RESEARCH


National Policy, Standards, Legislation & Enforcement

PHASING-OUT LEADED PETROL IN DELHI

Dr. S.K. Tyagi & Dr. B. Sengupta

Introduction

Air quality in Indian metropolitan cities is deteriorating very fast primarily due to Vehicular pollution. Vehicular emission is a deadly cocktail of poisonous gases and particles which affects the human beings, vegetation, agriculture and buildings. Petrol driven vehicles are recognized today as a major source of lead pollution in urban environment. In view of the rise in the number of vehicles on roads, there is an increase in lead emission from petrol driven vehicles. Realizing the gravity of problems, CPCB carried out systematic study1&2 over a period of January, 1984 to April, 1987 in the city of Delhi, in order to study the lead contamination of the roadside eco-system. Special attention was paid towards curtailment of emission coming out of the vehicular exhaust, introduction of unleaded petrol in four metro cities, a country-wide wide phase-out programme for reduction of lead in petrol and sulphur in diesel. Alongside, tightening of vehicular exhaust emission norms, effective inspection and maintenance, improvement in public transport and abatement of traffic management system are advocated by CPCB. Subsequently, CPCB is monitoring lead in atmospheric environment of Delhi over years since 1989 on monthly basis. However, concentrations of particle lead as monitored by CPCB are generally showing an increasing trend.

Hazard of Lead Pollution

Vehicular pollution accounts for about 70% of air pollution in India’s metropolitan cities. This figure was higher for Delhi, most of which is in close proximity to the breathing zone. Airborne lead is typically present in vehicular exhaust emission in the form of particles, which have diameter of less than 1 p.m. and therefore may be transported to large distance with a life time in the atmosphere between one and four weeks depending on climatic factors. Inhalation of leaded aerosol from vehicular exhaust is a potential source of body burden of lead. Pulmonary route of lead exposure may account 40% of blood lead as 40% of inhaled lead is supposed to be absorbed. However, 90% of the ingested lead is excreted out. In human beings all organs contain some quantity of lead but almost 90% is stored in the skeleton, while blood contains only 1% of lead. In the blood almost 99% lead is associated with porphyrins. Exposure to moderately low level of lead may produce abnormalities in the synthesis of porphyrins inhibiting delta amino laevulinic acid (d-ALA) dehyrogenage. As a consequence, blocking of haemoglobin occurs which result in increased blood and urine level of d-ALA, which is also a diagnostic test for acute and chronic lead poisoning.

Impact of Removing Leading from Petrol on Blood Lead Levels

Low blood lead levels were found in Tokyo, a city where all petrol has been free of lead since 1976. In contrast, petrol in Mexico City contained high lead content, and people in Mexico City had high level of lead in blood. In USA, a decline of petrol lead of 55% was accompanied by a fall of 37% in blood lead level. These results are similar in the UK, where the lead reduction in gasoline from 0.4 to 0.15 g/1 made in 1986 was followed by a 50% reduction in atmospheric lead levels and a significant reduction in blood lead levels.

Impact on Air Environment due to Phase-out of Lead from Gasoline in India

Introduction of lead free petrol in Delhi from. September l, 1998 has shown a reduction in ambient particulate lead concentration in Delhi to the tune of 60%, as monitored by CPCB. As a case study conducted by CPCB on impact of unleaded petrol on urban environment is reflected from the table given below:

Enrichment of Lead in Fine Particulate Matter

A short-term preliminary study conducted by CPCB has shown enrichment of lead in respirable particulate matter at BSZ Marg (ITO Intersection), Delhi. Monthly mean value of respirable particulate lead ranged between 339 and 581 ng/m', slightly higher than the lead level in total suspended particulate matter (SPM). However, this finding needs further investigation.

Vehicular Pollution Control Strategies

The menace posed by the vehicular population is further reinforced by sheer statistics. Two-wheelers have grown in number accounting for 78.8% of all vehicles in 1995 against 8.8% in 1951. The total number of vehicles in Delhi (27.0 lacs or 2,700,000) was more than the number of vehicles in cities of Mumbai (7.24 lacs), Calcutta (5.61 lacs) and Chennai (8-12 lacs) in 1995. The total number of vehicles has grown up to more than 30 lacs as on March 31, 1998.

Emissions from gasoline (4-stroke spark ignited engine) vehicles are mainly from three sources, i) crankcase blowby, which accounts for 20% all emission from vehicles; ii) evaporative emissions, which accounts for another 20% of all emissions from vehicles; and iii) exhaust emission (through tail pipe) which accounts for 60% of all emissions of a 4-stroke spark ignited vehicle. In case of 2-stroke gasoline engines, 3% emissions are due to evaporation while rest is from exhaust.

Therefore, exhaust emissions deserve special emphasis because it accounts for a larger chunk of all pollution from gasoline based vehicles. Keeping this in mind, CPCB has drawn an action plan at three stages: i) pre-combustion stage, where the quality of the fuel can be upgraded; ii) combustion stage, where engine modification and maintenance are required; and ii) post combustion stage, where exhaust treatment devices, like catalytic converters, are required.

Improvement in Fuel Quality

Improving the quality of fuel goes a long way in the abatement of vehicular pollution. With this in mind, specification of motor gasoline (petrol) and diesel recommended by CPCB has been notified under the Environment (Protection) Act, 1986, which limits lead levels to 0.15 gm/litre which was implemented in four metros namely Mumbai. Delhi, Calcutta and Chennai from June, 1994. Unleaded petrol (0.013 gm/litre lead) was introduced from April, 1995 on partial basis in 4 metros and in full in Delhi from September l, 1998. Benzene levels have been limited to 5% by volume in the gasoline which are to be further reduced to 3% in metro cities by year 2000. Total lead free petrol is planned to be used in all state capitals by April, 1999 and by December, 2000 in the entire country.

Emission Standards

The exhaust emission standards for idling CO emission have been prescribed for vehicles. The Ministry of Surface Transport has notified the vehicular mass emission standards, as recommended by CPCB through Ministry of Environment & Forests. Further, the stringent exhaust emission standard for vehicles has been notified for the year, 2000 AD.

Exhaust Treatment

In order to reduce the tail pipe emissions, government. has made the fitting passenger cars with catalytic converters mandatory from April, 1995 in four metros. Catalytic converters convert CO, HC and NOx into harmless CO2, H2O and N2. The efficiency of catalytic converter varies from 60-90%.

Maintenance of In-use Vehicles, and Other Measures

Regular inspection and maintenance by authorized service centres will go a long way in reducing the pollution load.. Proper inspection and maintenance programs are widely used in other countries where it has been possible to reduce about 30-40% of pollution load from old vehicles. Similarly, improvement in design of engines including fuel injection system will enable the automobiles to go beyond compliance of emission standards. Some alternative fuels have been used or are being tried, particularly alcohol, CNG and electricity which may be promising options for reducing vehicular pollution.

Recommendation and Further Work

  • Besides above abatement and control strategies, proper and systematic management, improved road conditions, mass rapid transport system (high speed tram) should be introduced at the earliest.
  • Trees like Euginea (Jamun) along roadsides and Nerium (Kaner) between road dividers and alongside should be grown. These plants absorb and accumulate maximum lead from the atmosphere as studied by CPCB.
  • Unauthorized primary lead smelting units should be identified, and the units not meeting the lead emission standard should be closed down.
  • Studies on Benzene in the urban environment and near petrol pumps should be initiated, which require immediate attention. CPCB has already initiated work on this line using five different techniques namely thermal desorption, metal traps filled with Tenax TA, activated charcoal glass traps, both using active sampling, standard passive sampling traps and subsequent analysis using capillary GC-FID, instant measurement with portable GC-PID and Indicator tubes. Methods are being standardized for selection and use in Indian conditions (both indicative and analytical methods).
  • Benzene concentration in motor gasoline has been prescribed as 3% (V/V) to be achieved by all refineries by year, 2000 AD. Also CPCB is presently working on an auto oil programme and is planning to reduce Benzene level to 1% (V/V) from the year, 2005. To meet the 3% Benzene level, the refineries in India are going through the catalytic reformer route to achieve the standard.

References

  1. CPCB (1986); "Impact of Auto exhaust lead pollution on vegetation in UT of Delhi"; Report No. EIAS/1/1985-86.
  2. CPCB (1987); "Impact of Auto exhaust lead pollution on vegetation in UT of Delhi"; Report No. EIAS/2/1986-87.
  3. CPCB (1992); "Report on Tetraethyl lead in petrol & lead in exhaust from automobiles"; Report No. Probes/46/1992.
  4. WHO (1997); "Environmental Health Criteria - 3 : Lead". 5. CPCB (1997); "CPCB News Letter"; Vol. 4 (iii).

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