City – Jamshedpur (Jharkhand, India)


Emissions Inventory

Jamshedpur, named after the founder of the Tata Company, Jamshetji Tata is the highest populated city in the state of Jharkhand. It is synonymous with the steel industry it houses. Tata Steel is based in Jamshedpur and is the eight largest manufacturing company in the world. It is the first planned city in India. Geographically, it is located on the Chota Nagpur plateau and is bounded by the Subarnarekha and Kharkai rivers.

The areas surrounding Jamshedpur are rich in minerals, including iron ore, coal, manganese bauxite and lime. It is a modern, industrial city; the main industries being iron and steel, truck manufacturing, tinplate production, cement and other small and medium scale industries revolving around these products. 

The largest factory is that of Tata Steel situated almost at the centre of the city.  The other major factory in the city is Tata Motors manufacturing heavy vehicles and earth moving equipment. The Tata Motors plant spreads over 822 acres, is one of the largest in the country, and at peak rate can roll out 450 vehicles per day. There are more than a thousand manufacturing units at the Adityapur Industrial Area which is located just across the Kharkai river and is now referred to as Greater Jamshedpur. Adityapur is one of the larger industrial areas in India with an area of 33,970 acres.

An interesting point is that Jamshedpur is the only city with a population of more than a million that does not have a municipality. The government has tried to set one up, but has been vetoed on a couple of occasions in favor of the Tatas overseeing the administration of the city.

The 2011 census estimates that the population of Jamshedpur at 1.3 million. It covers an area of 224 square kilometers. To assess Jamshedpur’s air quality, we selected a 40km x 30km domain. This domain is further segregated into 1km grids, to study the spatial variations in the emission and the pollution loads.

 

Meteorology fields are important as they have a direct impact on air pollution concentrations. During periods of high precipitation or high speed winds, emissions from a city are swept away and do not have an impact on concentrations. On the other hand, during the winter months when temperatures and inversion heights are low, there is a greater impact of emissions on pollution concentrations. Low temperatures also affect behaviour through the need for space and water heating – which in turn has increases emissions.

We processed the NCEP Reanalysis global meteorological fields from 2010 to 2018 through the 3D-WRF meteorological model. A summary of the data for one year, averaged for the city’s airshed is presented below by month. Download the processed data which includes information on year, month, day, hour, precipitation (mm/hour), mixing height (m), temperature (C), wind speed (m/sec), and wind direction (degrees) – key parameters which determine the intensity of dispersion of emissions.

WRF Meteorology for Jamshedpur


Multi-Pollutant Emission Inventory

We compiled an emissions inventory for the Jamshedpur region for the following pollutants – sulfur dioxide (SO2), nitrogen oxides (NOx), carbon monoxide (CO), non-methane volatile organic compounds (NMVOCs), carbon dioxide (CO2); and particulate matter (PM) in four bins (a) coarse PM with size fraction between 2.5 and 10 μm (b) fine PM with size fraction less than 2.5 μm (c) black carbon (BC) and (d) organic carbon (OC), for year 2015 and projected to 2030. In Phase 1, base year for all the calculations was 2015. In Phase 2, all the calculations are updated for year 2018.

Emissions Inventory We customized the SIM-air family of tools to fit the base information collated from disparate sources. Apart from the official reports, resource material ranges from GIS databases of land use, land cover, roads and rail lines, water bodies, built up area (represented in the adjacent figure), commercial activities (such as hotels, hospitals, kiosks, restaurants, malls, cinema complexes, traffic intersections, worship points, industrial hubs, and telecom towers), to population density and meteorology at the finest spatial resolution possible (1-km). A detailed description of these resources is published as a journal article in 2019, which also includes a summary of baselines and pollution analysis for 20 Indian cities.

This emissions inventory is based on available local activity and fuel consumption estimates for the selected urban airshed (represented in the grid above). This information is collated from multiple agencies ranging from the central pollution control board, state pollution control board, census bureau, national sample survey office, ministry of road transport and highways, annual survey of industries, central electrical authority, ministry of heavy industries, and municipal waste management, and publications from academic and non-governmental institutions.

For the road transport emissions inventory, besides the total number of vehicles and their usage information, we also utilized vehicle speed information to spatially and temporally allocate the estimated emissions to the respective grids. This is a product of google maps services. For the city of Jamshedpur, we extracted the speed information for representative routes across the city for multiple days. This data is summarized below for a quick look.

Emissions Inventory Emissions Inventory

The summary for a city’s emissions inventory does not include natural emission sources (like dust storms, lightning, and seasalt) and seasonal open (agricultural and forest) fires. However, these are included in the overall chemical transport modeling in the national scale simulations. These emission sources are accounted in the concentration calculation as an external (also known as boundary or long-range) contribution to the city’s air quality.

Projections to 2030 under the business as usual scenario are influenced by the city’s social, economic, landuse, urban, and industrial layout and hence the projected (increasing and decreasing) rates that we assume are an estimate only. We based the vehicle growth rate on the sales projection numbers; industrial growth on the gross domestic product of the state; domestic sector, construction activities, brick demand, diesel usage in the generator sets, and open waste burning on population growth rates and notes from the municipalities on plans to implement waste management programs. We used these estimates to evaluate the trend in the total emissions and their likely impact on ambient PM2.5 concentrations through 2030.

The emissions inventory was then spatially segregated at a 0.01° grid resolution in longitude and latitude (equivalent of 1 km) to create a spatial map of emissions for each pollutant (PM2.5, PM10, SO2, NOx, CO and VOCs). The gridded PM2.5 emissions and the total (shares by sector) emissions are presented below.

Gridded PM2.5 Emissions (2018 and 2030)

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Total PM2.5 Emissions by Sector 2018-2030

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Total Estimated Emissions by Sector for 2018 (units – tons/year)

JamshedpurPM2.5PM10BCOCNOxCOVOCSO2
39,200 63,700 6,150 5,750 68,750 233,350 590,800 7,400
Transport emissions from road, rail, aviation, and shipping (for coastal cities) 3,750 3,950 1,500 1,200 13,700 134,000 23,850 200
Residential emissions from cooking, heating, and lighting activities 1,300 1,400 300650200 22,850 2,100 700
Industrial emissions from small, medium, and heavy industries (including power generation) 28,100 32,750 3,650 2,950 48,850 45,250 556,500 5,800
Dust emissions from road re-suspension and construction activities 3,600 23,100 ------
Open waste burning emissions60060050350- 2,850 550-
Diesel generator set emissions650700350200 4,350 13,950 6,300 100
Brick kiln emissions (not included in the industrial emissions) 1,200 1,200 300400 1,650 14,450 1,500 600

TRANS = transport emissions from road, rail, aviation, and shipping (for coastal cities); RESIDEN = residential emissions from cooking, heating, and lighting activities; INDUS = industrial emissions from small, medium, and heavy industries (including power generation); ALL.DUST = dust emissions from road re-suspension and construction activities; W.BURN = open waste burning emissions; DG.SETS = diesel generator set emissions; B.KILNS = brick kiln emissions (not included in the industrial emissions)


Chemical Transport Modeling

We calculated the ambient PM2.5 concentrations and the source contributions, using gridded emissions inventory, 3D meteorological data (from WRF), and the CAMx regional chemical transport model. The model simulates concentrations at 0.01° grid resolution and sector contributions for the urban area, which include contributions from primary emissions, secondary sources via chemical reactions, and long range transport via boundary conditions (represented as “boundary” in the pie graph below).

Emissions Inventory

The ribbon graph shows the variation for average PM2.5 pollution by month. Due to precipitation during the monsoon, usually pollution levels dip and may fall within national air pollution standards, however most cities are unable to attain these standards at other times of the year.

The following is a map of annual average PM2.5 pollution for the city of Jamshedpur. The main sources contributing towards PM2.5 in 2018 are in the pie-chart on the left. The change in contributions in 2030 from different sources are shown on the right.

Jamshedpur PM2.5 Source Contributions Jamshedpur Ambient PM2.5 Concentrations Jamshedpur PM2.5 Source Contributions

There is a temporal variation in source contributions and spatial contributions depending on meteorological factors. We have a map of monthly average PM2.5 levels as well as their source contributions for every month in the charts below.

Jamshedpur PM2.5 Monthly Concentrations Jamshedpur PM2.5 Source Apportionment

Satellite Data Derived Surface PM2.5 Concentrations

The results of satellite data derived concentrations are useful for evaluating annual trends in pollution levels and are not a proxy for on-ground monitoring networks. This data is estimated using satellite feeds and global chemical transport models. Satellites are not measuring one location all the time, instead, a combination of satellites provide a cache of measurements that are interpreted using global chemical transport models (GEOS-Chem) to represent the vertical mix of pollution and estimate ground-based concentrations with the help of previous ground-based measurements. The global transport models rely on gridded emission estimates for multiple sectors to establish a relationship with satellite observations over multiple years. These databases were also used to study the global burden of disease, which estimated air pollution as the top 10 causes of premature mortality and morbidity in India. A summary of PM2.5 concentrations for the period of 1998 to 2016 for the city of Jamshedpur is presented below. The global PM2.5 files are available for download and further analysis @ Dalhousie University.

The graphs for other district PM2.5 concentrations for this period, maps of national averages, and year-wise changes are available here. The data for district level PM2.5 concentrations for 1998-2016 period for can downloaded here.


Monitoring

We present below a summary of the ambient monitoring data available under the National Ambient Monitoring Program (NAMP), operated and maintained by the Central Pollution Control Board (CPCB, New Delhi, India). In Jamshedpur, as of November 2018, there are 0 continuous and 2 manual air quality stations in operation. An archive of all the data from the NAMP network from stations across India for the period of 2011-2015 is available here.

PM2.5 Source Contributions Ambient PM2.5 Concentrations PM2.5 Source Contributions

Real time PM2.5 pollution levels in and around the city of Jamshedpur


Resource Material

    • CPCB repository of continuous air monitoring data (Link)

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