Abstract
A comparative life cycle energy and environmental inventory has been developed for public road transport modes in metropolitan regions in India. The environmental performance of public bus transport (PBT) and intermediate public transport (IPT) modes, viz. taxi and auto-rickshaw, in Mumbai Metropolitan Region has been assessed and compared at off-peak, average and peak levels of vehicle occupancy. Moreover, the environmental performance of vehicles adhering to Bharat Stage (BS) emission norms has been assessed. The inventory captures both vehicle operation (tail-pipe emissions) and non-operation components (e.g. vehicle manufacturing, vehicle maintenance and fuel production). GaBi 6.5 has been used to assess the environmental impact in terms of global warming, acidification, eutrophication, photochemical ozone creation, abiotic depletion potential and primary energy demand. The functional unit of the study was defined as passenger kilometre travelled in 15 years, the service lifetime of the vehicle. The results show that tail-pipe emissions dominate the life cycle environmental impact of PBT (75% of 17.2 g CO2-eq/PKT), taxi (78% of 85 g CO2-eq/PKT) and auto-rickshaw (78% of 78 g CO2-eq/PKT). However, in case of vehicles adhering to BS-VI stringent emission norms, vehicle non-operation components dominate the life cycle environmental impact of public road transport modes. Therefore, vehicle non-operation components should be considered while addressing the environmental performance of public road transport modes. For all three occupancy levels, PBT is environment-friendly compared to IPT modes. However, the break-even point assessment highlights that the bus services should be operated with at least 11 passengers to make its global warming potential equivalent to IPT modes. In case of shared services of the taxi and auto-rickshaw, this equivalency increases to 23 and 29 passengers, respectively. Eventually, this study provides the benchmark that can lead regional transport planners to more informed and prioritized mitigation measures for improving the environmental footprint of public transportation in metropolitan regions in India.
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Abbreviations
- ADP:
-
Abiotic depletion potential
- AP:
-
Acidification potential
- BEB:
-
Battery electric bus
- BEST:
-
Brihanmumbai Electric Supply and Transport
- BS:
-
Bharat Stage emission norms
- CAGR:
-
Compound annual growth rate
- CNG:
-
Compressed natural gas
- CTS:
-
Comprehensive Transport Study
- EP:
-
Eutrophication potential
- GHG:
-
Greenhouse gas
- GWP:
-
Global warming potential
- HC:
-
Hydrocarbons
- HFCB:
-
Hydrogen fuel cells-powered buses
- ICEB:
-
Internal combustion engine bus
- IPT:
-
Intermediate public transport
- LCA:
-
Life cycle assessment
- LCI:
-
Life cycle inventory
- LCIA:
-
Life cycle impact assessment
- MCGM:
-
Municipal Corporation of Greater Mumbai
- MMR:
-
Mumbai Metropolitan Region
- MMRDA:
-
Mumbai Metropolitan Region Development Authority
- NEERI:
-
National Environmental Engineering Research Institute
- ODP:
-
Ozone depletion potential
- OHE:
-
Overhead equipment
- PBT:
-
Public bus transport
- PED:
-
Primary energy demand
- PKT:
-
Passenger kilometre travelled
- PMSD:
-
Preventive maintenance schedule and docking
- POCP:
-
Photochemical ozone creation potential
- VKT:
-
Vehicle kilometre travelled
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Acknowledgements
Authors sincerely thank the management and the staff of the BEST public bus transport for providing the data needed for carrying out the present research study. The first author would like to acknowledge the Ministry of Human Resource Development, Government of India, for providing financial assistance.
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This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.
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Appendices
Appendix A: The general specifications of bus (Ashok Leyland 2016)
Specifications | |
---|---|
Chassis | Flat-ladder steel frame |
Engine | H Series HA135LT3, 6 cylinder |
Engine power | 135 kW (180 HP) @ 2500 rpm |
Maximum torque (Nm) | 550 Nm @ 1500–2100 rpm |
Gearbox | 6 speed ZF-S6-36 (synchromesh) |
Rear axle | Fully floating, single-speed hypoid gear |
Tyre | 10 R 20 radial |
Body | Extruded aluminium |
Length, height and width (mm) | 11,000, 3215 and 2540 |
Kerb weight | |
Diesel bus | 9850 kg |
CNG bus | 10,250 kg |
Passenger capacity | 70 (50 seating + 20 standing) |
Appendix B: Materials required for manufacturing of shell and furnishing interiors of bus
Component | Material | Percentage by mass |
---|---|---|
Shell | ||
Trough floor | Rolled mild steel | 35.2 |
Sidewall and roof | Extruded aluminium | 50.9 |
Floor sheet | Aluminium sheet | 13.9 |
Total | 100 | |
Furnishing interiors | ||
Exterior panel | Aluminium sheet | 11.3 |
Interior panel | Stainless steel sheet | 1.8 |
Aluminium sheet | 7.0 | |
Seats | Mild steel | 10.9 |
LDPE plastic | 8.1 | |
Windows | Glass | 39.8 |
Rubber | 1.8 | |
Handholds | Cast aluminium | 6.5 |
Paint | – | 0.6 |
Front module | Steel channels and sheet | 12.4 |
Total | 100 |
Appendix C: Major components of bus chassis
Component | Percentage by mass |
---|---|
Underframe | 18.7 |
Suspension | 14.9 |
Battery | 1.6 |
Engine | 8.3 |
Propeller | 3.1 |
Radiator | 0.7 |
Gearbox and clutch | 2.7 |
Steering | 1.0 |
Brake drums | 6.2 |
Rims | 4.1 |
Tyres | 2.4 |
Rear axle | 18.1 |
Front axle | 9.4 |
Cylinders | 8.1 |
Grease, oils and paint | 0.6 |
Total | 100 |
Appendix D: Materials required for replacement of furnishing interiors, PMSD and refurbishment of bus
Component | Percentage by mass |
---|---|
Replacement of furnishing interiors | |
Trough floor | 10.2 |
Shell | 8.8 |
Floor sheet | 15.9 |
Battery | 9.1 |
Radiator | 2.1 |
Gearbox (clutch replt.) | 4.4 |
Brake drums | 17.9 |
Tyres | 21.1 |
Axle shaft | 7.7 |
Engine (piston) | 2.9 |
Total | 100 |
PMSD | |
Lubrication | 43.4 |
Paint | 3.7 |
Unit replacement | 52.9 |
Total | 100 |
Refurbishment | |
Exterior panel | 11.3 |
Interior panel | 8.7 |
Seats | 19.0 |
Windows | 41.5 |
Handholds | 6.5 |
Paint | 0.6 |
Front module | 12.4 |
Total | 100 |
Appendix E: General specifications of the auto-rickshaw (Bajaj Auto 2017)
Specifications | |
---|---|
Chassis | Pressed steel sheets and sections |
Engine | CNG 2-stroke |
Engine power | 7.25 kW @ 5500 rpm |
Engine displacement | 198.8 cc |
Maximum torque (Nm) | 14.9 Nm @ 3750 rpm |
Rear axle | Fully floating axle shaft |
Tyre | (4.00-8) 4PR |
Length, height and width (mm) | 2800, 1778 and 1330 mm |
Kerb weight | 421 kg |
Passenger capacity | 3 |
Appendix F: Materials required for manufacturing and maintenance of the taxi and auto-rickshaw
Vehicle component/material | Percentage by mass | |
---|---|---|
Taxi | Auto-rickshaw | |
Manufacturing of vehicle | ||
Steel | 61.0 | 49.9 |
Aluminium | 5.6 | 10.5 |
Copper | 0.7 | 1.0 |
Glass | 3.3 | 4.0 |
Paint | 3.0 | 4.8 |
Plastic | 20.5 | 19.7 |
Tyres | 0.7 | 1.7 |
Battery | 1.2 | 3.3 |
Fluids | 4.1 | 5.2 |
Total | 100 | 100 |
Maintenance of vehicle | ||
Tyre | 10.0 | 10.7 |
Paint | 13.3 | 10.2 |
Battery | 10.3 | 14.2 |
Fluids | 66.4 | 64.9 |
Total | 100 | 100 |
Appendix G: Fuel consumption (in 1000 t) and PKT (in billion) for PBT in 15 years
Years | Diesel | CNG | PKT |
---|---|---|---|
2013–2015 | 63 | 186 | 35 |
2016–2018 | 66 | 175 | 37 |
2019–2021 | 69 | 181 | 40 |
2022–2024 | 68 | 180 | 43 |
2025–2027 | 72 | 180 | 46 |
Total | 337 | 902 | 201 |
Appendix H: Fuel consumption (in 1000 t) and PKT (in billion) for the taxi and auto-rickshaw in 15 years
Year | Taxis | Auto-rickshaws | ||
---|---|---|---|---|
CNG consumption | PKT | CNG consumption | PKT | |
2013–2015 | 122 | 5.2 | 246 | 4.6 |
2016–2018 | 138 | 5.9 | 283 | 5.3 |
2019–2021 | 146 | 6.3 | 300 | 5.7 |
2022–2024 | 153 | 6.7 | 318 | 6.0 |
2025–2027 | 164 | 7.1 | 340 | 6.4 |
Total | 723 | 31.2 | 1487 | 28.0 |
Appendix I: Population of PBT, taxi and auto-rickshaw since 2013–2027
Year | PBT | Taxi | Auto-rickshaw |
---|---|---|---|
2013 | 4327 | 57,095 | 111,591 |
2014 | 4288 | 57,798 | 109,170 |
2015 | 4011 | 65,094 | 128,120 |
2016 | 3921 | 66,396 | 130,811 |
2017 | 4224 | 67,724 | 133,558 |
2018 | 4317 | 69,078 | 136,362 |
2019 | 4412 | 70,460 | 139,226 |
2020 | 4509 | 71,869 | 142,150 |
2021 | 4608 | 73,307 | 145,135 |
2022 | 4710 | 74,773 | 148,183 |
2023 | 4813 | 76,268 | 151,295 |
2024 | 4919 | 77,794 | 154,472 |
2025 | 5027 | 79,349 | 157,716 |
2026 | 5138 | 80,936 | 161,028 |
2027 | 5251 | 82,555 | 164,410 |
Average fleet/annum | 4565 | 71,366 | 140,882 |
Appendix J: Emission factors (g/km) for CNG and diesel buses, CNG fuelled taxi and auto-rickshaw, and sulphur content of diesel fuel (ppm) (CPCB 2011, 2015)
Emission norms | Year of implementation | CO | HC | NOx | CO2 | Sulphur |
---|---|---|---|---|---|---|
Diesel buses | ||||||
BS-II | 2002 | 3.97 | 0.26 | 6.77 | 668.0 | 500 |
BS-III | 2005 | 3.92 | 0.16 | 6.53 | 602.0 | 350 |
BS-IV | 2010 | 2.78 | 0.11 | 4.57 | 553.8 | 50 |
BS-VI | 2020 | 0.56 | 0.03 | 0.52 | 492.9 | 10 |
CNG buses | ||||||
BS-II | 2002 | 3.72 | 3.75 | 6.21 | 806.5 | – |
BS-III | 2005 | 3.72 | 3.75 | 6.21 | 806.5 | – |
BS-IV | 2010 | 2.64 | 2.63 | 4.35 | 733.9 | – |
BS-VI | 2020 | 0.53 | 0.74 | 0.49 | 638.5 | – |
Taxis (CNG fuelled) | ||||||
BS-I | 2000 | 0.60 | 0.36 | 0.74 | 131.2 | – |
BS-II | 2002 | 0.60 | 0.36 | 0.74 | 131.2 | – |
BS-III | 2005 | 0.47 | 0.31 | 0.37 | 126.9 | – |
BS-IV | 2010 | 0.38 | 0.16 | 0.19 | 126.9 | – |
BS-VI | 2020 | 0.38 | 0.16 | 0.15 | 126.9 | – |
Auto-rickshaws (CNG fuelled) | ||||||
BS-I | 2000 | 1.37 | 2.53 | 0.2 | 62.4 | – |
BS-II | 2005 | 1.15 | 1.63 | 0.16 | 71.5 | – |
BS-III | 2010 | 0.77 | 1.09 | 0.11 | 71.5 | – |
BS-IV | 2016 | 0.62 | 0.69 | 0.07 | 71.5 | – |
BS-VI | 2023 | 0.33 | 0.69 | 0.05 | 71.5 | – |
Appendix K: Mileage (km/kg) of CNG and diesel buses, CNG fuelled taxi and auto-rickshaw
Emission norms | Diesel buses | CNG buses | Taxis | Auto-rickshaws |
---|---|---|---|---|
BS-I | – | – | 19.60 | 25.20 |
BS-II | 3.32 | 2.61 | 19.60 | 26.90 |
BS-III | 3.42 | 2.61 | 21.33 | 28.51 |
BS-IV | 3.90 | 2.89 | 22.61 | 29.93 |
BS-VI | 4.13 | 3.16 | 24.86 | 31.72 |
Appendix L: Sensitivity of final results to the fuel consumption (kg/km) of the vehicle
Mode of transport | Variation (%) | GWP (%) | AP (%) | EP (%) | POCP (%) | ODP (%) | ADP (%) | PED (%) |
---|---|---|---|---|---|---|---|---|
PBT | − 10 | − 1.83 | − 3.39 | − 1.17 | − 2.79 | − 5.55 | − 1.51 | − 8.53 |
+10 | 1.83 | 3.39 | 1.17 | 2.79 | 5.55 | 1.51 | 8.53 | |
Taxis | − 10 | − 1.35 | − 4.37 | − 2.14 | − 3.16 | − 7.11 | − 0.46 | − 8.24 |
+10 | 1.35 | 4.37 | 2.14 | 3.16 | 7.11 | 0.46 | 8.24 | |
Auto-rickshaws | − 10 | − 1.81 | − 5.63 | − 3.22 | − 0.98 | − 7.71 | − 0.58 | − 8.16 |
+10 | 1.81 | 5.63 | 3.22 | 0.98 | 7.71 | 0.58 | 8.16 |
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Shinde, A.M., Dikshit, A.K. & Singh, R.K. Comparison of life cycle environmental performance of public road transport modes in metropolitan regions. Clean Techn Environ Policy 21, 605–624 (2019). https://doi.org/10.1007/s10098-018-01661-1
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DOI: https://doi.org/10.1007/s10098-018-01661-1