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Mitigating Environmental Emissions from the Urban Transport System

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Car Ownership in 1998 and 2020 (Units/1000 population) Beijing would have the highest car ownership among the cities (248 in 2020) ... – PowerPoint PPT presentation

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Title: Mitigating Environmental Emissions from the Urban Transport System


1
Mitigating Environmental Emissions from the Urban
Transport System
Ram M. Shrestha S.C. Bhattacharya Nazrul
Islam N. T. Kim Oanh
Asian Regional Research Programme in Energy,
Environment and Climate (ARRPEEC) Asian
Institute of Technology, Thailand
2
Cities Covered
3
City Profile
4
Project Network
AITAsian Institute of Technology, Thailand
DOSTE Department of Science, Technology and
Environment, Vietnam Prof. Nguyen Thien Nhan
ERIEnergy Research Institute, China Dr. Zhou
Dadi IGIDRIndira Gandhi Institute of Development
Research Prof. Jyoti
Parikh ITBInstitut Technologi Bandung, Indonesia

Dr. Tatang H. Soerawidjaja SATMPSociety for the
Advancement of Technology in the Philippines,
Philippines
Dr. Joy V. Abrenica
5
Study Objectives
  • To analyze the demand for urban transport
    services and associated energy demand and
    environmental emissions
  • To analyze and select the technical options for
    energy efficiency improvement and mitigation of
    GHGs and other harmful emissions from the urban
    transport system and
  • To identify and rank the barriers to the
    introduction of selected technical options to
    mitigate environmental emissions from the urban
    transport system.

6
Travel Demand, Energy Demand and Associated
Environmental Emissions
7
Projection of Travel Demand
GDP Growth Rate for BAU Projection ()
GDP Growth Rate for Alternative Scenarios
Alternative Scenario 1 is 1.5 times BAU GDP
growth rate Alternative Scenario 2 is 1.25 times
BAU GDP growth rate Alternative Scenario 3 is
0.75 times BAU GDP growth rate Alternative
Scenario 4 is 0.5 times BAU GDP growth rate
8
Demand for Transport Services (p-km) BAU
Projection
  • Annual average growth rate of demand for
    transport services would be in the range of 3.3
    (Beijing) to 7.3 (HCMC) during 1998-2020.

9
Vehicle share (of the total vehicles) in Bandung
and Beijing
Bandung
Beijing
10
Vehicle share (of the total vehicles) in Delhi
and Hangzhou
Delhi
Hangzhou
11
Vehicle share (of the total vehicles) in HCMC and
Jakarta
HCMC
Jakarta
12
Vehicle share (of the total vehicles) in Manila
and Mumbai
Manila
Mumbai
13
Change in Model Mix (2005-2020)
14
Car Ownership in 1998 and 2020 (Units/1000
population)
  • Beijing would have the highest car ownership
    among the cities (248 in 2020). However, the
    number would be still less than that in OECD
    countries.

15
Bus Ownership in 1998 and 2020 (Units/1000
population)
  • Beijing would have the lowest bus ownership
    during the planning horizon.

16
Two-wheeler Ownership in 1998 and 2020
(Units/1000 population)
  • 2-wheeler ownership would be relatively low in
    Beijing, Hangzhou and Manila

17
Annual Average Growth Rate of Total Transport
Energy Demand (1998-2020) BAU Projection
  • AAGR is above 5 in all Cities

18
Share of CNG in Total Energy Demand in 2005 and
2020 ()
  • The share of cleaner fuels, i.e. CNG, would
    increase in the future especially in the Indian
    cities of Mumbai and Delhi followed by Hangzhou
    Beijing and Jakarta.

19
Average Annual Growth Rate of CO2 Emission During
1998-2020 ()
  • Average annual growth rate in the range of 3.1
    (in Jakarta) to 12 (in Manila).
  • Total transport CO2 emissions from the eight
    cities 53.8 million tonnes in 2020.

20
Ratio of CO2 in 2020 to the Base Year (1998)
Emission BAU Projection
21
Modal Share in CO2 Emissions in Bandung and
Beijing
Bandung
Beijing
22
Modal Share in CO2 Emissions in Delhi and Hangzhou
Delhi
Hangzhou
23
Modal Share in CO2 Emissions in HCMC and Jakarta
HCMC
Jakarta
24
Modal Share in CO2 Emissions in Manila and Mumbai
Manila
Mumbai
25
Changes in Modal Share in CO2 Emission
26
Ratio of Local Pollutants in 2020 to the Base
Year (1998) Emission BAU Projection
  • Among the cities, Mumbai would have the lower
    ratio due to the higher share of buses, use of
    CNG and penetration of 4-stroke 2-wheelers.
  • HCMC would have the higher ratio due to the
    higher share of 2-wheelers.

27
Technical Options for CO2 Emission Mitigation
28
Technology Options Considered for Emission
Mitigation
29
Least Cost CO2 Mitigation Options
ADOAdditive diesel oil
30
Least Cost CO2 Mitigation Options Contd..
  • MRTS is cost effective at 20, 40, 25 and 40
    CO2 reduction target in Bandung, Beijing,
    Hangzhou and HCMC respectively.

31
Impact of CO2 Mitigation Target on Emissions of
Local Pollutants
  • Local emission reduction objectives could still
    be served by focusing on CO2 emission reductions.
  • In the case of Beijing and Hangzhou, the
    introduction of efficient diesel car would reduce
    the emission level of CO, NOx and NMVOC. However,
    it would increase the emission of TSP.
  • TSP emission in Delhi would be reduced by 13
    under 10 CO2 reduction target.
  • In Mumbai. TSP emission would be reduced 14 to
    10.
  • In the case of Manila, CO emissions would fall by
    32 at 10 CO2 reduction.

32
Selected Technical Options to Mitigate CO2
Emission
  • Bandung LPG buses, bio-diesel buses and
    bio- ethanol buses
  • Beijing CNG buses, diesel cars and MRTS
  • Delhi CNG buses, CNG cars and 4-stroke
    2-wheelers
  • Jakarta CNG buses, LPG buses, bio-diesel
    buses and bio-ethanol buses
  • Hangzhou CNG buses, diesel cars and MRTS
  • HCMC MRT, Diesel bus
  • Manila CNG buses, alco-diesel buses and (coconut
    methyl ester) CME buses
  • Mumbai CNG cars, CNG 3-wheelers and BOV
    3- wheelers

33
Barriers to the Adoption of Efficient Options
34
Barriers to the Adoption of Efficient Options
  • Barriers varies from
  • Country to country
  • City to City
  • Technology to Technology
  • Technology specific barriers for each city were
    identified and the analysis of barriers are
    carried out using Analytic Hierarchy Process
    (AHP).

35
Barriers to the Adoption of CNG Bus
36
Barriers to the Adoption of Bio-fuel Buses in
Manila
37
Barriers to the Adoption of CNG Cars
38
Barriers to the Adoption of MRTS
39
Barriers to the Adoption of 4-Stroke 2-wheelers
in Delhi
40
  • Thank you

41
Additional Information
42
Project Approach
Project Development (AIT, NRIs, Regional
Experts/Policy Makers)
Review of Methodology (NRIs)
Development of Methodology (AIT)
Country Case Studies (NRIs)
Review of Case Studies (AIT)
Cross-Country Synthesis (AIT)
Publications (AIT, NRIs)
Dissemination (NRIs, AIT)
43
Methodology
Population
GDP
Emission Factor
Energy Intensity
Econometric Model
Vehicle Stocks
LEAP Model
Spread Sheet Model
Transport Demand (p-km)
Energy Demand
Utilization, Occupancy Rate
Emission
44
Modal Mix in 2005 and 2020 under the BAU Case,
45
Structure of the Projected Energy Demand in 2005
and 2020
  • The share of cleaner fuels, i.e. CNG, would
    increase in the future especially in the Indian
    cities of Mumbai and Delhi followed by the
    Chinese cities of Beijing and Hangzhou.

46
Ratio of Environmental Emission in 2020 to the
Base Year Emission
47
Flow Chart of Methodology
Candidate Options
Costs
Vehicle Penetration Rate Fuel Availability Emissio
n target
Transport Demand Data
Vehicle-Mix Model
Vehicle-km by mode
Vehicular Mix
Emission Factor
Total Cost
Total Emissions
48
Least-Cost Vehicle Options Bandung and Jakarta
  • In the base case, the shares of gasoline vehicles
    in total passenger transport service supplied in
    both cities would be decreasing while that of
    additive diesel oil (ADO) and LPG would be
    increasing
  • At 20 reduction target, LPG and bio-diesel
    vehicles (car, minibus, truck, and bus), and MRT
    would be cost effective options to meet the CO2
    reduction target in Bandung. The share of
    bio-diesel vehicles at 20 target would be 24.6
    in 2020.
  • In the case of Jakarta, LPG car would be selected
    at 10 reduction target and bio-diesel vehicles
    (car, bus, jeep, minibus, bus, pick up and truck)
    and MRT would be selected at 40 reduction
    target. The share of bio-diesel vehicles and MRT
    at 40 reduction target would be 42.6 and 4.8
    respectively in 2020 in Jakarta.

49
Least-Cost Vehicle Options Contd.. Beijing and
Hangzhou
  • Under Base Case, the shares of gasoline car and
    diesel buses on total passenger kilometer
    supplied would increase in both cities.
  • To achieve a reduction of 10 CO2 emission,
    gasoline cars needs to be replaced by diesel
    cars.
  • At higher emission reduction target of 40 for
    Beijing and 25 for Hangzhou, the share of MRTS
    would increase substantially.
  • The shares of diesel-buses in total passenger
    transport service supplied in different years
    would reduce significantly when the emission
    reduction target is increased from 30 to 40 for
    Beijing and 20 to 25 for Hangzhou.

50
Least-Cost Vehicle Options Contd.. Delhi and
Mumbai
  • Among the technologies considered, CNG buses
    would supply highest share of the transport
    services in passenger-km in Delhi while diesel
    buses would supply highest share of the transport
    services in Mumbai.
  • In Delhi, at higher emission reduction target
    level of 25, diesel buses would replace the
    gasoline and diesel cars.
  • In the case of Mumbai, CNG buses would replace
    diesel buses at the emission reduction target of
    5 while at higher emission reduction target of
    30 battery operated 3-wheelers (2.5 in 2020)
    would replace the diesel 3-wheelers.

51
Least-Cost Vehicle Options Contd..
  • Manila
  • Alco-diesel bus, alco-diesel trucks and cars with
    catalytic converters would be cost effective
    technologies at the lower CO2 emission mitigation
    target of 5 in Manila.
  • As the emission mitigation target is increased,
    the share of these three technologies would be
    increased, while the share of diesel buses and
    diesel trucks would decrease. At 15 reduction
    target, 99 of the trucks would be using
    alco-diesel in 2020.
  • HCMC
  • Vans would be a cost effective technology at
    lower CO2 emission reduction target of 3 in
    HCMC. At the emission reduction target of 3, van
    would replace diesel buses.
  • At higher emission reduction targets of 12,
    electric 2-wheelers would also be cost effective
    technology. Its share would be 27 at 12 CO2
    reduction target

52
Marginal Cost of CO2 Abatement (MAC), US/tonne
of CO2
  • MAC would be relatively high for Manila (178
    /tonne of CO2 at 5 reduction target) and
    relatively low for HCMC (0.5 /tonne of CO2 at 6
    reduction target).
  • The MAC values are relatively low in Beijing,
    Delhi and Mumbai.

53
Three important Barriers in Beijing and Hangzhou
for the Selected Options
54
Three important Barriers in Delhi and Mumbai for
the Selected Options
55
Three important Barriers in HCMC for the
Selected Options
56
Three important Barriers in Manila for the
Selected Options
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