CBA and climate change mitigation in transport - an urban case study
Patrizia Fagiani & Paul Riley 29
thOctober 2021
Climate policy evaluation seminars
EEA/ETC-CME
• Technical assistance partnership between EC and the EIB
• Managed by EIB on the basis of a Framework Partnership Agreement with the EC
• Multi-sector, multi-disciplinary advisory services to public sector recipients of EU grants
• Experienced technical experts supporting strategy, programming and project preparation
• Introduction to CBA in transport – context, principles and elements
• Case study in urban transport – metro line
• Focus on GHG emissions assessment in CBA, illustrated by the case study
• Conclusions
Content of the presentation
Planning and CBA in Transport
Good projects need good
strategies/plans behind them - to be in the right ball-park with policy coherence
and synergy
National Transport Strategy
(Integrated/multisector or sectorial)
• e.g. national and international traffic
Local/regional plans (e.g. SUMPS)
• e.g. local and regional traffic
Projects
• Feasibility Study, looking at options and viability
CBA is a tool used in the decision-making
process
Ranking investments for prioritisation according to socio-
economic performance
Comparative options assessment in project studies
Go-no go investment decisions – initial and final
Proof of viability for external funders
I. Avoiding unnecessary traffic /Reducing need for long-distance travel (sustainable development, spatial planning)
• Economic planning, social measures
• Integrated land use and transport planning
II. Shifting traffic to more environmentally friendly modes and decarbonizing all modes
• Transport planning, operations concept and Measure/Project identification/definition
Maximum results when I & II done in parallel coordinated way - holistic analysis of mobility + land-use with reference to GHG emissions
III. Implementing the transport plan
• Project’s detailed aspects –> unlock achievement of the full CC potential at feasibility stage
• Ensuring maximum integration of various complementary measures at project level
• If the planning is poor, this stage does more work
Effective Climate Change Mitigation in Transport
Biggest potential of CC mitigation is at Planning level
Key principles for economic (transport) CBA
• Incremental approach : project Costs minus without project Costs (Creates net Costs and Benefits)
• Discounting future cash flows accounts for opportunity cost : Present Value (PV)
• Economic CBA knows no physical or admin.
borders – e.g. CO2 is global impact
• Key indicators to show viability :
➢ NPV: Net Present Value = PVB-PVC > 0
➢ IRR: % Internal rate of return > Discount rate
➢ BCR or B/C : Benefit to Cost ratio > 1
-3500 -2500 -1500 -500 500 1500 2500 3500 4500 5500 6500
0 1 2 3 4 5 6 7 8 9
0% 3% 5% 8% 10% 15% 20%
Transport CBA typical economic costs and benefits
1. Incremental economic costs All costs of the project, taken at economic cost, typically :
• Investment CAPEX
• Project OPEX (e.g. O&M)
• Asset Replacement
2. Incremental economic benefits/disbenefits Monetised socio-economic benefits, typically
• Travel time
• Other impacted public transport OPEX
• Private vehicle OPEX
• Externalities:
• GHG emissions
• Air pollution
• Safety
• Noise
• Other impacts if justified
3. Residual value of assets or economic cash flows
Critical transport input data
• Traffic model + add-ons :
• Demand forecast with and without project
• Perceived time savings – door to door
• Emissions/noise calculations
• Accident rates
• CAPEX and OPEX with + without project
• Unit monetisation of economic benefits :
• Willingness to pay
• Damage estimation
• Market value minus distortions
• Alternative cost avoidance
Think of CBA as a calculator
Parameter values (e.g., discount rate, value of time)
Investment (&
O&M) costs
Demand,
emissions and operational model outputs
Project net present value
Benefit to cost ratio
Internal rate of return
INPUTS OUTPUTS
• Calculator can work in different ways but is only as good as the inputs
• Need to recognize uncertainty/distortions in the inputs
• Hence the importance of due-diligence and sensitivity testing
Case study: Extension of a metro line - I
• Strategic context:
• The City has a recent Strategic Sustainable Mobility Plan in force.
• At the national level, the country has established a strategic framework for climate related policies.
• Metropolitan transport system:
• Metropolitan area population of around 1.7 m inhabitants, spread over a large area (around 2000 km2), high number of trips/day (average
3.4m)
• Comprehensive public transport network: bus, metro, rail.
• Public transport network carries around 150 mppa.
63%
21%
16%
Mode split
Private transport Public transport Walking
45%
41%
14%
Public transport demand (pass)
Bus Metro Rail
Problem:
Some sections of the metro system in dense and mature central urban areas are reaching capacity, triggering problems of congestion and transport related carbon emissions
• Project objectives:
• Reduce congestion and transport related pollutant emissions in densely populated central areas by improving accessibility to the metro system.
• Contribute to national/local transport decarbonisation policies.
• Project scope
1. Extension of 3 km of metro line, including stations, track infrastructure, traction power supply, traffic management system.
2. Purchase of additional 8 bi-directional, low floor trains to run the additional service.
Case study: Extension of a metro line - II
• CBA input data:
• Project costs (including 1 and 2): EUR 210 m.
• Increased metro service: additional 160k train-km/year, associated OPEX increase at opening year EUR 2.3m.
• Restructuring of competing bus routes as feeding service to metro (-650k v-km/year, EUR -1.6m OPEX).
• Demand forecasts based on transport model.
• Unit costs for socio-economic benefits.
Case study: Extension of a metro line - Results
Discount rate 5% Year 1 2 3 4 5 10 15 20 25 30
Constant prices 2019 VAT-net, EUR m
Socio-economic costs Undiscounted Discounted
Project investment cost -190.0 -170.4 -46.2 -50.7 -45.2 -47.9 - - - - - -
Project O&M costs (incl. replacements) -95.8 -46.1 - - - - -2.3 -6.9 -3.2 -6.9 -3.4 -3.5
Total Economic costs -285.8 -216.5 -46.2 -50.7 -45.2 -47.9 -2.3 -6.9 -3.2 -6.9 -3.4 -3.5
Socio-economic benefits Undiscounted Discounted
Value of time 281.2 130.4 - - - - 8.0 9.2 10.1 11.2 12.5 14.1
Vehicle Operating Costs (individual transport) 95.0 44.0 - - - - 2.6 3.1 3.4 3.8 4.2 4.7
Bus carriers OPEX (reduction) 42.3 20.6 - - - - 1.6 1.6 1.6 1.6 1.6 1.6
Road maintenance cost (reduction) 1.0 0.5 - - - - 0.0 0.0 0.0 0.0 0.0 0.1
Residual value 212.2 56.7 - - - - - - - - - 212.2
Externalities:
Climate Change 26.2 10.7 - - - - 0.2 0.5 0.8 1.1 1.5 2.0
Air pollution 4.2 1.9 - - - - 0.1 0.1 0.1 0.2 0.2 0.2
Accidents 6.0 2.7 - - - - 0.2 0.2 0.2 0.2 0.3 0.3
Noise 5.2 2.4 - - - - 0.1 0.2 0.2 0.2 0.2 0.3
Total Economic benefits 673.4 269.9 - - - - 12.8 15.0 16.5 18.4 20.7 235.5
Net economic benefits (ENPV) 53.4 -46.2 -50.7 -45.2 -47.9 10.5 8.1 13.2 11.5 17.3 232.1
ERR 6.2%
B/C RATIO 2.36
Construction Operations
Socio-economic benefits %
Value of time 48.3%
Vehicle Operating Costs (private transport) 16.3%
Residual value 21.0%
Bus carriers OPEX (reduction) 7.6%
Road maintenance cost (reduction) 0.2%
Externalities:
Climate Change 4.0%
Accidents 1.0%
Noise 0.9%
Air pollution 0.7%
Total 100.0%
Metro: from 73m/year to 81m/year at year 5 (+11%,
modal shift)
Project GHG emissions: basic principles - I
• Absolute/relative/baseline emissions
• Project difference in GHG emissions (relative emissions compared to baseline) triggered by:
a. Project operations:
• Project leads to increase in service production in v-km and related consumption/emissions (e.g.
new line, extension of an existing line) (+)
• Project leads to reduced consumption/emissions per v-km with same service production (e.g.
rolling stock replacement with Low Emission Vehicles, traffic management improvement such as bus lanes, new traffic lights, etc.) (-)
Methodological reference:
EIB Project Carbon Footprint Methodologies
c. Restructuring of services in other PT modes connected to the Project mode lead to increase/reduction of v-km and related
consumption/emission (+/-)
d. Modal shift from private vehicles to PT lead to reduction of consumption/emissions (-)
Project GHG emissions: basic principles - II
Methodological reference:
EIB Project Carbon Footprint Methodologies
Consumption (KWh/veh-km or KWh/train-km or
litre/veh-km)
Carbon content (g CO2e/kWh, g
CO2e/MJ g CO2e/litre)
GHG emission of a transport project for the base year and reference period:
Emissions (t CO2e) in a year
Production/
transport mode (veh-km, pas-km, t-km or train-km)
Emission factor (g CO2e/veh-km)
Source: traffic model, or other tool to forecast
transport demand
Degree of accuracy of this calculation
depends on accuracy of project demand forecasting
Source: project data Source: national guidance, EIB, etc.
Source: national guidance, EIB, etc.
Production/
transport mode (veh-km, pas-km, t-km or train-km)
Production/
transport mode (veh-km, pas-km, t-km or train-km)
Production/
transport mode (veh-km, pas-km, t-km or train-km)
Production/
transport mode (veh-km, pas-km, t-km or train-km)
Project GHG emissions: basic principles - III
• Ref. EIB methodology as in CBR 2021-2025, Annex 5 (Aligned carbon prices)
• Monetisation in CBA through shadow cost of carbon: “cost of carbon required to drive the economy to meet the 1.5˚C global temperature target “ (Paris aligned). It is a measure of
changes in emissions induced by the project. It is not an indication of the required value of any one policy instrument.
Methodological reference:
EIB Group Climate Bank Roadmap 2021-2025(CBR)
Total climate change benefit/cost
EUR / year
Emissions (t CO2e) in a year
Shadow cost of carbon
EUR 2016/tCO2e
Source: EIB CBR 2021-2025
Project GHG emissions: results
NET GHG emissions over 30 years reference period in t CO2e
Project NET -58,487
t CO2e
Metro +1,363 t CO2e
Bus
-9,075 t CO2e
Cars
-50,775 t CO2e
Project NET EUR –10.7 m Input to CBA
(monetisation with shadow cost of carbon)
The project mitigates climate change (=saves
GHG emissions)
Discounted value over reference period
Project GHG emissions: calculations Metro
Methodological reference:
EIB Project Carbon Footprint Methodologies
Consumption KWh/train-km1.2
Grid emission factor g CO2e/kWh273
Metro (at start of operations)
Emissions t CO2e/year52
Production + 160k train-km
Emission factor g CO2/train-km328
Source: project demand
analysis Source: calculated
Source: Project data Source: Table A1.3, EIB Project Carbon Footprint Methodologies
Project GHG emissions: calculations Bus
Methodological reference:
EIB Project Carbon Footprint Methodologies
Emissions t CO2e/year-349
Production -650k bus v-km
Emission factor 1074
TTW g CO2e/v-km
Source: project demand analysis
Bus (at start of operations)
Source: Table A1.3, EIB Project Carbon Footprint Methodologies, average for
standard and articulated buses
Consumption (KWh/veh-km or KWh/train-km or
litre/veh-km)
Carbon content (g CO2/kWh, g
CO2/MJ g CO2/litre)
Project GHG emissions: calculations Road
Methodological reference:
EIB Project Carbon Footprint Methodologies
Emissions -1,820 t CO2e/year
Production -5.5m car v-km
Emission factor 0.277
kg CO2e/v-km
Source: project demand analysis
Private cars (at start of operations)
Source: Table A1.3, EIB Project Carbon Footprint Methodologies, average for
standard and articulated buses
Consumption (KWh/veh-km or KWh/train-km or
litre/veh-km)
Carbon content (g CO2/kWh, g
CO2/MJ g CO2/litre)
Concluding remarks
• CBA is a tool standardly used in many parts of EU to appraise the viability of major transport projects.
• Accuracy of CBA evaluation depends on accuracy of input data (demand forecasting, unit costs of benefits, investment cost estimation, emission factors etc.).
• Climate mitigation impact of a transport project can be reliably quantified and evaluated in the framework of a CBA.
• Impacts of climate policies on relevant input parameters can be factored in, for instance with sensitivity analysis (e.g. evolution of energy mix over time and grid emissions factors).
• GHG emissions and mitigation during the project construction phase (e.g. disruptions, congestion, etc.).
• Climate change mitigation at the level of plans/strategies (e.g. SUMP): assessing impacts, setting targets.
• CBA can be used for assessing economic impacts of adaptation measures as well as mitigation (e.g. JASPERS on-going work with Poland on national road climate change adaptation).
Methodological references
General approach to CBA, sectoral guidance:
• Guide to Cost-Benefit Analysis of Investment Projects. Economic appraisal tool for Cohesion Policy 2014- 2020 (2014) and Economic Appraisal Vademecum 2021-2027 - General Principles and Sector Applications (2021).
• Economic Appraisal Vademecum includes references to several national guidance to CBA.
• Unit values for socio-economic impacts: national values, EU average and country unit costs Handbook on the External Costs of Transport (check Handbook + Annexes).
GHG emissions calculation and monetisation (project, plans)
• EIB Project Carbon Footprint Methodologies
• EIB Group Climate Bank Roadmap 2021-2025 (Annex 5 - Aligned carbon price)
• Webinar on Climate Change Mitigation through Sustainable Urban Mobility Plans (SUMPs) - Events - JASPERS NETWORK
Climate change adaptation in transport
• Climate Change Adaption in Transport Sector - Events - JASPERS NETWORK
For more information:
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Please visit JASPERS website for more information about our activities and projects: http://jaspers.eib.org/
p.riley@eib.org p.fagiani@eib.org