ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

DISSEMINATION OF AIR QUALITY STATUS IN SMART CITIES- A CASE STUDY

Dr M V S RAJU G SIVA SANKAR Professor, Assistant professor Department of Civil Engineering Department of Civil Engineering V R Siddhartha Engineering College V R Siddhartha Engineering College Vijayawada

ABSTRACT Vijayawada is one of the biggest cities of even before separation of the state. Now it is considered as capital of newly formed Andhra Pradesh. There is a huge scope for lot of various activities in future being capital of Andhra Pradesh. Particulate matter and gaseous pollutants in the ambient atmosphere of Vijayawada are already increasing due to rapid increase in urbanization, congestion of roads, older vehicles and inadequate inspections of vehicles. Therefore there is a need to disseminate the status of air pollution in smart way to the public for their participation to mitigate the pollution. Air quality data is complex to understand for a common man. Nevertheless there is a necessity to report it to the public. Astonishingly little attention is paid to disseminate the information to the public, even though it is directly linked to the health of public. At the same time the dissemination of air quality data to the public should be simple and understandable. To meet the above an Air Quality Index (AQI) has been proposed to present the status of Vijayawada air quality. It is a rating scale in quantifying air pollution based on measured air pollutants for reporting daily status of pollution at a locality. In the present study, an Air Quality Index (AQI) has been calculated based on measured pollutants such as Sulphur dioxide (SO2), Nitrogen dioxide (NO2), Respirable Suspended Particulate Matter (RSPM) and Total Suspended Particulate Matter (TSPM) at selected residential area of Vijayawada city in 2014. It has been observed that the overall AQI value in residential area of Vijayawada is moderate and the responsible pollutant is RSPM. Keywords: Air Quality Index, Air Quality Standards, Pollution

1. INTRODUCTION humidity is 78% and the average annual Vijayawada is capital of newly rainfall is 103 cm. formed state ‘Andhra Pradesh’. General public will not understand Vijayawada is the biggest city in the the complex raw data, concentration - time Krishna District and the third largest city in plots, complex analysis and other findings the state of Andhra Pradesh, after of air quality. The complexity in air quality and Visakhapatnam, before data results in loss of interest among the separation. It extends over an area of 61.88 people. But the public is one of the main sq km. Vijayawada is located at 16.52° stakeholders in controlling air pollution. North Latitude 80.62° East Longitude. It is The information about daily air quality in situated on the banks of the cities is also important to those particularly as shown in Location Map (Figure 1). The who are suffering from health problems due City has a population of 14.7 lacs. The City to air pollution. Therefore they should be is also known as Bezawada. It is located at well informed the air quality status in about 275 Km from Hyderabad. It is well simple and understandable way. The connected to other regions via road, air and concept of air quality index (AQI) has been rail, and is one of the biggest railway developed to address the above concerns in junction in India. It is hub of various various countries. AQI is defined as an businesses including retail and wholesale overall scheme that transforms the markets. The climate is tropical, weighted values of individual air pollutants specifically a tropical wet and dry climate, (NO2, SO2, PM10, etc.) into a single with hot summers and moderate winters. number. Development of proper AQI and a The peak temperature reaches 47 °C mechanism to disseminate the index values (117 °F) in May - June, while the winter to citizens are essential for successful index temperature is 20-27 C. The average system. Different methods of disseminating

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

AQI include reporting on radio, newspaper time. Long-term, lower level RSPM and television and website. exposure may also cause cancer and premature deaths. Asthmatic patients when 2. Methodology exposed to high concentrations of NO2 Sampling locations suffer with lung irritation and lung damage. The air sampling station of present Sulphur dioxide affects humans by study is Benz Circle (Figure 1), which is a stimulating nerves in the lining of the nose main residential cum commercial centre of and throat and the lung’s airways. This Vijayawada city. It is the prominent causes a irritation in the throat, and a feeling junction of National highway 5 and 9 of chest tightness, which may lead to (Mahatma Gandhi Road) in Vijayawada. narrowing of the airways. About 99% of the sulphur dioxide in air comes from human sources. The main Air pollution in terms of particulate source of sulphur dioxide in the air is matter is growing in the city at an alarming industrial activity that processes materials rate due to increase in the number of that contain sulphur, such as generation of vehicles. The number of vehicles has electricity from coal, oil or gas that contains increased by 15 per cent in the last year, as sulphur. Some mineral ores also contain per official records. Older vehicles are also sulphur, and sulphur dioxide is released predominant in Vijayawada. Large number when they are processed. In addition, of two stroke two wheelers and old trucks industrial activities that burn fossil fuels in the city are significant contributors of air containing sulphur can be important pollution. Inadequate inspection and sources of sulphur dioxide. Sulphur dioxide maintenance facilities, road conditions and is also present in motor vehicle emissions, absence of fly over bridges at junctions as the result of fuel combustion. causing stagnation of vehicles also result in build up of air pollutants. About 60 percent of air pollution in Indian cities is due to automobile exhaust Another major source of RSPM and emission. Automobiles produces suspended Fine Particulate Matter in the city are coal particulate matter (SPM), oxides of sulphur based power plants, waste oil reprocessing (SOx), oxides of nitrogen (NOx), which industries, stone crusher, foundries, other have adverse effects on surrounding small scale industries and re-suspension of ecosystem. Finer particulate matter less road dust. Poor compliance of standard in than 10 micron size initiate diseases. small / medium scale industries also results in high levels of air pollution in particular Continuous exposure to the low at Autonagar. Frequent open burning of concentration and unexceptional conditions city garbage by Municipal Corporation leads to chronic diseases in humans. It is sanitary workers and private people to believed that these effects occur through easily get rid of the waste material on canal continued irritation by pollutants which bunds, road sides and near houses are interact with other environmental or another major source of fine particulate biological factors to Short-term exposure to matter in Vijayawada. RSPM can irritate the lungs and perhaps cause immune responses, lung constriction, Calculation of AQI consists of two producing shortness of breath and cough steps. (i) Sub-index for each pollutant is may result. Larger particles deposit in the calculated using sub index function given upper respiratory tract, while smaller below, which is based on National ambient inhalable particulates travel deeper into the air quality standards (Table 1) and health lungs and are retained for longer periods of effects. Each sub index represents a

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4 relationship between pollutant 3. Result and discussions: concentrations and health effects. Indian The sulphur dioxide (SO ) and 2 Air Quality Indices and corresponding Nitrogen dioxide (NO ) concentrations are health effects with colour coding are shown 2 in table 2. (ii) Maximum of sub-indices is fluctuating throughout the year. However considered as over all AQI of a locality. lower levels compared to prescribed air quality standards were reported during The general equation for the sub-index for entire period of study. The lower levels of a given pollutant concentration (Cp); SO and NO may be due to minimum 2 2 is based on ‘linear segmented principle’ and industrial activity and use of CNG and LPG is calculated as instead of diesel in Autos, Buses and private vehicles. Typical variations of SO 2 Ip= [{(IHI - ILO)/(BHI -BLO)} * (Cp- and NO were shown for the months of BLO)]+ ILO 2 April and Dec. 2014 in Figures 2 and 3 where, respectively. BHI = Breakpoint concentration greater or The concentrations of RSPM and TSPM equal to given concentration. exceeded the Air Quality Standards in the months of April, May and June. While they BLO = Breakpoint concentration smaller or were close to air quality standards during equal to given concentration. Feb, Mar, July, Nov and Dec months and IHI = AQI value corresponding to BHI reported below the prescribed limits in the remaining months of 2014. The reasons for ILO = AQI value corresponding to BLO high particulate matter in general, may be Cp = Pollutant concentration vehicles, commercial activities, Industrial activities, solid waste burning, re- For the AQI, a maximum operator system is suspension of traffic dust, commercial and selected: domestic use of fuels, etc. The major AQI = Max (I1, I2, I3, ..., In) sources of high RSPM levels in Vijayawada are vehicle traffic, burning of solid refuse Where p= 1,2,...,n; denotes number and re-suspension of traffic dust during dry of pollutants season. Lower levels of RSPM and TSPM were observed during monsoon months There are two reasons for adopting a possibly due to wet conditions. Variations maximum operator function: of RSPM and TSPM were shown for the

1. Free from ambiguity and months of April and Dec. 2014 in Figures 2 2. Health effects due to combination and 3 respectively. of pollutants are not known and So2 and No2 indices at Benz circle in thus a health- based index cannot residential area are good, while RSPM and be combined. TSPM indices are moderate and the Maximum operator approach has responsible parameter for pollution is been adopted by Sharma et al. (2001-2003) RSPM. From the above interpretation of air for development of an AQI scale for entire Quality index for Vijayawada is moderate India. and the responsible parameter for pollution is RSPM.

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

4. CONCLUSIONS  Frequent genuine pollution checks by Transport Department for The recorded values of SO and 2 vehicles reduce the pollutant NO are much lower than National ambient 2 emissions. air quality standards at Benz circle of  Abolishing two stroke two wheelers Vijayawada, Where as the concentrations and old trucks considerably reduce of RSPM and TSPM exceeded the Air the mobile pollution. Quality Standards in the months of April, May and June and they are close to the  There is a need to create awareness standards during Feb, Mar, July, Nov and among the public on the usage of Dec months. It clearly indicates that the diesel vehicles, as diesel emits more contribution of Particulate matter by hazardous gases than petrol. automobiles in residential areas is  Proper disposal method of city significant in Vijayawada. Burning of solid garbage is to be implemented and refuse and re-suspension of traffic dust open burning is to be stopped. during dry season are other major causes of RSPM and TSPM. ACKNOWLEDGEMENT AQI is the best and simple means The authors sincerely thank AP Pollution of disseminating the complex air quality Control Board, Vijayawada for providing data to the public of a locality. It creates not the data of air pollutants. only the interest but also makes the public to contribute for the abatement of air 5. REFERENCES pollution. [1] Banerjee, T. and Srivastava, A.K. (2010). Assessment of the Air Quality index for Vijayawada is Ambient Air Quality at the moderate and the responsible parameter of Integrated Industrial Estate- pollution is RSPM. Pantnagar through the Air Quality The following general recommendations Index (AQI) and Exceedence were made to improve the environmental Factor (EF). Asia-Pac. J. Chem. quality in Vijayawada. Eng. 6:64–70. [2] Borrego, C., Tchepel, O., Costa,  The citizens need to be encouraged A.M., Martins, H., Ferreira, J. and to opt the public transport system as Miranda, A. I. (2006). Traffic- it lessens fuel consumption by the related Particulate Air Pollution private vehicles. Exposure in Urban Areas. Atmos.  Absences of effective mass rapid Environ.40: 7205–7214. transport system and intra-city [3] Central Pollution Control Board railway networks have resulted in (2000) Air quality and status and people using their own vehicles for trends in India, NAAQMS/14/199 travel to workplace. This has 2000, CPCB, Delhi. resulted in uncontrolled growth of [4] Gurjar B.R., Butler T.M., vehicles Lawrence M.G. and Lelieveld J.,  Fly over bridges at main junctions Evaluation of emissions and air of roads prevent traffic jams quality in megacities, Atmospheric  The usage of petrol / CNG vehicles Environment, 42, 1593-1606 will reduce pollution to some (2008 extent. [5] Jain R., Dwivedi D.K. and Gupta A.B., Status of air quality at

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

selected traffic junctions of Jaipur Environment 37 (2003) 2005- city, Nature Environment and 2017. Pollution Technology, 3(4), 435- [10] Sharma, M., Aggrawal, S, Bose 442 (2004) P. (2002). Meteorology-based [6] Jaya Divakaran Sarasamma, Forecasting of Air Quality Index Beena Kochuraman using Neural Network. Narayanan,(2014). Air Quality Proceedings of International Assessment in the Surroundings of Conference ICONIP’02- KMML Industrial Area, Chavara SEAL’02-FSKD’02 on Neural in Kerala, South India, Aerosol Network, Singapore, November, and Air Quality Research, 14: 2002. 1769–1778. [11] Sharma, M., Maheshwari, M., [7] Joshi P.C., Swami A. and and Pandey, R. (2001) Gangwar K.K., Air quality Development of air quality index monitoring at two selected traffic for data interpretation and public junctions in the city of Haridwar, information. IIT-Kanpur, Report Him. J. Env. Zool., 20(2), 219-221 submitted to Central Pollution (2006) Control Board Delhi. [12] Tandon A., Yadav S. and Attri A.K., City-wide sweeping a [8] Mohanraj R. and Azeez P.A., source for respirable particulate Health effects of airborne matter in the atmosphere, particulate matter and the Indian Atmospheric Environment, 42, scenario, Current Science., 87(6), 1064-1069 (2008) 741-748 (2004) [13] Varma P.C., Jha C., Mian S., [9] Sharma M., Kiran YNVM and Sinha S.B. and Gupta V.S., Air Shandilya K. (2003).Investigation quality studies in an industrial and into formation of Atmospheric urban township of Jharia coal sulphate under High field, Dhanbad, IJEP., 14(4), 301- PM10concentration. Atmospheric 306 (1994)

List of Figures and List of Tables

Fig 1 Location map Benz circle, Vijayawada, Andhra Pradesh

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

SO2 µg/m3 300

250 NO2 µg/m3 200 SO2 & NO2 150 Limit 100 RSPM µg/m3 50

0

10-Apr-14 14-Apr-14 18-Apr-14 22-Apr-14 26-Apr-14

06-Apr-14 TSPM µg/m3 Concentration in in cu.m per micrograms Concentration TSPM Standard µg/m3 Fig2: Pollutant concentrations in April 2014 at Residential area of Benz circle

250 SO2 µg/m3

200 NO2 µg/m3

150 SO2 & NO2 Limit 100 RSPM µg/m3

50 TSPM µg/m3

0

Concentration in in cu.m per micrograms Concentration

17-Dec-14 07-Dec-14 12-Dec-14 22-Dec-14 27-Dec-14 02-Dec-14 TSPM Standard µg/m3 RSPM standard µg/m3

Figure 3: Pollutant Concentrations in Dec. 2014 at Residential area of Benz Circle

Table 1. National Ambient Air Quality Standards for Particulate Matter

Pollutant Time Weighted Concentration in Ambient Air Average Industrial Area Residential, Rural and other Areas Sulphur dioxide Annual Average 80 µg/m3 60 µg/m3 3 3 (So2) 24 Hours 120 µg/m 80 µg/m Average Oxides of nitrogen Annual Average 80 µg/m3 60 µg/m3 3 3 (No2) 24 Hours 120 µg/m 80 µg/m Average Suspended Annual Average 360 µg/m3 140 µg/m3 Particulate Matter 24 Hours 500 µg/m3 200 µg/m3 (SPM) Average Respirable Annual Average 120 µg/m3 60 µg/m3 Particulate Matter 24 Hours 150 µg/m3 100 µg/m3 (RSPM) Average

ELK Asia Pacific Journals – Special Issue ISBN: 978-81-930411-5-4

Table 2. Indian Air Quality Index (IND-AQI) and health statements

AQI AQI category Colour coding Associated Health Impacts 0–50 Good Minimal Impact 51–100 Satisfactory Minor breathing discomfort to sensitive people 101–200 Moderate Breathing discomfort to the people with lung disease such as asthma, people with heart disease, children and older adults 201–300 Poor Breathing discomfort to people on prolonged exposure and people with heart disease with short exposure 301–400 Very Poor Respiratory illness to the people on prolonged exposure. Effect may be more pronounced in people with lung and heart diseases 401-500 Severe Respiratory effects even on healthy people and serious health impacts on people with lung/heart diseases.

Table 3: Sub indices and AQI at Benz circle (Residential Area)-April, 2014

Sub index Dates AQI So2 No2 RSPM TSPM 3-Apr-14 2.89 7.5 172 110 172 6-Apr-14 2.58 6.58 169 115 169 8-Apr-14 2.55 7.47 176 149 176 12-Apr-14 2.86 6.41 187 152 187 18-Apr-14 2.64 6.23 182 134 182 20-Apr-14 2.81 6.64 180 141 180 23-Apr-14 2.72 5.94 187 144 187 26-Apr-14 2.83 5.94 171 128 171 28-Apr-14 2.69 5.27 177 129 177

Table 4: Sub indices and AQI at Benz circle (Residential Area)--December, 2014

Sub index Dates AQI So2 No2 RSPM TSPM 3-Dec-14 2.41 5.82 174 121 174 6-Dec-14 2.47 5.63 172 132 172 9-Dec-14 2.42 5.75 164 113 164 12-Dec-14 2.44 5.88 167 114 167 18-Dec-14 2.42 6.44 174 138 174 22-Dec-14 2.51 5.44 169 132 169 24-Dec-14 2.41 5.82 170 119 170 27-Dec-14 2.47 5.63 167 128 167