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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 705
A Literature Review on Ambient Air Quality Monitoring Near the Solid
Waste Disposal Site Harihar Tq, Davangere Dist.
Jagadeesh Chandra Bose G.S1, Dr. D. P Nagarajappa2, Shivakeshavakumar P3.
1PG student,Department of Studies in Civil Engineering, University B.D.T College of Engineering,Davangere,
Karnataka, India.
2Proffesor, Department of Studies in Civil Engineering, University B.D.T College of Engineering,Davangere,
Karnataka, India
3Proffesor, Department of Studies in Civil Engineering, Proudadevaraya institute of technology Hospet, Karnataka,
India
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract - One of the major drawbacks of solid waste
disposal site is air pollution. Hence monitoring of air quality
near the solid waste disposal sites is essential and hence
predicting concentrations levels of Suspended Particulate
matter (SPM) of diameter less than 10micron, SO2, NO2 is
needed in order to prevent the adverse impacts on health of
the workers working over there. This literaturereviewfocuses
on methodologies used for determiningconcentrationlevels of
pollutants that may generate air pollution and predict air
quality index (AQI) values from the obtained concentrations
levels of Suspended particulate matter, Sulphur dioxide,
Nitrogen dioxide.
Key Words: Air Quality, Suspended Particulate Matter,
SO2, NO2, NAAQS, AQI
1. INTRODUCTION
Air pollution can alsobethereasonfordifferentillness,
allergies and even may lead to human’s demise. These are
also dangerous to towards living organisms suchasanimals,
crop and also affect the natural environment by causing
ozone depletion, climate change or built environment such
as acid rain. Both the process from nature and activities of
human can produce air pollution.
Air pollution can also be a main harmful cause of
many of illness such as breathing infections, heart diseases,
chronic obstructive pulmonary illness, lung cancer stroke
etc. There are many evidences suggesting that air pollution
consumption might be linked with IQ scores, impaired
cognition, most of the problems of psychiatric disorders for
instance depression. Air pollution affects human especially
to cardiovascular system and respiratory system. Every
responses to the pollutants depends upon the variety of
pollutant that is exposed to, level of exposure, genetic and
general status of the health.
Most of the population of WHO European province
survive in an areas where the concentration of the air
pollution has attained certain level that resulting on worse
health impacts. Minimizing the impacts on the health is the
goal principle of the pollution abetments initiative’s run by
various entities at various level and encourage by society.
Preparing an effective pollution reducing strategy requires
identifying the most serious or most prevalent health
problems in exposed population. The location of pollution
hotspots, the change in the pollution as well as the
composition of the pollution are of concern.
Getting an idea forminimizingthepollutionfocused
at creatively conserving public health require more
information than knowledge of the location where the odd
health affects in terms of kind andpredictednumberofcases
attributes to the pollution, may be important to satisfy and
encourage the decisions that might be more expensive and
requires more involvement from the society. The CPCB
states that 12 parameters (Air Pollutants) are employed to
measure the AQI, including NO2 (Nitrogen Dioxide), SO2
(Sulfur Dioxide), CO (Carbon Monoxide), O3 (Ozone), PM10
(Particulate Matter having diameter 10 micron or less),
PM2.5 (Particulate Matter having diameter 2.5 micron or
less), NH3 (Ammonia), Pb (Lead), Ni (Nickel), As ( The
majority of cases, the air quality index (AQI) is based on the
criterion pollutants (i.e., PM10, PM2.5, SO2, NO2, CO, and
O3), however it is better to use manypollutants from the list
of 12 pollutants when computing the AQI. However, the
choice of pollutants is determined by the AQI objectives, the
averaging period, the availability of data, the frequency of
monitoring, and the measuring techniques.
A pollutant concentration all through a specificaveragetime
from air monitoring or a model is essential for computation.
The rate of air pollution is represented by the mixture of
Concentration and time. Epidemiological study shows the
clinical effects associated with a definite dosage. Ordinarily,
air quality indexes are classed into categories. Each range
has a typical public health advisory, a narrative, and color
codes.
Air quality index is directly proportional to the rate of
emissions. For instance at the peak hours traffic or when
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 706
there is unwind forest fire or when the air pollution is not
been diluted.
2 Objectives
 To Determine the Concentration Levels of Air
Pollutants such as Suspended Particulate Matter in
Solid Waste Disposal Site of Harihar Taluk,
Davangere District and Compare them with the
National Ambient Air Quality Standards..
 To Determine the Concentration Levels of Gaseous
Pollutants such as Sulphur Dioxide and Nitrogen
Dioxide in Solid Waste Disposal Site of Harihar
Taluk, Davangere District and Compare them with
the National Ambient Air Quality Standards.
Determining the Air Quality Index from the
Obtained Observations of Suspended Particulate
Matter, Sulphur Dioxide and Nitrogen Dioxide and
Comparing the AQI Values with NAAQS.
2.1 Formation of AQI values involves two steps
1. Determination of concentration level of suspended
particulate matter
2. Determination of concentration of Sulphur dioxide
3. Determination of concentration of Nitrogen dioxide
2.2 Calculation of Suspended particulate matter
C = (W1-W2) x 106/V in µg/m3
W1 = Starting weight in grams of the filter paper
W2 = Ultimate weight of the filter paper
V = volume of air assessed in m3
C = concentration of suspended particulatematterin µg/m3
2.3 Calculation of Sulphur dioxide
C (SO2µg/m3) = (A1-A2)*CF*V1/V2*V3
Where,
C SO2= Sulphur dioxide’s concentration, µg/m3
A1 = Sample’s absorbance
A2 = Reagents blank’s absorbance
CF = Caliberation factor
V2 = Air sampled volume, m3
V1 = Sample’s volume, ml
V3 = Volume of aliquot taken for analysis, ml.
2.4 Calculation of Nitrogen dioxide
C (NO2 µg/m3) = (A1-A2)*CF*V1/V2*V3*0.82
Where,
A1 = Sample’s absorbance
A2 = Reagent blank samples absorbance
CF = Caliberation factor
V2 = Air sampled volume, m3
V1 = Sample’s volume, ml
V3 = Volume of aliquot taken for analysis, ml.
2.5 Calculation of Air quality index (AQI)
AQI = 1/3[{SO2/sSO2} + {NO2/sNO2} + {SPM/sSPM}] x 100
Where,
SO2 = Obtained observations of Sulphur dioxide in µg/m3
NO2 = Obtained observations of Nitrogen dioxide in µg/m3
SPM = Obtained observations of the suspended particulate
matter in µg/m3
sSO2, sNO2, sSPM = standardized observations of SO2, NO2
and SPM.
Table -1: AQI and possible health impacts
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 707
As the AQI rises, as seen in figure 3, so will the likelihood of
unfavorable or grave health impacts. The AQI provides an
accurate representation of the air around us and indicates
the level of air pollution. People can take safeguards against
illness risks associated with air pollution by being aware of
the AQI and the air quality or pollution in their region or
location. In terms of air pollution, India isrankedfifthamong
98 nations. Therefore, it is crucial to do research on India's
air quality and develop regulations to lessen air pollution.
3. LITERATURE REVIEW
Anikender Kumar, PramilaGoyal(2011)presentedthe
study that forecasts the daily AQI value for the city Delhi,
India using previous record of AQI and meteorological
parameters with the helpofPrincipal ComponentRegression
(PCR) and Multiple Linear Regression Techniques. They
perform the prediction of daily AQI of the year 2006 using
previous records of the year 2000-2005 and different
equations. Afterthatthispredictedvaluethencomparedwith
observed value of AQI of 2006 for the seasons summer,
Monsoon, Post Monsoon and winter using Multiple Linear
Regression Technique [1]. Principal Component Analysis is
used to find the collinearityamongtheindependentvariables.
The Principal components were used in Multiple Linear
Regression to eliminate collinearity among the predictor
variables and also reduce the number of predictors [1]. The
Principal Component Regression gives the better
performance forpredictingtheAQIinwinterseasonthanany
other seasons. In this study only meteorological parameters
were considered or used while forecastingthefutureAQIbut
they have not considered theambientairpollutantsthatmay
cause the adverse health effects.
Huixiang Liu (et al.2019) have taken two different
cities Beijingand Italiancity forthestudypurpose.They have
forecasted the Air Quality Index (AQI) for the city Beijingand
predicting the concentration of NOx in an Italian City
depending on two different publicly available datasets. The
first Dataset forthe period ofDecember2013toAugust 2018
having 1738 instances is made available from the Beijing
Municipal EnvironmentalCentre[5]whichcontains thefields
like hourly averaged AQI and the concentrations of PM2.5,
O3, SO2, PM10, and NO2 in Beijing. The second Dataset with
9358 instances is collected from Italian city for the period of
March 2004 to February 2005. This dataset contains the
attributes as Hourly averaged concentration of CO, Non
methane Hydrocarbons, Benzene, NOx, NO2 [5]. But they
focused majorly on NOx prediction as it is one of the
important predictor for Air Quality evaluation. They used
Support Vector Regression (SVR) and Random Forest
Regression (RFR) techniques for AQI and NOx concentration
prediction. SVR shows better performance in prediction of
AQI while RFR gives the better performancein predictingthe
NOx concentration.
ZiyueGuan and Richard O. Sinnot(2018)usedthevarious
machine learning algorithms to predict the PM2.5
concentration. Data were collected from the official website
of Environment Protection Agency (EPA) for the city
Melbourne that contains PM2.5 air parameter and they have
also collected the unofficial data from Air beam which is the
mobile device used to measure PM2.5 value[8].Themachine
Learning Algorithms Artificial NeuralNetwork (ANN),Linear
Regression (LR) and Long Short Term Memory (LSTM)
recurrent neural network were usedforthePM2.5prediction
but out of these algorithmsLSTM givesthe best performance
ad predict the high PM2.5 value with reasonable Accuracy.
HeidarMaleki (et al.2019) predicted the hourly
concentration values for the ambient airpollutantsNO2,SO2,
PM10, PM2.5,COandO3forthestationsNaderi,Havashenasi,
MohiteZist and Bedsat in Ahvaz, Iran which is the most
polluted city in the world. They have also calculated and
predicted Air Quality Index (AQI) and Air Quality Health
Index (AQHI) for the four air quality monitoring stations in
Ahvaz mentioned above.TheyusedArtificial NeuralNetwork
(ANN) machine learning algorithm for the prediction of air
pollutants concentration (hourly) and two air qualityindices
AQI and AQHI over the August 2009 to August 2010. Input to
ANN algorithms involves the factors such as meteorological
parameters, Air pollutants concentration, time and date.
4. Results
Table 2:-Values of the AQI in respected areas during the
month of April, May and June
Sl
no
Locations of
solid waste
disposal site
AQI value
during
the
month of
March
AQI
value
during
the
month
of April
AQI
value
during
the
month
of June
1 NORTH ZONE 36.06 29.89 35.7
2 EAST ZONE 32.2 29.49 31.8
3 SOUTH ZONE 32.9 31.7 32.07
4 WEST ZONE 29.7 31.3 29.4
5 500m away
from the SWD
site
27.42 26.4 27.14
6 1.5km away
from the SWD
site
30.65 24.36 30.35
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 708
5. Conclusions
Determined the SPM, SO2, NO2,andAQIconcentrationsatthe
6 chosen locations neat solid waste disposal site at Harihar
taluk in order to resolve this current work. This chapter has
discussion of the conclusions drawn from the data and
results obtained.
 Based on the locations, it can be presume thatinthe
months of April, May and June the SPM
agglomeration is nearer to the limits of SPM
prescribed by the NAAQS in an industrial zone and
hence it is quite harmful to the workers who are
working near the landfill site of Harihar taluk.
 In all locations during the months of April, May and
June the SO2 and NO2 values were withintheNAAQS
permissible levels.
The solid waste disposal site is significantly polluted bySPM
and hence making it unhealthy for the workersandresulting
a variety of health concern
6. REFERENCES
 Anikender Kumar and Pramila Goyal., (2011),
“Forecasting of Air Quality in Delhi using Principal
Component Regression Technique”, Atmospheric
Pollution Research, 436-444.
 Archontoula Anitha K.G, Cynthia Carolin.,
(2015), “Assessment of Air Quality of Davangere
City-A Case Study, ISSN; 2321-0869(O) 2454-
4698(P), Volume-3, Issue-8.
 Chalouakou, Georgios Gravis., (2012), “Neural
Network and Multiple Regression Models for PM10
Prediction in Athens; A Comparative Assessment”,
Journal of the Air and Waste Management
Association.
 Gowtham Sarella.,(2015), “ Ambient Air Quality
Analysis using Air Quality Index “ A Case Study of
Vapi”, International Journal for Innovative
Research in Science and Technology,Vol(1),pp:01.
 Mohammad Shakir, N. Rakesh., “Investigation on
Air Quality Pollutant Data Sets using Data Mining
Tool”, IEEE Xplore Part Number: CFP 180ZV-ART;
ISBN;978-1-5386-1442-6
 Nidhi Sharma and Shwetha Taneja.,(2018), “
Forecasting Air Pollution Load in Dehli using Data
Analysis Tools”, Science Direct, 132 1077-1085
 Radhika M Patil and H. T Dinide., (2020), “A
Literature Review on Prediction of Air Quality
Index and Forecasting Ambient Air Pollutants
using Machine Learning Algorihtms”.
 R Gunasegaram, K. Kumarswamy., (2012)
“Monitoring of Ambient Air Quality in Salem City,
Tamil Nadu”, International Journal of Current
Research, ISSN: 0975-833X, Vol .4, Issue 03, and
pp: 275-280.
 Tanushree Ganguly, Kurinji L. Selvaraj., “Review
and Outlook of Clean Air and Action Plans”.

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A Literature Review on Ambient Air Quality Monitoring Near the Solid Waste Disposal Site Harihar Tq, Davangere Dist

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 705 A Literature Review on Ambient Air Quality Monitoring Near the Solid Waste Disposal Site Harihar Tq, Davangere Dist. Jagadeesh Chandra Bose G.S1, Dr. D. P Nagarajappa2, Shivakeshavakumar P3. 1PG student,Department of Studies in Civil Engineering, University B.D.T College of Engineering,Davangere, Karnataka, India. 2Proffesor, Department of Studies in Civil Engineering, University B.D.T College of Engineering,Davangere, Karnataka, India 3Proffesor, Department of Studies in Civil Engineering, Proudadevaraya institute of technology Hospet, Karnataka, India ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - One of the major drawbacks of solid waste disposal site is air pollution. Hence monitoring of air quality near the solid waste disposal sites is essential and hence predicting concentrations levels of Suspended Particulate matter (SPM) of diameter less than 10micron, SO2, NO2 is needed in order to prevent the adverse impacts on health of the workers working over there. This literaturereviewfocuses on methodologies used for determiningconcentrationlevels of pollutants that may generate air pollution and predict air quality index (AQI) values from the obtained concentrations levels of Suspended particulate matter, Sulphur dioxide, Nitrogen dioxide. Key Words: Air Quality, Suspended Particulate Matter, SO2, NO2, NAAQS, AQI 1. INTRODUCTION Air pollution can alsobethereasonfordifferentillness, allergies and even may lead to human’s demise. These are also dangerous to towards living organisms suchasanimals, crop and also affect the natural environment by causing ozone depletion, climate change or built environment such as acid rain. Both the process from nature and activities of human can produce air pollution. Air pollution can also be a main harmful cause of many of illness such as breathing infections, heart diseases, chronic obstructive pulmonary illness, lung cancer stroke etc. There are many evidences suggesting that air pollution consumption might be linked with IQ scores, impaired cognition, most of the problems of psychiatric disorders for instance depression. Air pollution affects human especially to cardiovascular system and respiratory system. Every responses to the pollutants depends upon the variety of pollutant that is exposed to, level of exposure, genetic and general status of the health. Most of the population of WHO European province survive in an areas where the concentration of the air pollution has attained certain level that resulting on worse health impacts. Minimizing the impacts on the health is the goal principle of the pollution abetments initiative’s run by various entities at various level and encourage by society. Preparing an effective pollution reducing strategy requires identifying the most serious or most prevalent health problems in exposed population. The location of pollution hotspots, the change in the pollution as well as the composition of the pollution are of concern. Getting an idea forminimizingthepollutionfocused at creatively conserving public health require more information than knowledge of the location where the odd health affects in terms of kind andpredictednumberofcases attributes to the pollution, may be important to satisfy and encourage the decisions that might be more expensive and requires more involvement from the society. The CPCB states that 12 parameters (Air Pollutants) are employed to measure the AQI, including NO2 (Nitrogen Dioxide), SO2 (Sulfur Dioxide), CO (Carbon Monoxide), O3 (Ozone), PM10 (Particulate Matter having diameter 10 micron or less), PM2.5 (Particulate Matter having diameter 2.5 micron or less), NH3 (Ammonia), Pb (Lead), Ni (Nickel), As ( The majority of cases, the air quality index (AQI) is based on the criterion pollutants (i.e., PM10, PM2.5, SO2, NO2, CO, and O3), however it is better to use manypollutants from the list of 12 pollutants when computing the AQI. However, the choice of pollutants is determined by the AQI objectives, the averaging period, the availability of data, the frequency of monitoring, and the measuring techniques. A pollutant concentration all through a specificaveragetime from air monitoring or a model is essential for computation. The rate of air pollution is represented by the mixture of Concentration and time. Epidemiological study shows the clinical effects associated with a definite dosage. Ordinarily, air quality indexes are classed into categories. Each range has a typical public health advisory, a narrative, and color codes. Air quality index is directly proportional to the rate of emissions. For instance at the peak hours traffic or when
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 706 there is unwind forest fire or when the air pollution is not been diluted. 2 Objectives  To Determine the Concentration Levels of Air Pollutants such as Suspended Particulate Matter in Solid Waste Disposal Site of Harihar Taluk, Davangere District and Compare them with the National Ambient Air Quality Standards..  To Determine the Concentration Levels of Gaseous Pollutants such as Sulphur Dioxide and Nitrogen Dioxide in Solid Waste Disposal Site of Harihar Taluk, Davangere District and Compare them with the National Ambient Air Quality Standards. Determining the Air Quality Index from the Obtained Observations of Suspended Particulate Matter, Sulphur Dioxide and Nitrogen Dioxide and Comparing the AQI Values with NAAQS. 2.1 Formation of AQI values involves two steps 1. Determination of concentration level of suspended particulate matter 2. Determination of concentration of Sulphur dioxide 3. Determination of concentration of Nitrogen dioxide 2.2 Calculation of Suspended particulate matter C = (W1-W2) x 106/V in µg/m3 W1 = Starting weight in grams of the filter paper W2 = Ultimate weight of the filter paper V = volume of air assessed in m3 C = concentration of suspended particulatematterin µg/m3 2.3 Calculation of Sulphur dioxide C (SO2µg/m3) = (A1-A2)*CF*V1/V2*V3 Where, C SO2= Sulphur dioxide’s concentration, µg/m3 A1 = Sample’s absorbance A2 = Reagents blank’s absorbance CF = Caliberation factor V2 = Air sampled volume, m3 V1 = Sample’s volume, ml V3 = Volume of aliquot taken for analysis, ml. 2.4 Calculation of Nitrogen dioxide C (NO2 µg/m3) = (A1-A2)*CF*V1/V2*V3*0.82 Where, A1 = Sample’s absorbance A2 = Reagent blank samples absorbance CF = Caliberation factor V2 = Air sampled volume, m3 V1 = Sample’s volume, ml V3 = Volume of aliquot taken for analysis, ml. 2.5 Calculation of Air quality index (AQI) AQI = 1/3[{SO2/sSO2} + {NO2/sNO2} + {SPM/sSPM}] x 100 Where, SO2 = Obtained observations of Sulphur dioxide in µg/m3 NO2 = Obtained observations of Nitrogen dioxide in µg/m3 SPM = Obtained observations of the suspended particulate matter in µg/m3 sSO2, sNO2, sSPM = standardized observations of SO2, NO2 and SPM. Table -1: AQI and possible health impacts
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 707 As the AQI rises, as seen in figure 3, so will the likelihood of unfavorable or grave health impacts. The AQI provides an accurate representation of the air around us and indicates the level of air pollution. People can take safeguards against illness risks associated with air pollution by being aware of the AQI and the air quality or pollution in their region or location. In terms of air pollution, India isrankedfifthamong 98 nations. Therefore, it is crucial to do research on India's air quality and develop regulations to lessen air pollution. 3. LITERATURE REVIEW Anikender Kumar, PramilaGoyal(2011)presentedthe study that forecasts the daily AQI value for the city Delhi, India using previous record of AQI and meteorological parameters with the helpofPrincipal ComponentRegression (PCR) and Multiple Linear Regression Techniques. They perform the prediction of daily AQI of the year 2006 using previous records of the year 2000-2005 and different equations. Afterthatthispredictedvaluethencomparedwith observed value of AQI of 2006 for the seasons summer, Monsoon, Post Monsoon and winter using Multiple Linear Regression Technique [1]. Principal Component Analysis is used to find the collinearityamongtheindependentvariables. The Principal components were used in Multiple Linear Regression to eliminate collinearity among the predictor variables and also reduce the number of predictors [1]. The Principal Component Regression gives the better performance forpredictingtheAQIinwinterseasonthanany other seasons. In this study only meteorological parameters were considered or used while forecastingthefutureAQIbut they have not considered theambientairpollutantsthatmay cause the adverse health effects. Huixiang Liu (et al.2019) have taken two different cities Beijingand Italiancity forthestudypurpose.They have forecasted the Air Quality Index (AQI) for the city Beijingand predicting the concentration of NOx in an Italian City depending on two different publicly available datasets. The first Dataset forthe period ofDecember2013toAugust 2018 having 1738 instances is made available from the Beijing Municipal EnvironmentalCentre[5]whichcontains thefields like hourly averaged AQI and the concentrations of PM2.5, O3, SO2, PM10, and NO2 in Beijing. The second Dataset with 9358 instances is collected from Italian city for the period of March 2004 to February 2005. This dataset contains the attributes as Hourly averaged concentration of CO, Non methane Hydrocarbons, Benzene, NOx, NO2 [5]. But they focused majorly on NOx prediction as it is one of the important predictor for Air Quality evaluation. They used Support Vector Regression (SVR) and Random Forest Regression (RFR) techniques for AQI and NOx concentration prediction. SVR shows better performance in prediction of AQI while RFR gives the better performancein predictingthe NOx concentration. ZiyueGuan and Richard O. Sinnot(2018)usedthevarious machine learning algorithms to predict the PM2.5 concentration. Data were collected from the official website of Environment Protection Agency (EPA) for the city Melbourne that contains PM2.5 air parameter and they have also collected the unofficial data from Air beam which is the mobile device used to measure PM2.5 value[8].Themachine Learning Algorithms Artificial NeuralNetwork (ANN),Linear Regression (LR) and Long Short Term Memory (LSTM) recurrent neural network were usedforthePM2.5prediction but out of these algorithmsLSTM givesthe best performance ad predict the high PM2.5 value with reasonable Accuracy. HeidarMaleki (et al.2019) predicted the hourly concentration values for the ambient airpollutantsNO2,SO2, PM10, PM2.5,COandO3forthestationsNaderi,Havashenasi, MohiteZist and Bedsat in Ahvaz, Iran which is the most polluted city in the world. They have also calculated and predicted Air Quality Index (AQI) and Air Quality Health Index (AQHI) for the four air quality monitoring stations in Ahvaz mentioned above.TheyusedArtificial NeuralNetwork (ANN) machine learning algorithm for the prediction of air pollutants concentration (hourly) and two air qualityindices AQI and AQHI over the August 2009 to August 2010. Input to ANN algorithms involves the factors such as meteorological parameters, Air pollutants concentration, time and date. 4. Results Table 2:-Values of the AQI in respected areas during the month of April, May and June Sl no Locations of solid waste disposal site AQI value during the month of March AQI value during the month of April AQI value during the month of June 1 NORTH ZONE 36.06 29.89 35.7 2 EAST ZONE 32.2 29.49 31.8 3 SOUTH ZONE 32.9 31.7 32.07 4 WEST ZONE 29.7 31.3 29.4 5 500m away from the SWD site 27.42 26.4 27.14 6 1.5km away from the SWD site 30.65 24.36 30.35
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 10 | Oct 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 708 5. Conclusions Determined the SPM, SO2, NO2,andAQIconcentrationsatthe 6 chosen locations neat solid waste disposal site at Harihar taluk in order to resolve this current work. This chapter has discussion of the conclusions drawn from the data and results obtained.  Based on the locations, it can be presume thatinthe months of April, May and June the SPM agglomeration is nearer to the limits of SPM prescribed by the NAAQS in an industrial zone and hence it is quite harmful to the workers who are working near the landfill site of Harihar taluk.  In all locations during the months of April, May and June the SO2 and NO2 values were withintheNAAQS permissible levels. The solid waste disposal site is significantly polluted bySPM and hence making it unhealthy for the workersandresulting a variety of health concern 6. REFERENCES  Anikender Kumar and Pramila Goyal., (2011), “Forecasting of Air Quality in Delhi using Principal Component Regression Technique”, Atmospheric Pollution Research, 436-444.  Archontoula Anitha K.G, Cynthia Carolin., (2015), “Assessment of Air Quality of Davangere City-A Case Study, ISSN; 2321-0869(O) 2454- 4698(P), Volume-3, Issue-8.  Chalouakou, Georgios Gravis., (2012), “Neural Network and Multiple Regression Models for PM10 Prediction in Athens; A Comparative Assessment”, Journal of the Air and Waste Management Association.  Gowtham Sarella.,(2015), “ Ambient Air Quality Analysis using Air Quality Index “ A Case Study of Vapi”, International Journal for Innovative Research in Science and Technology,Vol(1),pp:01.  Mohammad Shakir, N. Rakesh., “Investigation on Air Quality Pollutant Data Sets using Data Mining Tool”, IEEE Xplore Part Number: CFP 180ZV-ART; ISBN;978-1-5386-1442-6  Nidhi Sharma and Shwetha Taneja.,(2018), “ Forecasting Air Pollution Load in Dehli using Data Analysis Tools”, Science Direct, 132 1077-1085  Radhika M Patil and H. T Dinide., (2020), “A Literature Review on Prediction of Air Quality Index and Forecasting Ambient Air Pollutants using Machine Learning Algorihtms”.  R Gunasegaram, K. Kumarswamy., (2012) “Monitoring of Ambient Air Quality in Salem City, Tamil Nadu”, International Journal of Current Research, ISSN: 0975-833X, Vol .4, Issue 03, and pp: 275-280.  Tanushree Ganguly, Kurinji L. Selvaraj., “Review and Outlook of Clean Air and Action Plans”.