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Modern Geomatics Technologies and Applications

          of particulate matter less than 2.5 microns using machine learning algorithms and identified and selected effective meteorological
          parameters. Wei et al.[7] used support vector machine and artificial neural network methods to model the level of air pollution
          and proposed the support vector machine method as the superior method for modelling air pollution. Kurani et al.[8] used the
          network bayesian method for modelling ozone and PM2.5 pollutant.
               In previous research, to classify particulate matter pollution, in some cases only meteorological parameters have been
          considered and there was not enough attention to the most effective parameters and also in other cases only one method has been
          used for classification. Accordingly, there is no research that fully classifies the pollution class, compares them, and prepares the
          classification map by considering the most effective parameters using decision tree algorithms. In this research, an attempt has
          been made to pay the above issues. In this regard, in this study, CART and C4.5 decision tree algorithms were used to classify
          the concentration of suspended particles less than 2.5 microns and prepare a pollution classification map of the methods.


          2.  Study area and Dataset

               The city of Tehran is located in the southern foothills of the Alborz mountain range, the longitude between 51° 05′-51°
          53′East and latitude 35 ° 34 ′-35 ° 59′North with an area of about 700 square kilometers. The altitude of Tehran is between
          1050-2000 meters above the sea level. The period of data collection and research is related to the autumn season of 2017 and
          2018.

               This research uses several types of data:

               A)  Six-hour data of meteorological parameters, including relative humidity, rainfall, temperature, air pressure, wind
                   speed, wind direction of synoptic stations in Tehran province received from the Meteorological Organization of the
                   country.
               B)  Data related to PM2.5 pollutant concentration that is six hours from the station active measurements of air pollution
                   in Tehran received from the Air Quality Control Office of Tehran.
               C)  Related data to the topographic status of the whole city of Tehran received from the National Cartographic Center of
                   Iran (NCC).
               D)  Intensity of temperature inversion obtained for 12 hours from observational data of high atmosphere (extracted from
                   radio sound) by the website of the University of Wyoming[9].
               E)  All these parameters were determined next to a specific time unit (month of the year, day of the week, hour of the
                   day) and time dependence was considered for each parameter by creating a time series.



          3.  Proposed method

               The general trend of the proposed method is presented in Fig. 1. In this study, as shown in Fig. 1, by using the Kriging[10]
          interpolation method and considering the pixel size of 100 m on the ground, all parameters for the city of Tehran were created
          as several layers of information. Accordingly, all points of air pollution in Tehran in addition to all meteorological parameters
          were determined on time and concentration of pollutants. Another factor that affects air pollution is the temperature inversion
          [11]. Of course, temperature inversion in infected days is not the same amount and intensity, but in some days are different in
          terms of intensity and performance [12]. For this purpose, another parameter called inversion intensity is considered along with
          other parameters where the unit of it is the Celsius degree per hundred meters. To find this parameter, Equation (1) is used [13,
          14] as follows [14]:


                                                                
                                                            =    (1)
                                                                



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