- Open Access
Vehicular emission inventory of criteria pollutants in Delhi
© Goyal et al.; licensee Springer. 2013
Received: 28 February 2013
Accepted: 20 April 2013
Published: 10 May 2013
The rapid urbanization in Delhi has resulted in a tremendous increase in the number of motor vehicles with the increase in population and urban mobilization. The vehicular traffic is now recognized as one of the main sources of air pollution in Delhi and has noticeable impact on air quality. The emission of criteria pollutants namely Carbon Monoxide (CO), Nitrogen Oxide (NOx) and Particulate Matter (PM) due to vehicles is estimated through the International Vehicle Emission (IVE) model, which includes the different driving modes of vehicles and meteorological parameters. The estimated emissions of Carbon Monoxide (CO), Nitrogen Oxides (NOx) and Particulate Matter (PM) due to different types of vehicles in the year 2008–09 are found to be 509, 194 and 15 tons/day respectively. The diurnal variation of emissions of air pollutants shows two peaks, which are fortunately matching with the morning and evening office hours. The emissions of CO and NOx due to personal cars (PCs) are found to be about 34% and 50% respectively, and the emission of CO due to 2 W (2- Wheeler) is about 61%. Similarly, the Heavy Commercial Vehicles (HCVs) are contributing PM about 92%. The analysis of fuel-wise emission of pollutants reveals that CO is mainly contributed by petrol, and NOx and PM are contributed by diesel. It is also noticeable that CO, NOx and PM emissions at ITO, one of the busiest traffic intersections of Delhi, are approximately 15, 6 and 0.5 tons/day respectively, which are found to be the maximum followed by Kashmiri Gate (ISBT), Nizamuddin etc. The present vehicular emissions inventory has been compared quantitatively with previous studies of Delhi. The present vehicular emission inventory has also validated using US environmental protection agency’s (USEPA’s) AERMOD model with observed concentration at different locations in Delhi. However, the present study shows that the air quality of Delhi has been degraded due to high level emissions of criteria pollutants.
Delhi is spread over an area of 1,484 km2 (573 sq mi), of which 783 km2 (302 sq mi) is designated rural and 700 km2 (270 sq mi) urban. The city's population is increasing rapidly with a consequent increase in the number of vehicles without a commensurate increase in road length. The number of vehicles registered in Delhi has already crossed 6 million and a sizeable vehicular traffic joins Delhi roads from the neighboring states (DSH 2010). It has been observed that vehicles alone contribute about 64% of the pollution in Delhi while other sources like power plants, industries, and domestic contribute 16%, 12% and 8% respectively (MoEF 1997). The maximum contribution of air pollution is growing rapidly from vehicular sources (Mitra and Sharma 2002). The main air pollutants emitted from these sources are Carbon monoxide (CO), Oxides of nitrogen (NOx) and Particulate Matter (PM). Some of them have been found to be much beyond the permissible levels governed by the Central Pollution Control Board (CPCB). The increasing levels of air pollutants are responsible for higher incidence rate of respiratory diseases, cancer, and heart diseases (Peters et al. 1997). Delhi’s degraded air quality is held responsible for about 18,600 premature deaths per year (TERI 2001).
There are several models used for estimation of vehicular emissions. The USEPA MOBILE model is one of them, which has been widely used. But in this model, the emission factors are conventionally based on the model years of US vehicle type and they are tested only on U.S. fuels and driving cycles, which can lead to incorrect emission values in India. So this model cannot be used for Delhi. One another vehicular emission model COPERT, which is widely used throughout Europe. However, this model cannot be used in Delhi as the emission factors used in this model are designed to be applied to average speeds for different road types. There are many more emission models such as LEAP (Long-range Energy Alternative Planning), VAPIS (Vehicle Air Pollution Information System) and Spreadsheet etc. But these models do not consider the variations in the local environment such as driving behaviors and traffic management and also assume that lower vehicle speeds increase emissions. In view of the above discussion, IVE model has been chosen for emission estimations. This model has been applied in several cities worldwide including Beijing and Shanghai, China (Nicole et al. 2005). The basic features of IVE model are based on (1) different modes of driving; (2) meteorological variables; and (3) emission factors of different pollutants with respect to different fueled vehicles.
The vehicle and fuel systems have to be addressed as a whole and jointly optimized in order to achieve significant reduction in emission. It was in 1996, the Ministry of Environment and Forests (MoEF), India, formally notified fuel specifications. In place of phase-wise up-gradation of fuel specifications, there appears to be a region-wise introduction of fuels of particular specifications. The high levels of pollution have necessitated eliminating leaded petrol throughout the country. To address the high pollution in 4 metro cities, 0.05% low sulfur diesel has been introduced since 2000–2001.
A domain of the study area 26 km × 30 km (~780 km2 area) in central Delhi has been selected.
The numbers of vehicles monitored by Central Road Research Institute (CRRI) at 27 locations on different types of roads in the year 2008–09 has been used. It is noticeable that during the monitoring hours, there were no unusual conditions such as major processions, VIP visits, or other activities, which could induce abnormal traffic characteristics in the selected grids during the survey.
The diurnal variations of vehicular movement are observed at major traffic intersections.
An emission inventory of each type of vehicle with respect to CO, NOx and PM has been made individually.
The diurnal variations of emissions during a study of start-up and running modes of different fueled vehicles have been estimated through IVE model.
The input data of the model is prepared according to the format of the model, which are fleeting characteristics, vehicular activity and emission factors based on local conditions. A fleet file contains the base emission factor adjustment by technology and pollutants. The basis of the emission prediction process of the IVE model begins with a base emission rate and a series of correction factors, which are applied to estimate the amount of pollutants from a variety of vehicle types. On-road fleet characteristics are one of the important factors to estimate emissions. A vehicle activity files mainly requires the information of location/time, temperature, road grade, gasoline information, diesel information and driving pattern distribution. While vehicle emission rate files contain the information of base emission factor and correction factors. There are three critical components that are used in the IVE model to create accurate emissions inventories: (1) Vehicle emission rates (Base Emission Factor and Correction Factors); (2) Vehicle activity (Location Input Data); and (3) Vehicle.
where, Q[t]: adjusted emission rate for each technology (start (g) or running (g/km); B[t]: base emission rate for each technology (start (g) or running (g/km). The correction factors used in equation 1 are categorized into several categories as local, fuel quality and power & driving variables. The local variables are ambient temperature, ambient humidity and altitude. The fuel quality variables are gasoline and diesel. The power & driving variables are road grade and air conditioning usage (IVEM, 2008). Equation (1) uses correction factors for eight parameters. Because of the lack of location specific data, an adjustment factor to the base emission rate “K(Base)[t]” has been taken equal to 1 that is the default value for IVE model and the fuel quality “K(Fuel)[t]”, inspection/maintenance correction factor “K(IM)[t]”, country correction factor “K(Cntry)[t]” and driving pattern “K[dt];” correction factor are taken from IVEM BERCF 2008 and IVEM Correction Factor Data 2008. In addition to this, values for temperature “K(Temp)[t]”, humidity “K(Hmdt)[t]”, altitude “K(Alt)[t]”, and base emission rate “B[t]” have been taken from the IVE model dataset (IVEM Correction Factor Data 2008).
A data collection methodology has been designed to collect a large amount of data with the help of the resources typically available in Delhi. The hourly number of vehicles monitored at 27 different locations in Delhi by CRRI, have been collected. The roads are chosen in the representative of residential streets, arterials and freeways.
AERMOD is the new dispersion model, proposed for use in regulatory applications, in the United States. AERMOD is intended to replace the USEPA regulatory model, ISCST3. The U.S. EPA has evaluated AERMOD using several field databases. The AERMOD atmospheric dispersion modelling system is an integrated system that includes- 1) A steady-state dispersion model designed for short-range (up to 50 kilometers) dispersion of air pollutant emissions from stationary industrial sources. 2) A meteorological data preprocessor (AERMET) that accepts surface meteorological data, upper air soundings, and optionally, data from on-site instrument towers. AERMOD requires hourly surface and upper air meteorological observations for simulating the pollutant dispersion (USEPA 2004). The major purpose of AERMET is to calculate boundary layer parameters for use by AERMOD. The meteorological preprocessor of AERMOD, known as AERMET calculates boundary layer parameters, viz. frictional velocity, Monin–Obukhov length, convective velocity scale, temperature scale, mixing height, surface heat flux by using local surface characteristics in the form of surface roughness and Bowen ratio in combination with standard meteorological observations (wind speed, wind direction, temperature and cloud cover). These parameters are then passed through an interface present in AERMOD to calculate vertical profiles of wind speed, lateral and vertical turbulent fluctuations, and the potential temperature gradient. The hourly surface meteorological observations have been acquired from Indian Meteorological Department (IMD), Delhi and twice daily upper air soundings have been acquired from university of Wyoming’s upper air sounding.
Results and discussions
Emissions (tons/day) from each type of vehicle
It is also observed that the emissions of air pollutants at various locations as ITO, Kashmiri Gate (ISBT), Nizamuddin, Shahzada bagh, Sirifort, Shahdara are in decreasing order. The estimated values of emission of CO, NOx, and PM at ITO are as 15, 6 and 0.5 tons/day respectively.
It is noticeable that the emissions of different criteria pollutants are varying differently into the different operating conditions of vehicles, e.g., CO emissions are found to be higher during idling and decelerating than cruising, the NOx and PM emissions are lower during idling and decelerating than cruising. Therefore, shutting down the engine and restarting it will result in reduced emissions compared to allowing it to idle. Thus, one can say that the longer the shutdown period, the greater the emission benefits.
Evaluation of present estimated emissions
Comparative analysis of vehicular emissions (tons/day) from different studies
Kansal et al. 2011 (ITO- all fuel) for year 2004-05
IIT study (ITO- all fuel) for the years 2008-09
Nagpure et al. 2011 (Delhi- petrol) for average values of years 1995-2005
IIT study (Delhi- petrol) for the year 2008-09
Gurjar et al. 2004 (Delhi- all fuel) for the year 2000
IIT study (Delhi- all fuel) for the year 2008-09
The “IIT study” estimated the emissions of CO, NOx and PM due to all different fueled (petrol, diesel and CNG) vehicles over study area of Delhi for the year 2008–09 and emission factors by ARAI (2007). Kansal et al. (2011) studied emissions of NOx and PM at different locations due to all fueled vehicles for the year 2004–05 with the emission factor of Kandilkar and Ramachandran (2000). Nagpure et al. (2011) studied emissions of CO and NOx over Delhi due to petrol vehicles for the years 1995–2005 excluding 2 wheelers. Gurjar et al. (2004) estimated the emissions of the same pollutants due to different fueled vehicles for the year 2000 using emission factors of Kandilkar and Ramachandran (2000).
Comparison of emissions between Kansal et al. 2011 and IIT study for the year 2004-05
PM Emissions (g/sec)
Kansal et al.2011 study for the year 2004-05
IIT study for the year 2004-05
Kansal et al.2011 study for the year 2004-05
IIT study for the year 2004-05
Comparison of emissions between Nagpure et al. 2011 and IIT study for the year 1995-2005
Nagpure et al. 2011 for the average values of emissions of 1995-2005
IIT study for the average values of emissions of 1995-2005
On the basis of the above discussion, it can be seen that emissions of IIT study for different years are very well matching with the emissions of the previous studies. Although, the methods used in all four are different. Finally it can be concluded that estimated emissions by IIT study are validated and can be considered for modeling studies and projection of future emissions. This study can also be used by policy makers and regulatory agencies for making some strategies for controlling the vehicular emissions in Delhi.
Spatial distribution of vehicle emissions
Simulation of the pollutant dispersion
The USEPA’s AERMOD model is a well accepted air pollution dispersion model worldwide. Currently, AERMOD is proposed the regulatory models for the Indian conditions. In this study, AERMOD model is adopted to simulate pollutant dispersion caused by motor vehicle emissions.
The dealing with meteorological data in AERMET, upper air data for Delhi cannot be used directly. The upper air data at 0:00 and 12:00 (UTC) switched in order to require by AERMET. The upper air data and surface air data for Delhi are received from the Atmospheric Science Department, University of Wyoming, Laramie, WY.
Variations of predicted concentrations with observed concentrations
This paper develops vehicle emission inventory for Delhi, the capital of India, using for detailed study of emissions from vehicular sources. The purpose of this paper is to introduce a new grid based mobile source emission inventory using IVE model. The vehicle emissions of CO, NOx and PM are approximately 509, 194 and 15 tons per day respectively, in Delhi for the year 2008–09. The maximum emissions approximately 86%, 27% and 71% of the total emissions are emitted during the starting-up period for CO, NOx and PM respectively. Petrol and diesel fuel vehicles are the main source of CO and PM pollutants respectively. CNG vehicles are one of the main contributors in NOX emission. The emissions of the present study are evaluated with those of previous studies made by Kansal et al. (2011), Nagpure et al. (2011) and Gurjar et al. (2004), which reveals that the results of the present study are quite satisfactory and agreed well with previous studies. The spatial and temporal emission inventories of criteria pollutants from on-road vehicle emissions are justified with AERMOD analysis. The IIT emission inventory is superior to previous studies in the following manner as these three studies are based on number of vehicles, emission factor and vehicle kilometer travel. The IIT study calculates the emissions using IVE model, which also includes (1) different modes of driving; (2) meteorological variables in terms of correction factor; and (3) emission factors of different pollutants with respect to different type and fueled vehicles. However, the IIT emissions are seems to be comparable with earlier studies and are also validated through air quality model.
There are some drawbacks in the present emission inventory as the emission values of the present study would be improved if hourly monitored values of the number of all different types and different fueled vehicles at each grid point, i.e., at each 2 km distance would be available. The major uncertainty of the present study is the use of piecewise information concerning the emissions.
- ARAI (The Automotive Research Association of India): Air Quality Monitoring Project-Indian Clean Air Programme (ICAP), Draft Report on “Emission Factor Development for Indian Vehicles” as a part of ambient air quality monitoring and emission source apportionment studies. 2007.Google Scholar
- DSH (Delhi Statistical Handbook): Directorate of Economics & Statistics, Government of National Capital Territory of Delhi, various issues. 2010. . Accessed on October 2010 http://www.delhi.gov.in/ Google Scholar
- GNCTD: State of Environment Report for Delhi, Department of Environment and Forests. New Delhi, India: Government of NCT of Delhi; 2010.Google Scholar
- Gurjar BR, Van Aardenne JA, Lelieveld J, Mohan M: Emission estimates and trends (1990–2000) for megacity Delhi and implications. Atmos Environ 2004, 38: 5663-5681. 10.1016/j.atmosenv.2004.05.057View ArticleGoogle Scholar
- IVEM: International vehicular emission model, development of the emission rates for use in the IVE Model. 2008. . Jan. 23, 2009 http://www.issrc.org/ive/ Google Scholar
- IVEM BERCF: IVEM Base Emission Rate Correction Factor Data, Appendix B: Correction Factor Data (.xls). 2008. . (Jan. 23, 2009) http://www.issrc.org/ive Google Scholar
- IVEM Correction Factor Data: Appendix B: Correction Factor Data (.xls). 2008. . (Jan. 23, 2009) http://www.issrc.org/ive Google Scholar
- Kandilkar M, Ramachandran G: The causes and consequence of particulate air pollution in urban: A Synthesis of the Science. Annu Rev Energy Env 2000, 25: 629-684. 10.1146/annurev.energy.25.1.629View ArticleGoogle Scholar
- Kansal A, Khare M, Sharma CS: Air quality modelling study to analyse the impact of the World Bank emission guidelines for thermal power plants in Delhi. Atmos Pollut Res 2011, 2: 99-105. 10.5094/APR.2011.012View ArticleGoogle Scholar
- Mitra AP, Sharma C: Indian aerosols: present status. Chemosphere 2002, 49: 1175-1190. 10.1016/S0045-6535(02)00247-3View ArticleGoogle Scholar
- MoEF: White paper on pollution in Delhi with an action plan. New Delhi: Ministry of Environment and Forest, Government of India; 1997.Google Scholar
- Nagpure AS, Gurjar BR, Kumar P: Impact of altitude on emission rates of ozone precursors from gasoline-driven light-duty commercial vehicles. Atmos Environ 2011, 45: 1-5. 10.1016/j.atmosenv.2010.09.021View ArticleGoogle Scholar
- Nicole D, James L, Mauricio O, Nick N, Matthew B: Transportation Research Board 81st Annual Meeting, Washington DC. 2005.Google Scholar
- Peters A, Wichmann HE, Tuch T, Heinrich J, Heyder J: Respiratory effects are associated with the number of ultrafine particles. Am J Respir Crit Care Med 1997, 155: 1376-1383. 10.1164/ajrccm.155.4.9105082View ArticleGoogle Scholar
- TERI: TERI Project Report No. 2001EE41. New Delhi: Tata Energy Research Institute; 2001.Google Scholar
- The Economic Times: Delhi world's fifth worst city for commuters: Study. 2010.Google Scholar
- USEPA: AERMOD: description of model formulation. Report EPA-454/R-03- 04. 2004. September 2004. http://www.epa.gov/scram001/7thconf/aermod/aermod_mfd.pdf Google Scholar
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