Emission Factor Toolkit (EFTv5.2c) User Guide January 2013

Similar documents
Public Complaints Key Indicators (PCKI) - Public Complaints Data November 2017 (covering period November 2016 to October 2017) Version 1 Summary

Road Transport Emission Factors and Fleet Data Information from the National Atmospheric Emissions Inventory

Freedom of Information Request Reference No: I note you seek access to the following information:

Put yourself in the driving seat

RoadPeace. TfL Roads Policing Enforcement Statistics 2015 RoadPeace analysis. April Key points. The national charity for road crash victims

NewcastleGateshead Low Emission Zone Feasibility Study

LAEI 2013 Non-road transport emission estimates

L O W E M I S S I O N CITY

Emissions source apportionment Putney High Street

Deriving Background Concentrations of NOx and NO 2 April 2016 Update

ONE YEAR ON: THE IMPACTS OF THE LONDON CONGESTION CHARGING SCHEME ON VEHICLE EMISSIONS

London Buses Emissions Reduction. Finn Coyle Environmental Manager, Transport Emissions

Low Emission Strategies Sussex-DEFRA Seminar, March 2011

Introduction to the Ultra Low Emission Zone

Deriving Background Concentrations of NOx and NO 2 for Use with CURED V3A

Low Emission Vehicle Policy Development in London

Overview of Changes Introduced by EFT V7.0 and by CURED V2A

CAROLINE PIDGEON MBE AM J A N U A R Y

Modelling LEZ and Demand Management measures in the City of York using Detailed Traffic-Emission Tools

Environmental Impact of Taxis Is there a Business Case for Hybrids. Dr James Tate, Institute for Transport Studies

Ealing Car Club Study

COPERT 4 v7.1. Dimitrios Gkatzoflias Chariton Kouridis Giorgos Mellios Leon Ntziachristos

Improving the air we breathe A Clean Air Zone for Birmingham. Birmingham City Council

Evaluating opportunities for soot-free, low-carbon bus fleets in Brazil: São Paulo case study

Atmosphere and Local Environment. Trends in NO X /NO 2 emissions and ambient measurements in the UK

Project Appraisal Guidelines for National Roads Unit National Parameters Values Sheet

VEHICLE EMISSIONS. ITF-SEDEMA workshop in Mexico City Norbert Ligterink

Vehicle emissions prediction model (VEPM 5.3) user guide. Version 2.0, April 2018

Proposals for an Ultra Low Emission Zone

Congestion Charging in London

NOx Emissions from Modern Diesel Vehicles. Dr Ben Marner

VEPM 5.3. Vehicle Emission Prediction Model update: Technical report. Prepared for NZ Transport Agency. April 2017

The Low Emissions Toolkit

Poppy Lyle Greater London Authority

French - IFSTTAR activities

The Low Emission Zone

Trends in air pollution and emissions projections

EMISSION FACTORS FROM EMISSION MEASUREMENTS. VERSIT+ methodology Norbert Ligterink

METHODOLOGIES FOR CALCULATING ROAD TRAFFIC EMISSIONS IN MILAN

Vehicle Emissions Remote Sensing Preliminary results from Measurements on A472 Hafod Road

A comparison of the impacts of Euro 6 diesel passenger cars and zero-emission vehicles on urban air quality compliance

San Joaquin Valley APCD

Evaluation of the suitability to European conditions of the WNTE control zone concept as set out in the OCE GTR

NGC Emissions Calculator Methodology (United Kingdom)

RHA NOx Emission Assessment 2018

Institute for Transport Studies FACULTY OF ENVIRONMENT. Remote Sensing Vehicle Emissions

INDEX What is CNG? Advantages CNG / LNG network Experience Daily Natural Power Eurocargo Natural Power Stralis Hi-Street and Hi-Road Natural Power

Documentation for Passenger Vehicle Processes

NSW Fleet Forecast for Tunnel Ventilation Design: 2016 to 2040

Bus and coach transport for greening mobility

Innovation in London. Policy approaches to mobility management and sustainable travel. Transport for London

Low Emission Zones in Germany

Gas natural Combustible alternativo para automoción

Energy in transports: quantification of impacts

USE OF VEHICLE FLEET DATA FOR ON-ROAD MOBILE SOURCES EMISSION INVENTORIES

NGC Emissions Calculator Methodology (United Kingdom)

TEST PROCEDURE. BAB Motorway Test Cycle

2012 Air Emissions Inventory

Some Comments on Air Quality Nitrogen Oxide

BUS SERVICES IN CHAMBERLAYNE ROAD NW10

Department for Transport. Transport Analysis Guidance (TAG) Unit Values of Time and Operating Costs

Official Journal L 076, 22/03/2003 P

Eric Ling, Committee on Climate Change Secretariat

Methods to Find the Cost-Effectiveness of Funding Air Quality Projects

Upgrading City Buses to Reduce NOx Emissions

CIVITAS SMILE Introduction of a Low Emission Zone in Norwich. Andy Watt Head of City Development Services

Volume 8, ISSN (Online), Published at:

Work Package 4 Examining the emission reductions from changes in the Private Car Fleet and Public Transport Bus Fleet

The growing phenomenon of the CCTV Smart Car 1

GOVERNMENT CLEAN AIR STRATEGY

What do you need to know about Congestion Charging Fleet Auto Pay?

Newcastle/Gateshead Low Emission Zone Feasibility Study

REAL WORLD DRIVING. Fuel Efficiency & Emissions Testing. Prepared for the Australian Automobile Association

Module 8: Nonroad Mobile Source Emission Inventory Development

Business incentives Low carbon transition

Application of EMME3 and Transportation Tomorrow Survey (TTS) for Estimation of Zonal Time Varying Population Density Distribution in

Methodological tool Baseline emissions for modal shift measures in urban passenger transport

NORMAN HARDING CORPORATE FLEET MANAGER LONDON BOROUGH OF HACKNEY

The Largest Low Emission Zone of Europe: Traffic and Air Quality in London

Zorik Pirveysian, Air Quality Policy and Management Division Manager Policy and Planning Department

Clean vehicles & fuels in the EU

TfL Managing London s Roads. Glynn Barton, Head of RSM Outcomes Delivery, Transport for London. Copyright 2016 TRL Ltd

Singapore and Manila March Successful Deployment of Low Emission Vehicles Industry Viewpoint

Use of Big Data for Vehicle Kilometres. Noreen Dorgan CSO Ireland April 2018

Key Outcomes. The key outcomes of the preliminary study:

AIR QUALITY DETERIORATION IN TEHRAN DUE TO MOTORCYCLES

Dialogue of the South on Clean Air and Sustainable Mobility

Impact of Delhi s CNG Program on Air Quality

Successfully switching to CNG buses in Verona

SNAP CODES:

Medium term effects of London s low emission zone

VEHICLE FLEET CHARACTERIZATION STUDY OF THE CITY OF MADRID Year General Direction of Sustainability and Mobility Planning

MAN Buses & Coaches Comparing drivetrain technologies. Robert Staimer, NGVA Brussels, July 09th, 2014

Examining the benefits of using bio-cng in urban bus operations

The role of biomethane transport fuel Update from the Department for Transport

Evaluation of the effectiveness of measures to improve quality air applied in Northern and Central Europe. Claire Holman, Roy Harrison, Xavier Querol

New methodological elements. EMISIA workshop, 27 May 2016, Lyon, France

GUIDE FOR VAN DRIVERS

Assessment of emissions from transport sector in Delhi

Traffic Emission modelling

Transcription:

Emission Factor Toolkit (EFTv5.2c) User Guide January 2013 This guidance refers to the Emission Factor Toolkit (EFT) (v5.2c) released January 2013 through the LAQM Support Helpdesk. The Emission Factor Toolkit allows users to calculate emissions of nitrogen oxides (NO x ), Particulate Matter PM 10 and PM 2.5, hydrocarbons, and carbon dioxide (CO 2 ). A Quick Start Guide sheet is available in the EFT to provide some basic definitions and guidance to complement this more detailed User Guide. This document also contains the Process Map of calculations used to generate results. In order to use the EFTv5.2c you must enable macros in your MS Excel security settings before opening the Spreadsheet. When using Excel 2010 this can be found under: DEVELOPER > MACRO SECURITY > MACRO SETTINGS. For previous versions of Excel this can be found in: TOOLS > MACROS > SECURITY LEVEL > MEDIUM. This document contains the following sections: Basic Operation of the EFTv5.2c; Advance Options in the EFTv5.2c; o Euro Compositions; o Alternative Technologies; and EFT Process Map. 1

Basic Operation of the EFTv5.2c 1. Go to the Input Data sheet using the tabs at the bottom of the workbook. 2. In the Select Pollutants box, select the pollutants for which you require emissions information (NO x uses the COPERT4 v8.1 NO x emission factors and supersede the NO x (TRL) emission factors used in EFTv4). 3. In the Select Outputs box, select your required output from the following categories: Air Quality Modelling Emission Rates PM by Source Annual Link Emissions Source Apportionment Breakdown by Vehicle g/km/s emission rates for each road link g/km emission rates for each road link Proportion of particulate emissions from Exhaust, Brake, Tyre and Abrasion (output generated in an additional tab) Emissions of each pollutant per year for each road link (requires a specified link length) % emission from each vehicle type specified on each road link All output options above are provided for each vehicle type on the road link for the following vehicle categories: Petrol cars, diesel cars, petrol LGVs, diesel LGVs, Rigid HGVs, Artic HGVs, Buses and Coaches, and Motorcycles. If the user specifies the Basic Split option, then the emissions are based entirely on the vehicle fleet composition embedded in the EFT. 2

4. Enter Area using drop-down box. This incorporates area specific information from detailed traffic surveys on fleet composition. The areas available are: o England; o Scotland; o Wales; o Northern Ireland; and o London. 5. Enter the Year for which you wish to predict emissions. Years 2008 to 2030 can be selected. 6. Select one of the following Traffic Formats which matches the available data, using the drop-down box: Basic Split Detailed Option 1 Detailed Option 2 Detailed Option 3 Assumes standard fleet composition for the selected road type, with specified %HDV (HGV and buses/coaches) Allows user input by %Car, %Taxi, %LGV, %HGV, %Bus and Coach, %Motorcycle Allows additional specification of HGV into rigid and articulated Allows additional specification of cars into Petrol and Diesel Note 1: Taxi refers to Black Cabs and can only be entered when London is selected in Area Type. 7. Under the header SourceID enter a name for each of your roads (this can be anything you like). You can enter up to 10,000 road links. 3

8. Under the Road Type header, select a road type from the following list: Urban (Not London) Rural (Not London) Motorway (Not London) London Central 1 London Inner 2 London Outer 3 London Motorway Use this option for roads that are not motorways or similarly fast flowing roads in urban areas (by the DfT definition of an urban area with a population of 10,000 or more) Use this option for roads that are not motorways or similarly fast flowing roads outside urban areas Use this option for motorways and fast dual carriageways Use this option for roads in Central London as defined in the London Atmospheric Emissions Inventory (LAEI) Use this option for roads in Inner London as defined in the LAEI Use this option for roads in Outer London as defined in the LAEI Use this option for motorways and fast dual carriageways in Greater London 9. Under Traffic Flow header, enter the number of vehicles on each road. This will usually be vehicles per day (i.e. AADT flow) but can be any time period up to one day (24-hours). 10. Enter the percentage of the total traffic flow of each vehicle type in the categories depending on the Traffic Format selected. If a vehicle category has no vehicles a 0 must be entered. 1 Roughly corresponds to the original boundary of the Central London Congestion Charging Zone (CCZ implemented in February 2003) and is made up of some of the 1 km 2 grids in the London boroughs of Camden, City of London, Islington, Lambeth, Southwark, Tower Hamlets, and Westminster. 2 Consists of some of the 1 km 2 grids in the London boroughs of Camden, Greenwich, Hackney, Hammersmith and Fulham, Haringey, Barnet, Islington, Kensington and Chelsea, Lambeth, Lewisham, Newham, Southwark, Tower Hamlets, Wandsworth, Westminster, Waltham Forest and Redbridge. 3 Consists of some of the 1 km 2 grids in the London boroughs of Enfield, Barking and Dagenham, Barnet, Bexley, Brent, Bromley, Croydon, Ealing, Harrow, Havering, Hillingdon, Hounslow, Kingston-upon-Thames, Merton, Richmond-upon-Thames, Redbridge, Sutton and Waltham Forest. 4

11. Under the Speed (kph) header, enter the average traffic speed on each road (this should relate to the same time period as the Traffic Flow). This can be between 5kph and 140kph. Where the maximum possible speed for a vehicle defined within emissions functions is below the specified speed, the emissions for the maximum speed of that vehicle will be used. Similarly, where the speed entered is below the minimum speed allowed for that vehicle type, the minimum will be assumed. 12. Under the No of Hours header, enter the time period used for the Traffic Flow (for example, if you entered the number of vehicles per day, this will be 24; but if you entered the number of vehicles per hour, this will be 1). 13. Under the Link Length (km) enter the length of each road link. This is only required if the Annual Link Emissions option has been specified. 14. Should the user wish to display the contribution of each Euro category within the emissions for each vehicle class, the Output Euro Compositions option in the Advanced Options box of the Input Data sheet should be selected. These results will be displayed in a separate output tab. 15. If you require the output to be saved in a new workbook, tick the box, and specify a file name next to File Name. The file will be generated in the directory where you have saved the EFT. 16. Click on Run EFT to run the calculations, or Clear Input Data to recommence data entry. 17. You will automatically be taken to the Output sheet of the workbook, where the requested emission information for each source name and pollutant will be displayed. 5

Advanced Options in the EFTv5.2 The following Advanced Options have been added to the EFT to provide greater flexibility in input options so that the user can more accurately represent the situation in their locality or test the impact of proposed intervention measures. It is recommended that these features are only used by experienced air quality modellers. If users are not comfortable with the underlying methodology 4 and limitations of these features, their use is not recommended as results may be misinterpreted. Further information can be obtained from the LAQM Helpdesk (laqm.helpdesk@uk.bureauveritas.com, 0800 032 7953). Euro Compositions Should the user wish to specify the Euro classification of the fleet used in the emission calculations to more accurately reflect local conditions or test intervention measures under consideration, then the following procedure should be followed: 1. In the Advanced Options box of the Input Data sheet select Euro Compositions. 2. Go to the UserEuro sheet that is generated. This displays all of the Euro class splits that will be used in the calculation of emission factors. The proportions in each box add up to 1 (100%). The boxes with headings in blue display the proportions built into the toolkit based on the selected Road Type, Area and Year. 3. The boxes with headings in orange will be used in the calculations if the Euro Compositions option has been selected. These can be automatically populated with the standard Euro class information. 4 Scaling factors used for Alternative Technology vehicles will shortly be available from http://naei.defra.gov.uk/ 6

4. In order to change the Euro proportions in any specific vehicle class, the user can amend the proportions in the box with orange headings. The proportions in each box should always add up to 1 (100%) or 0 (0%). The text adjacent to each box confirms whether the proportions add up to 1. IMPORTANT: Unlike Fleet Data entered into the Input Data worksheet, which can be based on survey data, such as Automatic Traffic Counts (ATC), or Automatic Number Plate Recognition counts (ANPR), Euro Class proportions entered into the UserEuro worksheet must be based on activity data (i.e. vehicle kilometres, veh-km). 5. The Euro compositions incorporated within the EFT are different for NO x and PM (and other pollutants) as in some cases the standards apply differ, therefore user entered fleet data should be added in both sets of tables where necessary. Note 2: Emission reductions that can be achieved by retrofitting HGVs with Selective Catalytic Reduction (SCR) systems have not been confirmed at this stage. As a result, if any proportion information is input next to boxes ending in SCRRF, the standard emission factor for the Euro class of that HGV will be used. It is intended that the EFT will be updated as and when further data becomes available on the likely effectiveness of such systems. Alternative Technologies Should the user wish to predict the impact on emissions of introducing vehicles with alternative technologies to the traffic fleet under consideration, then the following procedure should be followed: 1. In the Advanced Options box of the Input Data sheet select Alternative Technologies. 2. Select Alternative Technologies in the drop-down box adjacent to Traffic Format. 7

3. Under Traffic Flow header, enter the number of vehicles on each road. This will usually be vehicles per day (i.e. AADT flow) but can be any time period up to one day (24-hours). 4. Enter the percentage of the total traffic flow of each vehicle type in all categories. If a vehicle category has no vehicles a 0 must be entered. The following additional vehicle categories are available: Petrol HEV Cars Petrol PHEV Cars BEV Cars FCEV Cars E85 Bioethanol Cars LPG Cars Petrol HEV LGV Petrol PHEV LGV BEV LGV FCEV LGV E85 Bioethanol LGV LPG LGV B100 Rigid HGV B100 Artic HGV B100 Bus CNG Bus Biomethane Bus Biogas Bus Hybrid Bus FCEV Bus B100 Coach Petrol Hybrid Electric Vehicle Cars Petrol Plug-in Hybrid Electric Vehicle Cars Battery Electric Vehicle Cars Fuel Cell Electric Vehicle Cars Bioethanol Cars Liquefied Petroleum Gas Cars Petrol Hybrid Electric Vehicle LGVs Petrol Plug-in Hybrid Electric Vehicle LGVs Battery Electric Vehicle LGVs Fuel Cell Electric Vehicle LGVs Bioethanol LGVs Liquefied Petroleum Gas LGVs B100 Biodiesel Rigid HGVs B100 Biodiesel Articulated HGVs B100 Biodiesel Buses Compressed Natural Gas Buses Biomethane Buses Biogas Buses Hybrid Buses Fuel Cell Electric Vehicle Buses B100 Biodiesel Coaches 8

Note 3: Standard vehicle classes will have to be reduced to create space for Alternative Technology Vehicles. For example, if the % Bus and Coach in the baseline fleet is 5% and the user wishes to test the impact of converting half of these to B100 Biodiesel Buses, 2.5 should be entered under % Bus and Coach and % B100 Bus. Note 4: The London bus fleet included by default in the EFT includes alternative technologies as shown in the UserEuro sheet when selecting the Euro Compositions option. The standard % Bus and Coach proportion will already include a certain proportion of fuel cell (e.g. 0.1% in 2015) and hybrid buses (e.g. 8.5% in 2015), so the final proportions of each additional Alternative Technology should be calculated accordingly. In this example, entering a figure of 5 in the % Hybrid Bus box will mean that calculations assume an overall hybrid bus percentage of 13.5% of the fleet. 5. Enter the Speed (kph), No of Hours and Link Length (km) details as normal. 9

EFTv5 Process Map Initial Input Parameters Year (2008 2030) Speed (5 140kph) Vehicle Emissions (g/km) Per vehicle type based on vehicle classification per speed Emission Degradation, Mileage and Fuel Per year per vehicle type. Emission degradation NOx only, Mileage NOx and HC, Fuel CO2 and PM Constants Per vehicle type based on speed, fuel usage, Euro composition, Degradation Brake and Tyre Wear and Abrasion PM10 & PM2.5 only Emission (g/km) Expressed per Euro Classification per vehicle group as individual vehicle, including failed catalysts per Euro class Weighted Emissions Per vehicle per road type Adjusted Brake and Tyre Wear and Abrasion PM10 & PM2.5 only Euro Classification Per vehicle per Euro class per year PM2.5 Conversion Factors Emission (g/km) Expressed per year per vehicle group Traffic Data Flow, Hours and Vehicle Proportions Road Type Composition Urban (Not London) Rural (Not London) Motorway (Not London) London Central London Inner London Outer London Motorway Per vehicle per year Pollutant Emissions (g/km) & (g/km/s) NOx, PM10, PM2.5, HC, CO2 Total emission per traffic data entry g/km as above divided by time Link Length (km) Annual Emissions g/km/s x Link Length x (3600x8760) 10