte Cambridge Systematics, Inc. March.
Assessing the Marginal Cost of Congestion for Vehicle Fleets Using Passive GPS Data Nick Wood, TTI Randall Guensler, Georgia Tech Presented at the 13 th.
Missoula Air Quality Conformity Analysis Required by Federal and Montana Clean Air Act – Transportation-specific air quality requirements enacted in Federal.
1 Session IV: Onroad Mobile Sources Laurel Driver US EPA.
1 Air Pollution Automobile Emissions: An Overview Emissions from an individual car
Considerations in using NEMS (and other input…) Alison Bailie Associate Scientist December 2003.
I/M Model Program Characterization I/M Solutions Schaumberg, IL May 5-8,
Kanok Boriboonsomsin, Guoyuan Wu, Peng Hao, and Matthew Barth
PM Control Strategies for Mobile Sources
CMAQ Emissions Calculator Toolkit Gina Solman – Volpe Center
Induced Travel: Definition, Forecasting Process, and A Case Study in the Metropolitan Washington Region A Briefing Paper for the National Capital Region.
EPA Phase II for Greenhouse Gas Emissions
Red Line Customer Capacity Update
The TPB What Would It Take Scenario: Meeting Regional Climate Change Mitigation Goals for the Mobile Sector Presentation to MWAQC CAC June 15, 2009 Monica.
Overview of FHWA CMAQ & System Performance Measures
Network Attributes Calculator
EXPOSURE OF CHILDREN TO ULTRAFINE PARTICLES AROUND AN URBAN INTERSECTION S Kaur, M J Nieuwenhuijsen & R Colvile Environmental Processes & Systems Research.
Southern California Transportation Outlook to the year 2040
PROJECT LOCATION Project begins at Garden Lane (East of I-4)
Andrey Khlystov and Dave Campbell
Modelling Sustainable Urban Transport
Applied Technology and Traffic Analysis Program(ATTAP) MIDCAP & MUID
Assessing Emissions Impacts of Automated Vehicles
Macroscopic Speed Characteristics
a view from the Automotive Industry
The Transportation & Air Quality Research Group
Utilizing Traffic Simulation Tools with MOVES and AERMOD
CTR Performance 2015/2016 Cycle Aggregate Report
Irvine Traffic Research & Control Center (ITRAC)
ITTS FEAT Tool Methodology Review ITTS Member States Paula Dowell, PhD
ACEC of Arizona & ADOT Liaison Todd A. Emery, PE
Preparation of Fine Particulate Emissions Inventories
Ventura County Traffic Model (VCTM) VCTC Update
George Noel and Dr. Roger Wayson
Problem 5: Interstate 87 Interchange
אמצעי מדיניות להפחתת זיהום אוויר במרכזי הערים
Problem 3: Shenendehowa Campus
Impacts of hydrogen pathways vs
School of Civil Engineering
Sensitivity Analysis Update
Highway Engineering CE 431
Methodology and Results
Presented By: George Noel – Volpe Mark Glaze - FHWA 1/13/2014
Statistics.
Transportation Engineering Calculating Signal Delay February 23, 2011
Presentation transcript:

George Noel and Dr. Roger Wayson MOVES Project Level Sensitivity Analysis George Noel and Dr. Roger Wayson 107th Air & Waste Management Association Annual Conference and Exhibition Paper # 33650 June 26th, 2014 The National Transportation Systems Center U.S. Department of Transportation Office of the Secretary of Transportation John A. Volpe National Transportation Systems Center Advancing transportation innovation for the public good

Overview Background Analysis Results Findings Questions Age Distribution Fleet Mixture Average Speed compared to user defined Operating Mode Distributions Results Findings Questions

Background Project sponsored by Federal Highway Administration (FHWA) MOVES Regional Level Sensitivity Analysis Report released in December of 2012 MOVES Project Level Sensitivity Analysis Was a follow up analysis to the Regional Level Sensitivity Analysis Parameters chosen to be analyzed for the Project Level analysis were based on some of the finings from the Regional Level Analysis Final Report completed in March Highlight the Regional level analysis and how it was presented at A&WMA in 2012 in San Antonio. Also the Regional level was used to determine the input parameters we analyzed for the project level analysis

Age Distribution Age Distribution was analyzed for the Regional Level Sensitivity Analysis The Project Level Analysis applied more meaningful variations Reached out to the Metropolitan Washington Council of Governments (MWCOG) to obtain data. Analyzed multiple vehicle types Passenger Cars Transit Buses Single Unit Trucks Combination Trucks When Age Distribution was analyzed in the Regional Sensitivity we used arbitrary values to test the senstivity. For the project level we wanted to be more realistic. We reached out to an MPO to get real world data. We used that real world data to obtain more realistic vairaions

Age Distribution MWCOG provided data for 2005, 2008, and 2011 The data showed the fleet aging throughout the years

Passenger Car Age Distribution Trends More variable for newer model years Less variable for latter years Age Groupings were based on these observed trends Point out the blue line being the national default

Passenger Car Age Distribution Groupings Passenger Cars were put into five age groups Five Scenarios were analyzed Scenario 1 has the least amount of variation based upon the observed data Scenario 5 has the highest amount of variation base upon the observed data Vehicle Age Range Baseline Age Fractions Scenario 1 Scenario 2 Scenario 3 Scenario 4 Scenario 5 0-3 years 0.32 -5% -10% -20% -30% -45% 4-7 years 0.22 -2% -7.50% 8-12 years 0.26 +5% +10% +20% +30% +50% 13-17 years 0.14 +4% +8% +15% 18-30 years 0.06 +2.5% +7.5% +25% Average Vehicle Age 7.48 7.68 7.86 8.21 8.53 9.24 Also mention that we are aging the fleet in each scenario. Also highlight that these ranges are realistic. Even in scenario 5 we did observed some model years have that much variation at the high end.

Passenger Car Age Distribution Results Source Type Pollutant Case Average Age Emission Rate (gram/vehicle-mile) Percent Change Passenger Car CO Baseline 7.48 1.484 - Scenario 1 7.68 1.516 2.15% Scenario 2 7.86 1.548 4.14% Scenario 3 8.21 1.604 7.49% Scenario 4 8.53 1.653 10.24% Scenario 5 9.24 1.776 16.47% NOX 0.2929 0.3017 2.91% 0.3104 5.63% 0.3246 9.76% 0.3367 12.99% 0.3700 20.84% VOC 0.0398 0.0409 2.88% 0.0421 5.56% 0.0439 9.51% 0.0455 12.62% 0.0502 20.78% PM2.5 0.0067 0.0068 1.16% 0.0069 2.27% 0.0070 4.01% 0.0071 0.0075 9.94% Shows that the emissions rates increase as the fleet gets older and more vairable. Once again highlight that these ranges are observed from an actual MPO. Shows how much the fleet can change for the same area in just a few years. Also, highlight that is shows how important it is to get the most recent age distribution. For certain analyses it may be important to forecast possible aging of the fleet.

Fleet Mix Analyzed five cases to determine how sensitive fleet can be a specific MOVES link The five cases include Geographic area comparisons of fleet mix(Georgia Tech provided data) Passenger Car to Passenger Truck ratio Percent Truck Mix Truck Type Mix Transit Bus Mix We will only show the passenger Car to Passenger Truck Ratio Case. Mentioned Ga. Tech for the Geographic area case.

Passenger Car to Passenger Truck Ratio Passengers Car and Passenger Truck CO emission rates are significantly different This analysis tested how sensitive this ratio is and the impact on emission rates from MOVES First Bullet: Passenger Trucks are much higher than passenger cars in MOVES.

Passenger Car to Passenger Truck Ratio Results Pollutant Description Emission Rate (gram/vehicle-mile) Percent Change CO Baseline_Highway 2.5700 - Passenger Cars +5%/Passenger Trucks -5% 2.4692 -3.92% Passenger Cars +10%/Passenger Trucks -10% 2.3684 -7.84% Passenger Cars +20%/Passenger Trucks -20% 2.1668 -15.69% Passenger Cars -5%/Passenger Trucks +5% 2.6708 3.92% Passenger Cars -10%/Passenger Trucks +10% 2.7716 7.84% Passenger Cars -20%/Passenger Trucks +20% 2.9733 15.69% NOX 1.2006 1.1727 -2.33% 1.1447 -4.65% 1.0889 -9.31% 1.2285 2.33% 1.2565 4.65% 1.3123 9.31% The closer you are to a 50/50 split the higher the CO and NOX rates will be. The main take away is that if you can increase your proportion of passenger trucks your CO and NOX rates can go up by a significant amount. It will be important to classify these vehicles appropriately.

Average Speed and Operating Mode Distribution Comparison Compared utilizing average speed for a link to a user defined operating mode distribution When using average speed with MOVES, default drive schedules are applied Highway Capacity Manual (HCM) based drive schedules Georgia Tech provided operating mode distributions During the first main and sub bullet explain the how the average speed works and the different options that can be used. Average Speed Drive Schedule Operating Mode Distribution. Remind everyone that everything turns into an operating mode distribution. Mention Ga. Tech here again and how important they were for this portion of the analysis.

Example of MOVES Default Drive Schedules Explain that the default drive schedules might not represent the type of link we are tying to model 1029 – Red line in the chart – represents an average speed of 31.02 mph. There are speeds all the way up to 64-65 mph in the drive schedule. This might not represent an arterial you want to model.

Intersection Analysis 25 mph, 35 mph, 45 mph approach speeds LOS B,D, and E Consisted of approach, queue, and departure (acceleration) links 35 mph Scenario Intersection Data Approach Speed (mph) LOS Signal Cycle Length (seconds) Yellow Time (seconds) Green Time (seconds) Red Time (seconds) Vehicle Headway (seconds) Decel Rate (mph/s) Acc Rate (mph/s) Volume per Cycle 35 B 55 4 10 41 14 -5 3 D 95 23 68 E 9 11 This is an example of the detail we come up with to develop these scenarios. We used this information in conjunction with the kinematic equations. We developed our own drive schedules and using the VSP calculation converted them into Operating Mode Distributions.

Operating Mode Distributions 35 mph Intersection Scenario – Queue Links LOS D Operating Mode Distributions For the Queue link LOS D in the 35 mph scenario Blue is MOVES average speed Red is HCM generated Green is Georgia Tech provided.

Intersection Results Link Description LinkID Modeled Average Speed (mph) Level of Service CO Emission Rate (gram/veh-mile) CO % Difference Compared to Average Speed NOX Emission Rate (gram/veh-mile) NOX % Difference Compared to Average Speed Intersection Queue Link Average Speed 111 15.94 LOS B 3.066 - 0.366 Intersection Queue Link HCM 11 1.858 -39.38% 0.2254 -38.41% Intersection Queue Link GATech 211 1.53 -50.09% 0.1875 -48.77% 114 13.04 LOS D 3.273 0.3754 14 2.477 -24.32% 0.3274 -12.77% 214 1.871 -42.85% 0.2292 -38.95% 117 13.81 LOS E 3.209 0.3725 17 2.391 -25.49% 0.3144 -15.59% 217 1.766 -44.97% 0.2164 -41.91% Large variations compared to average speed for the queue segment. CO and NOX results. Very important finding for getting a good representative operating mode distribution for the segment being modeled.

Some of the Findings Variations in Age Distribution from year to year can impact emission rates Passenger Car to Passenger Truck Ratio is important The proportion of combination trucks in your fleet mix has a large influence on composite emission rates Although a small sample size from this analysis: There is large variation in emissions rates when comparing average speed to the HCM based operating mode distribution and/or Georgia Tech operating mode distribution. Tell them more are highlighted in the report.

Acknowledgments Michael Claggett and Paul Heishman from FHWA Ann Xu, Randy Guensler, and Vetri Elango from Georgia Tech The late Ron Kirby from the Metropolitan Washington Council of Governments (MWCOG)

Questions?