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TOWARDS
INTEGRATED APPROACH
Containment of vehicular pollution
requires an integrated approach, the essential components of which include the
following :
Optimisation of traffic flow and improvement in traffic management (e.g. area traffic control system, no-traffic zone, green corridors, removal of encroachment on roads, regulation of construction activities and digging of roads).
Fuel quality improvement (e.g. benzene and aromatics in petrol, reformulated gasoline with oxygenates/additives, reduction of sulphur in diesel).
Improvement in vehicle technology (e.g. restriction on the 2 stroke engines, emission warranty, on-board diagnostic system).
According to an estimate made by RITES, a modal split of 70-75% infavour of public transport needs to be planned for the city of Delhi. Presently, the modal share of public transport (Bus) is 62 percent. Along with the increase in number of buses, the passenger capacity should also be increased and the engines should conform to urban design. The existing circular ring railway network also requires to be improved. These measures will meet the immediate requirements since the mass rapid transport system (MRTS) will take some years to materialise.
Traffic Management System
Well planned Traffic management system results in better mobility level on road by providing higher journey speeds and reduced delay at intersection thereby bringing significant reduction in fuel consumption and emission. Automatic traffic control, signal optimisation, tidal flow and removal of encroachments are among the important components of traffic management system. This will reduce the congestion and consequently pollution. Frequent digging of roads and construction work also leads to congestion and pollution, which can be minimised through proper coordination with traffic police.
Comprehensive Inspection and Certification System
It is a system to reduce the pollution by requiring regular inspection and maintenance of motor vehicles already plying on roads. It identifies those in-use vehicles that need maintenance and repair because they pollute more than the new vehicles. The system helps in reducing the air pollution. Such system is widely used in other countries and it has been possible to reduce about 30-40% of pollution loads by proper inspection and maintenance of vehicles. Such facilities for thorough inspection and maintenance of vehicles are required in different parts of the country.
Phasing Out of Grossly Polluted Vehicles
Pre-1990 vehicles emit more than ten times pollutants than the vehicles meeting Euro I norms (India 2000 norms). In Delhi, more than 15 year old commercial vehicles are not allowed to ply on roads. Similarly, de-registration of all older vehicles should be made effective so that the grossly polluting vehicles are phased out.
Fuel Quality Improvement
Benzene and aromatics in petrol
Due to high level of benzene in atmosphere, benzene content of gasoline needs to be reduced to 1% (v/v) or lower as in other countries. With the reduction of benzene in gasoline (<1%) it is possible to achieve significant reduction in benzene emission from exhaust. Benzene and PAH emission also depend upon the aromatic content of gasoline. Therefore, in addition to reduction of benzene, it is also necessary to reduce the aromatic content in petrol.
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Benzene is a proven carcinogen. The most significant health effects from a short or long term exposure to benzene are haemotoxicity, immunotoxicity, neurotoxicity and carcinogenicity.
Benzene in the crude oil is present at levels upto 4 g/l. Its concentration varies from one source to another. In India, Benzene content in motor gasoline varies from 3-5% by weight.
Although Benzene is also emitted from industrial activity, about 80 to 85% of benzene in atmosphere comes from automobiles. In heavy traffic area, upto 40 to 50 ug/m3 of Benzene in the ambient air has been observed.
About 80-90% of the Benzene from automobile sector is emitted from the exhaust. About 10-20% are from evaporation while 3-6% are from transportation, delivery and distribution at petrol stations. Most part of benzene in gasoline is oxidised during combustion while some part are emitted through exhaust. Some portion of benzene is formed from the other aromatics by process of dealkylation during combustion. On an European vehicle fuelled with gasoline containing 3% by wt of benzene and 30% by wt of other aromatics, it has been found that 44% of the benzene survived combustion and 56% was created during combustion from other aromatics.
Average benzene emission of 32 mg/km out of 1130 mg/km of HC has been measured on American automobiles equipped with catalytic converter in FTP cycle. European automobiles without catalytic converter emit about 270 mg/km of benzene in ECE cycle.
Benzene exhaust emission ( B.E.E.) can be estimated by following equation, BEE mg/km = [1.884 + (0.949 x % Benzene) x 0.113 + (% aromatics - % of Benzene)] x 1.609
By this equation, it can be estimated that if benzene control is reduced from 5% to 3% there will be 35% reduction in the exhaust emission of Benzene.
In USA, Europe and
Japan, benzene content in motor gasoline has been reduced to 1%. In India, the
benzene content of 5% has been prescribed which will be reduced to 3% from year
2000. |
Sulphur Content in Diesel
Sulphur in diesel has direct effect on SO2 and particulate emission and indirectly on other pollutants due to its poisoning effect on catalytic converter. In European countries, sulphur content in diesel has been reduced to 0.05% from 1996 and it will be further reduced to 0.005 from the year 2000.
Reformulated gasoline
Reformulated gasoline with the use of oxygenates and additives etc. help reducing pollution load from on-road vehicles. According to a study commissioned by CPCB, 3-5% ethanol can be used in petrol without affecting the engine performance and with the attendent benefits in terms of emission control.
Tightening of emission norms
The emission norms effective from 2005 need to be further tightened to offset the increase of pollution load due to exponential growth of vehicles. It is time to bridge the gap between Euro norms and Indian norms. Euro IV norms for petrol vehicles and diesel passenger cars and Euro III norms for heavy diesel vehicles may be a preferred target for 2005.
Improvement in Vehicles
In India, majority of vehicles is of two stroke engines. Although the two stroke engine technology for 2 or 3 - wheelers has been upgraded to some extent there is not much improvement in control of hydrocarbons and particulate (due to combustion of lube oil). Hence, it is necessary to consider as to whether 2-stroke technology should be replaced by 4-stroke technology for reducing the emission specially in terms of hydrocarbons and particulate matter apart from increased fuel efficiency in 4-stroke engines.
On Board Diagnostic System
The On Board Diagnostic System (OBD) electronically records the fault and their causes in combination with various Diagnostic Strategies to enable vehicle owner / driver to take corrective action. This is one of the requirements of emission regulation in USA and it will be followed in Europe from year 2000 which will be a part of Euro III norm for 2000.
Checking Fuel Adulteration
Adulteration of fuel plays a major role in emission of pollutants from on roads vehicles. Effective measures are required to prevent adulteration of fuel.
Evaporative Emission Control
To
minimise evaporation losses of fuel and consequent pollution, adequate preventive
steps need to be taken during storage, loading, unloading and distribution. Vapour
recovery system in the filling stations is yet another important measure for reducing
evaporative losses.
Table 5 Indian and EURO Norms for Petrol Driven Passenger Cars
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| | | INDIA | INDIA | EURO-II | INDIA | EURO-III2 | EURO-IV2 | ||
| CO g/km | 14.3-27.1 |
| 8.68-12.4 | 4.34-6.20 | 2.2 | 2.72 | 2.3 | 1.0 | |
| HC g/km | 2.0-2.9 |
| - | - | - | 0.20 | 0.1 | ||
| NOx g/km | - |
| - | - | - | 0.15 | 0.08 | ||
| HC+NOx g/km | - |
| 3.4-4.36 | 1.5-2.18 | 0.57 | 0.97 | |||
2. In case of Euro III &
Euro IV COP = type approved norms
Table
6 Indian and EURO norms for Diesel driven Passenger cars
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| INDIA | EURO-I | INDIA | EURO-II | INDIA | EURO-III | |
| CO g/km | 14.0 (g/KWH) | 2.72 | 5.0 - 9.0 | 1.00 | 2.72-6.90 | 0.6 |
| HC g/km | 3.5 (g/KWH) | - | ||||
| NOx g/km | 18.0 (g/KWH) | |||||
| HC+NOx g/km | - | 0.97(IDI) 1.36 (DI) | 2.0-4.0 | 0.7 | 0.97 - 1.70 | 0.56 |
| PM g/km | - | 0.14(IDI) 0.19 (DI) | 0.08 | 0.14-0.25 | 0.05 | |
Table 7 Indian and EURO norms for Diesel Light duty Vehicles < 3.5 tonnes
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| INDIA | EURO-I | INDIA | EURO-II |
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| CO | 14.0 g/KWH | 2.72-6.902 g/km | 11.21 g/km or 50-9.03 g/km | 1.0
to 1.52 g/km
| 4.51 g/KWH or 2.75-6.903 g/km |
| HC | 3.51 g/KWH | - | 2.41 g/KWH or HC+NOx norms | - | 1.11 g/KWH or HC+NOx Norms |
| NOx
HC+NOx | 18
g/KWH - | -
0.97-1.72 (g/km) | 14.41
g/KWH or 2.0 to 4.03 g/km | -
0.7 - 1.32
| 8.01g/KWH
or 0.97-1.703 g/km |
| PM | - | 0.14-.7
(g/km) | - | - | 0.61
KWH or 0.14 - 0.25 g/km3 |
2 = EDC + EUDC
3 = Indian Driving Cycle
Table 8 Indian and EURO norms for Diesel Vehicles > 3.5 tonnes
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| INDIA | EURO-I | INDIA | EURO-II | INDIA | EURO-III | |
| CO g/KWH | 14.0 | 4.5 | 11.2 | 4.00 | 4.5 | 2.1 |
| HC g/KWH | 3.5 | 1.10 | 2.4 | 1.10 | 1.10 | 0.66 |
| NOx g/KWH | 18.0 | 8.00 | 14.4 | 7.00 | 8.00 | 5.0 |
| PM>85 g/KWH | - | 0.36 | - | 0.15 | 0.36 | 0.1 |
| PM<85 g/KWH | - | 0.61 | - | 0.15 | 0.61 | 0.1 |
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| | Complete removal of leaded petrol in NCT Delhi | 01.09.1998 | Ministry of Petroleum & Natural Gas | Done |
| | Phasing out of 15 years old commercial vehicles | 31.12.1998 | Transport Department, Govt. of NCT-Delhi. | Done |
| | Installation of pre-mixed 2T oil dispensers in petrol filling stations. | 31.12.1998 | Ministry of Petroleum & Natural Gas | Done |
| | Expansion of CNG Supply Network (from 9 to 80 stations) | 31.03.2000 | Gas Authority of India Limited | Pending issues relating to allotment of land for the CNG stations has been sorted out through intervention of the Authority with the concerned land owning agencies. |
| | Setting up of two independent fuel testing laboratories for checking the quality of the fuel. | 01.06.1999 | Ministry of Petroleum & Natural Gas and Association of Indian Automobile Manufacturers (AIAM) | One laboratory is being set up at NOIDA and the other will be at Gurgaon. |
| | Replacement of all pre-1990 autos and taxis with new vehicles using clean fuel | 31.03.2000 | Transport Department, Govt. of NCT-Delhi. | Action due. |
| | No 8 years old bus is to ply except on CNG or other clean fuel. | 01.04.2000 | Transport Department, Govt. of NCT-Delhi. | Action due. Work plan not received. |
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| All buses to switch over to CNG instead of diesel | 31.03.2001 | Transport Department, Govt. of NCT-Delhi. | Action due. |
| | The bus fleet to be augmented to 10,000 | 01.04.2001 | Transport Department, Govt. of NCT-Delhi | Action due. |
| | New ISBTs to be set up at entry points in north and south-west to avoid congestion and pollution due to entry of inter-state buses. | 31.03.2000 | Transport Department, Govt. of NCT-Delhi. | Action due. |
| | Automated inspection and certification facilities to be set up for commercial vehicles in the first phase. | 31.03.2000 | Transport Department, Govt. of NCT-Delhi. | Action due. As of now, only one station is in operation. |
| | Augmentation of air quality monitoring network. | 31.03.2000 | Central Pollution Control Board, Ministry of Environment & Forests and Delhi Pollution Control Committee, Govt. of NCT-Delhi. | CPCB has prepared a comprehensive proposal. DPCC has been asked to set up monitoring facilities in addition to the monitoring stations set up by CPCB. Besides the criteria pollutants, facilities for monitoring of additional parameters like benzene, RSPM, Poly aromatics and Ozone have been set up by CPCB. |
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The method of measuring exhaust emission rates from motor vehicles is determined by statutory test procedure, the objective being to establish the mass of each exhaust component emitted during the test. The mass is computed from the measured concentration of each pollutant in the known exhaust gas volume. Exhaust species are generated when the vehicle is operated on a chasis dynamometer according to certain driving cycle which are designated to simulate driving condition in urban traffic. To be able to check the application of the regulation in measurement conditions that are reproducible as possible it is necessary to adopt these test procedures. The Indian driving cycle has been developed by IIP, Dehradun and ARAI Pune.
Different countries used different test cycles. A comparision of different test cycle for passenger cars is given in Table 10. So far unfortunately the countries have not been unanimous in adopting universally applicable procedures and several types of test cycles are in use, for which no correlation exists for converting from one to another.
In
Europe, Extra urban cycle (EUDC) was introduced under pressure from Netherland
which showed that over 70% of European mileage was driven at more than 70 km/hr,
conditions that lead to 40% of HC emission and 80% of NOx emission. |
Table 10 Comparision of Different Driving Cycles for Passengers Cars
| Parmeters | Units | ECE-15 cycle | ECE- 15+EUDC cycle | FTP – 75 cycle | Japan 11 mode cycle | Japan 10.15 mode | Indian driving cycle (IDC) |
| Total time | Seconds | 780 | 1220 | 2477 | 120 | 660 | 648 |
| Distance covered | Km | 4.052 | 11.007 | 17.87 | 1.021 | 4.16 | 3.948 |
| Average Speed | Km/hr | 18.7 | 33.6 | 34.1 | 30.6 | 22.7 | 21.93 |
| Max. Speed | Km/hr | 50 | 120 | 91.2 | 60 | 70 | 42 |
| Idling | % time | 35.4 | 31 | 17.3 | 21.7 | 31.4 | 14.81 |
| Acceleration | % time | 21.6 | 33.7 | 34.2 | 38.89 | ||
| Constant Speed | % time | 29.3 | 20.5 | 13.3 | 12.04 | ||
| Deceleration | % time | 13.8 | 26.5 | 30.8 | 34.26 | ||
| Implementation in countries | Earlier by EEC Countries, Malasiya | Most of EEC countries | USA, California, Canada, Australia, Norway, Sweden, Brazil, S. Koria | Earlier by Japan | Japan | India |