<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">ACS</journal-id><journal-title-group><journal-title>Atmospheric and Climate Sciences</journal-title></journal-title-group><issn pub-type="epub">2160-0414</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/acs.2022.122025</article-id><article-id pub-id-type="publisher-id">ACS-116483</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Impact of Concentration Levels of Atmospheric Pollutants on Local Climate of Delta State, Nigeria
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Ifeanyi</surname><given-names>Innocent Onwosi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Emmanuel</surname><given-names>Fartiyahcha Nymphas</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Department of Physics, University of Ibadan, Ibadan, Nigeria</addr-line></aff><aff id="aff1"><addr-line>Department of Physics and Engineering, Delaware State University, Dover, DE, USA</addr-line></aff><pub-date pub-type="epub"><day>10</day><month>02</month><year>2022</year></pub-date><volume>12</volume><issue>02</issue><fpage>421</fpage><lpage>440</lpage><history><date date-type="received"><day>18,</day>	<month>February</month>	<year>2022</year></date><date date-type="rev-recd"><day>9,</day>	<month>April</month>	<year>2022</year>	</date><date date-type="accepted"><day>12,</day>	<month>April</month>	<year>2022</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Studies in various regions of the world have revealed that air pollution can have a significant influence on local climate. This study
   
  therefore
   
  considers the impact of concentration levels of atmospheric pollutants on local climate of Delta state, Nigeria. Monthly and annual averaging of the daily pollutant concentrations and meteorological parameters within the period of investigation was carried out. Descriptive Statistics, correlation analysis, coefficient of determination (R<sup>2</sup>) analysis and least squares regression analysis of the selected meteorological parameters with CH<sub>4</sub> and O<sub>3</sub> concentrations for the period of 2003 to 2012 and NO<sub>2</sub> and CO<sub>2</sub> concentrations for the period of 2011 to 2014 were carried out. The regression relationship was then used to obtain predicted values for the meteorological parameters within the period of investigation. The results of the descriptive statistics of annual averages of CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations within the period of investigation revealed that the emission levels breached FEPA and EGASPIN limits
  .<b> </b>
  The results of the correlation analysis indicated that CO<sub>2</sub> had a strong significant positive correlation with temperature with a correlation coefficient of 0.962, while a moderate negative correlation coefficient of 0.549 was obtained for CH<sub>4</sub>, and very weak correlation coefficients of -
  0.167 and 0.077 were obtained for O<sub>3</sub> and NO<sub>2</sub> respectively. CH<sub>4</sub>, O<sub>3</sub> and CO<sub>2</sub> had a moderately significant positive correlation with solar radiation with correlation coefficients of 0.661, 0.571 and 0.656 respectively, while a weak negative correlation coefficient of 0.106 was obtained for NO<sub>2</sub>. CH<sub>4</sub> had a strong significant positive correlation with relative humidity with a correlation coefficient of 0.859, while moderate correlation coefficients of -
  0.516 and 0.646 were obtained for NO<sub>2</sub> and CO<sub>2</sub> respectively, and a weak correlation coefficient of 0.345 was obtained for O<sub>3</sub>. CO<sub>2</sub> and CH<sub>4</sub> had a strong significant correlation with wind speed with correlation coefficients of 0.951 and -0.906 respectively, while a moderate negative correlation coefficient of 0.518 was obtained for O<sub>3</sub>, and a weak negative correlation coefficient of 0.317 was obtained for NO<sub>2</sub>. The predicted values of the meteorological parameters showed a significant level of agreement with their measured values. Therefore, among the atmospheric pollutants postulated as influencing meteorological parameters, CO<sub>2</sub> appears to be the most strongly significant in explaining temperature variations in this region of Niger Delta, with correlation coefficient of 96.2% and coefficient of determination (R<sup>2</sup>) of 0.926, implying that CO<sub>2</sub> influenced 92.6% variation in temperature in this part of Niger Delta within the period of investigation.
 
</p></abstract><kwd-group><kwd>Air Pollution</kwd><kwd> Atmospheric Pollutants</kwd><kwd> Local Climate</kwd><kwd> Meteorological Parameters</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Air pollution is a major environmental problem facing the Niger Delta region [<xref ref-type="bibr" rid="scirp.116483-ref1">1</xref>]. Air pollution is the contamination of the atmosphere by noxious gases and particulates.</p><p>Studies have revealed that air pollution can have a major effect on local climate [<xref ref-type="bibr" rid="scirp.116483-ref1">1</xref>]. Due to the spatial distributions of atmospheric pollutants with higher concentration levels mostly found near emission sources, variations in emission and concentration levels of air pollutants can cause a significant influence on local climate [<xref ref-type="bibr" rid="scirp.116483-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.116483-ref3">3</xref>] and in some situations regional climate by means of teleconnections in the atmosphere [<xref ref-type="bibr" rid="scirp.116483-ref4">4</xref>].</p><p>About 8 billion cubic meters of gas is flared yearly at various oil production sites in Nigeria [<xref ref-type="bibr" rid="scirp.116483-ref1">1</xref>]. It has been reported that the Niger Delta region of Nigeria has more than 123 gas flaring sites making Nigeria one of the major emitters of greenhouse gases in Africa [<xref ref-type="bibr" rid="scirp.116483-ref5">5</xref>]. Nigeria is accountable for almost one-sixth of the gas flared worldwide [<xref ref-type="bibr" rid="scirp.116483-ref6">6</xref>]. Nearly 75% of Nigeria’s natural gas is being flared and all occur in the Niger Delta region. The flares have contributed more greenhouse gases thereby causing climate change which could possibly lead to increased occurrence of flooding in the region [<xref ref-type="bibr" rid="scirp.116483-ref7">7</xref>].</p><p>There have been occurrences of acidified rain in the Niger Delta region due to the introduction of a high concentration of sulphur and oxides of nitrogen into the atmosphere [<xref ref-type="bibr" rid="scirp.116483-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.116483-ref9">9</xref>]. Combustion processes in gas flaring sites give rise to the emission of lower fractions of hydrocarbons and oxides of nitrogen and the presence of ultraviolet radiation produces smog which could cause a reduction in visibility [<xref ref-type="bibr" rid="scirp.116483-ref10">10</xref>].</p><p>About 45.8 billion kilowatts of heat are released into the atmosphere of the Niger-Delta from 1.8 billion ft<sup>3</sup> of gas daily [<xref ref-type="bibr" rid="scirp.116483-ref11">11</xref>]. Heat production destroys vegetation in the vicinity of the heat source [<xref ref-type="bibr" rid="scirp.116483-ref12">12</xref>]. [<xref ref-type="bibr" rid="scirp.116483-ref13">13</xref>] undertook a study on the analysis of carbon monoxide concentration levels with some selected meteorological parameters such as wind speed, relative humidity and temperature in ten major cities in the south eastern part of Nigeria. The result of the correlation analysis showed that out of all the meteorological parameters studied, only wind speed showed a strong correlation with carbon monoxide.</p><p>[<xref ref-type="bibr" rid="scirp.116483-ref14">14</xref>] undertook a study on the use of greenhouse gases as climate proxy data in explaining variability in climate. The standard deviation of CH<sub>4</sub> and CO<sub>2</sub> concentrations showed good correlations with the years associated with warming and can be used as good climate proxies. Furthermore, [<xref ref-type="bibr" rid="scirp.116483-ref15">15</xref>] carried out a study on the effect of meteorological parameters on distribution of atmospheric pollutants in Bayelsa State, Nigeria. The results revealed that wind speed showed a strong correlation with O<sub>3</sub> and CH<sub>4</sub> concentration levels.</p><p>Even though some amount of work has been done on the sources and distribution of air pollutants, so far, no major study has been undertaken on the effect of atmospheric pollutants on local climate in the Niger Delta. This work is aimed at increasing research efforts on understanding the association of atmospheric pollutants and related climate and environmental impacts in the Niger Delta Area.</p></sec><sec id="s2"><title>2. Study Station, Materials and Method</title><sec id="s2_1"><title>2.1. Study Station</title><p><xref ref-type="fig" rid="fig1">Figure 1</xref> is the map showing gas flaring sites and highlighting study station (Warri). The city of Warri (5.52˚N, 5.75˚E) is a major center of petroleum activities in</p><p>southern Nigeria. It has a population of over 311,970 (2006 census) [<xref ref-type="bibr" rid="scirp.116483-ref16">16</xref>]. The climate is marked by two different seasons: the rainy season (May to October) and the dry season (November to April). Over the course of the year, temperature typically varies from 20.56˚C to 31.11˚C and is rarely below 16.11˚C or above 33.33˚C. Rainfall periods vary from January to December with annual rainfall amount of about 2768.8 mm.</p></sec><sec id="s2_2"><title>2.2. Materials</title><p>Data description</p><p>The data on daily methane (CH<sub>4</sub>) with tropospheric ozone (O<sub>3</sub>) concentration levels (for the period of 2003 to 2012) and daily nitrogen dioxide (NO<sub>2</sub>) with carbon dioxide (CO<sub>2</sub>) concentration levels (for the period of 2011 to 2014) used in this study were obtained from the National Aeronautics and Space Administration (NASA). The data on meteorological parameters (wind speed, solar radiation, temperature and relative humidity) for the period of 2003 to 2014 were acquired from the Nigerian Meteorological Agency (NIMET), Lagos.</p></sec><sec id="s2_3"><title>2.3. Method</title><p>Monthly and annual averaging of the daily pollutant concentrations (NASA data) and meteorological parameters (NIMET data) within the period of investigation was carried out. The statistical analysis of weather parameters in this region of the Niger Delta with CH<sub>4</sub> and O<sub>3</sub> concentrations for the period of 2003 to 2012 and with NO<sub>2</sub> and CO<sub>2</sub> concentrations for the period of 2011 to 2014 were carried out. The regression relationship:</p><p>Y = a + b X (1)</p><p>was used to obtain predicted values for the meteorological parameters within the period of investigation, so that by comparing the level of agreement between the predicted and measured values, we could ascertain the reliability of the model in this part of Niger Delta. Where:</p><p>Y = meteorological parameter (predicted);</p><p>X = atmospheric pollutant concentration;</p><p>b and a are the slope and intercept respectively and are given as:</p><p>b = n Σ x y − Σ x Σ y n Σ x 2 − ( Σ x ) 2 (2)</p><p>a = Σ y n − b Σ x n (3)</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Average Annual Concentration Levels of the Atmospheric Pollutants and Meteorological Parameters</title><p><xref ref-type="table" rid="table1">Table 1</xref> shows the values of average annual concentration levels of CH<sub>4</sub> with O<sub>3</sub> for the period of 2003 to 2012 and selected meteorological parameters for the period of 2003 to 2014, while <xref ref-type="table" rid="table2">Table 2</xref> shows the values of average annual concentration</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Values of average annual concentration levels of CH<sub>4</sub> and O<sub>3</sub> for the period of 2003 to 2012 and selected meteorological parameters for the period of 2003 to 2014</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean CH<sub>4</sub> (ppmv)</th><th align="center" valign="middle" >Mean O<sub>3</sub> (ppmv)</th><th align="center" valign="middle" >Solar radiation (MJ/m<sup>2</sup>)</th><th align="center" valign="middle" >Relative humidity (%)</th><th align="center" valign="middle" >Temperature (˚C)</th><th align="center" valign="middle" >Wind speed (m/s)</th></tr></thead><tr><td align="center" valign="middle" >2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014</td><td align="center" valign="middle" >1740.994 1738.120 1737.331 1730.918 1740.740 1743.628 1750.178 1746.312 1759.923 1773.787</td><td align="center" valign="middle" >56.262 57.253 54.501 57.139 55.272 58.556 57.259 58.033 58.319 56.800</td><td align="center" valign="middle" >22.973 22.723 21.970 23.072 22.791 23.062 22.251 23.548 23.921 24.012 23.582 24.963</td><td align="center" valign="middle" >81.567 81.207 79.705 80.560 79.938 78.871 84.289 84.700 85.781 87.538 87.920 87.388</td><td align="center" valign="middle" >23.361 23.215 23.381 23.229 23.037 22.977 23.536 23.693 22.669 22.724 22.898 23.315</td><td align="center" valign="middle" >2.327 2.329 2.415 2.346 2.341 2.324 2.235 2.242 2.068 2.093 2.092 2.122</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Values of average annual concentration levels of NO<sub>2</sub> and CO<sub>2</sub> for the period of 2011 to 2014</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean NO<sub>2</sub> (ppmv)</th><th align="center" valign="middle" >Mean CO<sub>2</sub> (ppmv)</th></tr></thead><tr><td align="center" valign="middle" >2011 2012 2013 2014</td><td align="center" valign="middle" >135.695 127.516 133.934 132.747</td><td align="center" valign="middle" >382.370 385.108 388.111 392.186</td></tr></tbody></table></table-wrap><p>levels of NO<sub>2</sub> and CO<sub>2</sub> with selected meteorological parameters for the period of 2011 to 2014.</p></sec><sec id="s3_2"><title>3.2. Descriptive Statistics of the Atmospheric Pollutants and Selected Meteorological Parameters</title><p><xref ref-type="table" rid="table3">Table 3</xref> shows the descriptive statistics of annual averages of CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations, while <xref ref-type="table" rid="table4">Table 4</xref> shows the descriptive statistics of annual averages of selected meteorological parameters.</p></sec><sec id="s3_3"><title>3.3. Impact of the Atmospheric Pollutants Concentration on Meteorological Parameters</title><p>The impact of the concentration of atmospheric pollutants on selected meteorological parameters was determined using correlation analysis, coefficient of determination (R<sup>2</sup>) analysis and least squares regression analysis.</p><sec id="s3_3_1"><title>3.3.1. Correlation Analysis</title><p><xref ref-type="table" rid="table5">Table 5</xref> shows the correlation coefficients between selected meteorological parameters and CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations.</p><p>Figures 2(a)-(d) show temperature correlation with CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations respectively, Figures 3(a)-(d) show solar radiation correlation</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Descriptive statistics of annual averages of CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations within the period of investigation</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle" >Mean</th><th align="center" valign="middle" >Standard Deviation</th><th align="center" valign="middle" >Minimum</th><th align="center" valign="middle" >Maximum</th></tr></thead><tr><td align="center" valign="middle" >CH<sub>4</sub> (ppmv) O<sub>3</sub> (ppmv) NO<sub>2</sub> (ppmv) CO<sub>2</sub> (ppmv)</td><td align="center" valign="middle" >1746.193 56.939 132.473 386.944</td><td align="center" valign="middle" >12.500 1.300 3.519 4.208</td><td align="center" valign="middle" >1730.918 54.501 127.516 380.139</td><td align="center" valign="middle" >1773.787 58.556 135.695 392.186</td></tr></tbody></table></table-wrap><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Descriptive statistics of annual averages of selected meteorological parameters within the period of 2003 to 2014</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle" >Mean</th><th align="center" valign="middle" >Standard Deviation</th><th align="center" valign="middle" >Minimum</th><th align="center" valign="middle" >Maximum</th></tr></thead><tr><td align="center" valign="middle" >Solar radiation (MJ/m<sup>2</sup>) Relative humidity (%) Temperature (˚C) Wind speed (m/s)</td><td align="center" valign="middle" >23.239 83.289 23.170 2.245</td><td align="center" valign="middle" >0.822 3.355 0.315 0.121</td><td align="center" valign="middle" >21.970 78.871 22.669 2.068</td><td align="center" valign="middle" >24.963 87.920 23.693 2.415</td></tr></tbody></table></table-wrap><table-wrap id="table5" ><label><xref ref-type="table" rid="table5">Table 5</xref></label><caption><title> Correlation coefficients between selected meteorological parameters (dependent variables) and CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations (independent variables) within the period of investigation</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle" >CH<sub>4</sub> (ppmv)</th><th align="center" valign="middle" >O<sub>3</sub> (ppmv)</th><th align="center" valign="middle" >NO<sub>2</sub> (ppmv)</th><th align="center" valign="middle" >CO<sub>2</sub> (ppmv)</th></tr></thead><tr><td align="center" valign="middle" >Solar radiation (MJ/m<sup>2</sup>) Relative humidity (%) Temperature (˚C) Wind speed (m/s)</td><td align="center" valign="middle" >0.661* 0.859* −0.549 −0.906</td><td align="center" valign="middle" >0.571 0.345 −0.167 −0.518</td><td align="center" valign="middle" >−0.106 −0.516 0.077 −0.317</td><td align="center" valign="middle" >0.656 0.646 0.962* 0.951*</td></tr></tbody></table></table-wrap><p>with CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations respectively, Figures 4(a)-(d) show relative humidity correlation with CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations respectively, while Figures 5(a)-(d) show wind speed correlation with CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations respectively.</p></sec><sec id="s3_3_2"><title>3.3.2. Coefficient of Determination (R<sup>2</sup>) and Least Squares Regression Analysis</title><p>Figures 6(a)-(d) to Figures 9(a)-(d) show the coefficient of determination (R<sup>2</sup>) of the selected meteorological parameters with the concentration of atmospheric pollutants.</p><p>1) Coefficient of determination (R<sup>2</sup>) analysis</p><p>The coefficient of determination analysis gives us the measure of the variation in the meteorological parameters (dependent variable) that is predictable from the atmospheric pollutants (independent variable).</p><p>Methane (CH<sub>4</sub>) had coefficients of determination (R<sup>2</sup>) of 0.820, 0.738, 0.437 and 0.302 with wind speed, relative humidity, solar radiation and temperature respectively. Tropospheric ozone (O<sub>3</sub>) had coefficients of determination (R<sup>2</sup>) of 0.326, 0.268, 0.119 and 0.028 with solar radiation, wind speed, relative humidity and temperature respectively. Nitrogen dioxide (NO<sub>2</sub>) had coefficients of determination (R<sup>2</sup>) of 0.266, 0.101, 0.011 and 0.006 with relative humidity, wind speed, solar radiation and temperature respectively. Carbon dioxide (CO<sub>2</sub>) had coefficients of determination (R<sup>2</sup>) of 0.926, 0.904, 0.430 and 0.417 with temperature, wind speed, solar radiation and relative humidity respectively.</p><p>2) Least squares regression analysis</p><p>The Least squares regression analysis gives us the line of best fit enabling us to predict the behavior of the meteorological parameters.</p><p>CO<sub>2</sub> had the highest R<sup>2</sup> of 0.926 with temperature, as shown in <xref ref-type="fig" rid="fig6">Figure 6</xref>(d). To obtain predicted values for temperature, we substitute the values of a (intercept) and b (slope) from <xref ref-type="fig" rid="fig6">Figure 6</xref>(d) into the regression relationship Y = a + b X , where Y is temperature (predicted) and X is CO<sub>2</sub> concentration to obtain Equation (4) as:</p><p>Temperature = − 2.972 + 0.067 ( CO 2 ) (4)</p><p>Therefore by substituting the values of CO<sub>2</sub> concentration into Equation (4), we obtain predicted values for temperature within the period of investigation. <xref ref-type="table" rid="table6">Table 6</xref> shows predicted and measured values of temperature, while <xref ref-type="fig" rid="fig1">Figure 1</xref>0 shows the graph of predicted and measured values of temperature.</p><p>CH<sub>4</sub> had the highest R<sup>2</sup> of 0.437 with solar radiation, as shown in <xref ref-type="fig" rid="fig7">Figure 7</xref>(a). To obtain predicted values for solar radiation, we substitute the values of a (intercept) and b (slope) from <xref ref-type="fig" rid="fig7">Figure 7</xref>(a) into the regression relationship Y = a + b X , where Y is solar radiation (predicted) and X is CH<sub>4</sub> concentration to obtain Equation (5) as:</p><p>Solar   radiation = − 37.859 + 0.035 ( CH 4 ) (5)</p><p>Therefore by substituting the values of CH<sub>4</sub> concentration into Equation (5),</p><table-wrap id="table6" ><label><xref ref-type="table" rid="table6">Table 6</xref></label><caption><title> Predicted and measured values of temperature</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean CO<sub>2</sub> (ppmv)</th><th align="center" valign="middle" >Temperature ˚C (measured)</th><th align="center" valign="middle" >Temperature ˚C (predicted)</th></tr></thead><tr><td align="center" valign="middle" >2011 2012 2013 2014</td><td align="center" valign="middle" >382.370 385.108 388.111 392.186</td><td align="center" valign="middle" >22.669 22.724 22.898 23.315</td><td align="center" valign="middle" >22.647 22.830 23.031 23.304</td></tr></tbody></table></table-wrap><p>we obtain predicted values for solar radiation within the period of investigation. <xref ref-type="table" rid="table7">Table 7</xref> shows predicted and measured values of solar radiation, while <xref ref-type="fig" rid="fig1">Figure 1</xref>1 shows the graph of predicted and measured values of solar radiation.</p><table-wrap id="table7" ><label><xref ref-type="table" rid="table7">Table 7</xref></label><caption><title> Predicted and measured values of solar radiation</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean CH<sub>4</sub> (ppmv)</th><th align="center" valign="middle" >Solar radiation MJ/m<sup>2</sup> (measured)</th><th align="center" valign="middle" >Solar radiation MJ/m<sup>2</sup> (predicted)</th></tr></thead><tr><td align="center" valign="middle" >2003 2004 2005 2006 2007 2008 2009 2010 2011 2012</td><td align="center" valign="middle" >1740.994 1738.120 1737.331 1730.918 1740.740 1743.628 1750.178 1746.312 1759.923 1773.787</td><td align="center" valign="middle" >22.973 22.723 21.970 23.072 22.791 23.062 22.251 23.548 23.921 24.012</td><td align="center" valign="middle" >23.076 22.975 22.948 22.723 23.069 23.168 23.397 23.262 23.738 24.224</td></tr></tbody></table></table-wrap><p>CH<sub>4</sub> had the highest R<sup>2</sup> of 0.738 with relative humidity, as shown in <xref ref-type="fig" rid="fig8">Figure 8</xref>(a). To obtain predicted values for relative humidity, we substitute the values of a (intercept) and b (slope) from <xref ref-type="fig" rid="fig8">Figure 8</xref>(a) into the regression relationship Y = a + b X , where Y is relative humidity (predicted) and X is CH<sub>4</sub> concentration to obtain Equation (6) as:</p><p>Relative   humidity = − 270.779 + 0.202 ( CH 4 ) (6)</p><p>Therefore by substituting the values of CH<sub>4</sub> concentration into Equation (6), we obtain predicted values for relative humidity within the period of investigation. <xref ref-type="table" rid="table8">Table 8</xref> shows predicted and measured values of relative humidity, while <xref ref-type="fig" rid="fig1">Figure 1</xref>2 shows the graph of predicted and measured values of relative humidity.</p><p>CO<sub>2</sub> had the highest R<sup>2</sup> of 0.904 with wind speed, as shown in <xref ref-type="fig" rid="fig9">Figure 9</xref>(d). To obtain predicted values for wind speed, we substitute the values of a (intercept) and b (slope) from <xref ref-type="fig" rid="fig9">Figure 9</xref>(d) into the regression relationship Y = a + b X , where Y is wind speed (predicted) and X is CO<sub>2</sub> concentration to obtain equation (7) as:</p><table-wrap id="table8" ><label><xref ref-type="table" rid="table8">Table 8</xref></label><caption><title> Predicted and measured values of relative humidity</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean CH<sub>4</sub> (ppmv)</th><th align="center" valign="middle" >Relative humidity % (measured)</th><th align="center" valign="middle" >Relative humidity % (predicted)</th></tr></thead><tr><td align="center" valign="middle" >2003 2004 2005 2006 2007 2008 2009 2010 2011 2012</td><td align="center" valign="middle" >1740.994 1738.120 1737.331 1730.918 1740.740 1743.628 1750.178 1746.312 1759.923 1773.787</td><td align="center" valign="middle" >81.567 81.207 79.705 80.560 79.938 78.871 84.289 84.700 85.781 87.538</td><td align="center" valign="middle" >80.902 80.321 80.162 78.866 80.850 81.434 82.757 81.976 84.725 87.526</td></tr></tbody></table></table-wrap><p>Wind   speed = 0.162 + 0.005 ( CO 2 ) (7)</p><p>Therefore by substituting the values of CO<sub>2</sub> concentration into Equation (7), we obtain predicted values for wind speed within the period of investigation. <xref ref-type="table" rid="table9">Table 9</xref> shows predicted and measured values of wind speed, while <xref ref-type="fig" rid="fig1">Figure 1</xref>3 shows the graph of predicted and measured values of wind speed.</p></sec></sec><sec id="s3_4"><title>3.4. Discussion</title><p>The results of the descriptive statistics of annual averages of selected meteorological parameters within the period of investigation showed that relative humidity had the highest standard deviation value of 3.355%, while wind speed had the lowest standard deviation value of 0.121 m/s. Solar radiation and temperature had standard deviation values of 0.822 MJ/m<sup>2</sup> and 0.315˚C respectively.</p><table-wrap id="table9" ><label><xref ref-type="table" rid="table9">Table 9</xref></label><caption><title> Predicted and measured values of wind speed</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Year</th><th align="center" valign="middle" >Mean CO<sub>2</sub> (ppmv)</th><th align="center" valign="middle" >Wind speed m/s (measured)</th><th align="center" valign="middle" >Wind speed m/s (predicted)</th></tr></thead><tr><td align="center" valign="middle" >2011 2012 2013 2014</td><td align="center" valign="middle" >382.370 385.108 388.111 392.186</td><td align="center" valign="middle" >2.068 2.093 2.092 2.122</td><td align="center" valign="middle" >2.074 2.088 2.103 2.123</td></tr></tbody></table></table-wrap><p>Therefore relative humidity values were the most dispersed or spread out around the mean of 83.289%, while wind speed values were the least dispersed around the mean of 2.245 m/s.</p><p>The results of the descriptive statistics of annual averages of CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations within the period of investigation revealed that the mean values were higher than the acceptable ambient values [<xref ref-type="bibr" rid="scirp.116483-ref17">17</xref>]. The continuous increase in concentration level of these pollutants is due to the activities of the artisanal petroleum refineries in the Niger Delta region. The emission levels of these pollutants breached FEPA and EGASPIN limits [<xref ref-type="bibr" rid="scirp.116483-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.116483-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.116483-ref20">20</xref>]. The results also showed that CH<sub>4</sub> had the highest standard deviation value of 12.500 ppmv while O<sub>3</sub> had the lowest standard deviation value of 1.300 ppmv. NO<sub>2</sub> and CO<sub>2</sub> had standard deviation values of 3.519 ppmv and 4.208 ppmv respectively. Therefore CH<sub>4</sub> concentration values were the most dispersed or spread out around the mean of 1746.193 ppmv, while O<sub>3</sub> concentration values were the least dispersed around the mean of 56.939 ppmv. Methane (CH<sub>4</sub>) had higher standard deviation (S.D) values than carbon dioxide (CO<sub>2</sub>), showing that on a per molecule basis, proportional rise in CH<sub>4</sub> concentration is much more efficient as a greenhouse gas than a comparable rise in CO<sub>2</sub> concentration [<xref ref-type="bibr" rid="scirp.116483-ref14">14</xref>]. However, CO<sub>2</sub> has a greater influence than CH<sub>4</sub> on climate change due to its higher atmospheric concentration.</p><p>The results of the correlation analysis between the selected meteorological parameters (dependent variables) and CH<sub>4</sub>, O<sub>3</sub>, NO<sub>2</sub> and CO<sub>2</sub> concentrations (independent variables) within the period of investigation as shown in <xref ref-type="table" rid="table5">Table 5</xref>, indicated that CO<sub>2</sub> had a strong significant positive correlation with temperature with a correlation coefficient of 0.962, while a moderate negative correlation coefficient of 0.549 was obtained for CH<sub>4</sub>, and very weak correlation coefficients of −0.167 and 0.077 were obtained for O<sub>3</sub> and NO<sub>2</sub> respectively. Therefore, among the atmospheric pollutants postulated as influencing temperature, CO<sub>2</sub> appears to be the most strongly significant (P &lt; 0.05) in explaining temperature variations in this region of Niger Delta, with a correlation coefficient of 96.2%. CH<sub>4</sub>, O<sub>3</sub> and CO<sub>2</sub> had a moderately significant positive correlation with solar radiation with correlation coefficients of 0.661, 0.571 and 0.656 respectively, while a weak negative correlation coefficient of 0.106 was obtained for NO<sub>2.</sub> Therefore, among the atmospheric pollutants postulated as influencing solar radiation, CH<sub>4</sub> appears to be the most strongly significant (P &lt; 0.05) in explaining variations in solar radiation in this region of Niger Delta, with a correlation coefficient of 66.1%. CH<sub>4</sub> had a strong significant positive correlation with relative humidity with a correlation coefficient of 0.859, while moderate correlation coefficients of −0.516 and 0.646 were obtained for NO<sub>2</sub> and CO<sub>2</sub> respectively, and a weak correlation coefficient of 0.345 was obtained for O<sub>3</sub>. Therefore, among the atmospheric pollutants postulated as influencing relative humidity, CH<sub>4</sub> appears to be the most strongly significant (P &lt; 0.01) in explaining variations in relative humidity in this region of Niger Delta, with a correlation coefficient of 85.9%. CO<sub>2</sub> and CH<sub>4</sub> had a strong significant correlation with wind speed with correlation coefficients of 0.951 and −0.906 respectively, while a moderate negative correlation coefficient of 0.518 was obtained for O<sub>3</sub>, and a weak negative correlation coefficient of 0.317 was obtained for NO<sub>2</sub>. Therefore, among the atmospheric pollutants postulated as influencing wind speed, CO<sub>2</sub> appears to be the most strongly significant (P &lt; 0.05) in explaining variations in wind speed in this region of Niger Delta, with a correlation coefficient of 95.1%.</p><p>The results of the coefficient of determination (R<sup>2</sup>) analysis revealed that Methane (CH<sub>4</sub>) had coefficients of determination (R<sup>2</sup>) of 0.820, 0.738, 0.437 and 0.302 with wind speed, relative humidity, solar radiation and temperature respectively. This implies that CH<sub>4</sub> influenced 82.0% variation in wind speed, 73.8% variation in relative humidity, 43.7% variation in solar radiation and 30.2% variation in temperature in this region of Niger Delta within the period of investigation. Tropospheric ozone (O<sub>3</sub>) had coefficients of determination (R<sup>2</sup>) of 0.326, 0.268, 0.119 and 0.028 with solar radiation, wind speed, relative humidity and temperature respectively. This implies that O<sub>3</sub> influenced 32.6% variation in solar radiation, 26.8% variation in wind speed, 11.9% variation in relative humidity and 2.8% variation in temperature in this part of Niger Delta within the period of investigation. Nitrogen dioxide (NO<sub>2</sub>) had coefficients of determination (R<sup>2</sup>) of 0.266, 0.101, 0.011 and 0.006 with relative humidity, wind speed, solar radiation and temperature respectively. This implies that NO<sub>2</sub> influenced 26.6% variation in relative humidity, 10.1% variation in wind speed, 1.1% variation in solar radiation and 0.6% variation in temperature in this region of Niger Delta within the period of investigation. Carbon dioxide (CO<sub>2</sub>) had coefficients of determination (R<sup>2</sup>) of 0.926, 0.904, 0.430 and 0.417 with temperature, wind speed, solar radiation and relative humidity respectively. This implies that CO<sub>2</sub> influenced 92.6% variation in temperature, 90.4% variation in wind speed, 43.0% variation in solar radiation and 41.7% variation in relative humidity in this part of Niger Delta within the period of investigation.</p><p>The predicted values of the meteorological parameters showed a significant level of agreement with their measured values as shown in Figures 10-13.</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>Changes in emission and concentration levels of atmospheric pollutants can significantly affect local climate and in some situations regional climate by means of teleconnections in the atmosphere. Among the atmospheric pollutants postulated as influencing meteorological parameters, CO<sub>2</sub> appears to be the most strongly significant in explaining temperature variations in this region of Niger Delta, with a correlation coefficient of 96.2% and a coefficient of determination (R<sup>2</sup>) of 0.926, implying that CO<sub>2</sub> influenced 92.6% variation in temperature in this part of Niger Delta within the period of investigation. The emission levels of the atmospheric pollutants breached FEPA and EGASPIN limits.</p></sec><sec id="s5"><title>Acknowledgements</title><p>I. I. Onwosi gratefully thanks Dr. Chinonyelum Vivian Onwosi for being his source of inspiration. The authors gratefully acknowledge the valuable discussions with Emmanuel Iruka Njoku.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Onwosi, I.I. and Nymphas, E.F. (2022) Impact of Concentration Levels of Atmospheric Pollutants on Local Climate of Delta State, Nigeria. Atmospheric and Climate Sciences, 12, 421-440. https://doi.org/10.4236/acs.2022.122025</p></sec></body><back><ref-list><title>References</title><ref id="scirp.116483-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Chuwah, C. and Santillo, D. (2017) Air Pollution due to Gas Flaring in the Niger Delta: A Review of Current State of Knowledge. Greenpeace Research Laboratories Technical Report, University of Exeter, Exeter, UK.</mixed-citation></ref><ref id="scirp.116483-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Chen, W.T., Liao, H. and Seinfeld, J.H. (2007) Future Climate Impacts of Direct Radiative Forcing of Anthropogenic Aerosols, Tropospheric Ozone, and Long-Lived Greenhouse Gases. Journal of Geophysical Research, 112, D14209. https://doi.org/10.1029/2006JD008051</mixed-citation></ref><ref id="scirp.116483-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Shindell, D., Kuylenstierna, J.C., Vignati, E., van Dingenen, R., Amann, M., Klimont, Z., Anenberg, S.C., Muller, N., Maenhout, G.J., Raes, F., Schwartz, J., Faluvegi, G., Pozzoli, L., Kupiainen, K., Isaksson, L.H., Emberson, L., Streets, D., Ramanathan, V., Hicks, K., Oanh, N.K., Milly, G., Williams, M., Demkine, V. and Fowler, D. (2012) Simultaneously Mitigating Near-Term Climate Change and Improving Human Health and Food Security. Science, 335, 183-189. https://doi.org/10.1126/science.1210026</mixed-citation></ref><ref id="scirp.116483-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Chuwah, C., van Noije, T., van Vuuren, D.P., Le Sager, P. and Hazeleger, W. (2016) Climate Impacts of Future Aerosol Mitigation in an RCP6.0-Like Scenario. Climatic Change, 134, 1-14. https://doi.org/10.1007/s10584-015-1525-9</mixed-citation></ref><ref id="scirp.116483-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Akinro, A.O., Opeyemi, D.A. and Ologunagba, I.B. (2008) Climate Change and Environmental Degradation in the Niger Delta Region of Nigeria: Its Vulnerability, Impacts and Possible Mitigations. Research Journal of Applied Sciences, 3, 167-173.</mixed-citation></ref><ref id="scirp.116483-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">World Bank (2008) World Bank Development Report: Agriculture for Development. World Bank, Washington, DC.</mixed-citation></ref><ref id="scirp.116483-ref7"><label>7</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Nzeadibe</surname><given-names> T.C.</given-names></name>,<name name-style="western"><surname> Egbule C.L.</surname><given-names> Chukwuone</given-names></name>,<name name-style="western"><surname> N.A. and Agu</surname><given-names> V.C. </given-names></name>,<etal>et al</etal>. (<year>2011</year>)<article-title>Climate Change Awareness and Adaptation in the Niger Delta Region of Nigeria</article-title><source> African Technology Policy Studies Network</source><volume> 57</volume>,<fpage> 7</fpage>-<lpage>27</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.116483-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Olobaniyi, S.B. and Efe, S.I. (2007) Comparative Assessment of Rainwater and Groundwater Quality in an Oil Producing Area of Nigeria: Environmental and Health Implications. Journal of Environmental Health Research, 6, 111-118.</mixed-citation></ref><ref id="scirp.116483-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Akpoborie, I.A., Ekakite, A.O. and Adaikpoh, E.O. (2000) The Quality of Groundwater from Dug Wells in Parts of the Western Niger Delta. Knowledge Review, 2, 72-79.</mixed-citation></ref><ref id="scirp.116483-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Tawari, C.C. and Abowei, J.F.N. (2012) Air Pollution in the Niger Delta Area of Nigeria. International Journal of Fisheries and Aquatic Sciences, 1, 94-117.</mixed-citation></ref><ref id="scirp.116483-ref11"><label>11</label><mixed-citation publication-type="book" xlink:type="simple">Aaron, K.K. (2006) Human Rights Violation and Environmental Degradation in the Niger-Delta. In: Elizabeth P. and O. Baden, Eds., Activating Human Rights, Barne, Oxford, New York.</mixed-citation></ref><ref id="scirp.116483-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Ogbuigwe, A. (1998) Judicial Activism in the Enforcement of Environmental Regulations in the Petroleum Industry: Past, Present and the Future. Proceedings of 1998 International Conference on the Petroleum and the Nigerian Environment, 83-123.</mixed-citation></ref><ref id="scirp.116483-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Ngele, S.O., Eboatu, A.N. and Onwu, F.K. (2012) Preliminary Study of the Influence of Some Meteorological Parameters on the Concentration of CO in South Eastern Part of Nigeria. Chemical Science Transactions, 1, 702-708. https://doi.org/10.7598/cst2012.4395</mixed-citation></ref><ref id="scirp.116483-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Ogunsola, O.E. and Oladiran, E.O. (2013) The Use of Greenhouse Gases as Climate Proxy Data in Interpreting Climatic Variability. Atmospheric and Climate Sciences, 3, 6-10. https://doi.org/10.4236/acs.2013.31002</mixed-citation></ref><ref id="scirp.116483-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Njoku, E.I., Ogunsola, O.E. and Oladiran, E.O. (2019) The Influence of Atmospheric Parameters on Production and Distribution of Air Pollutants in Bayelsa: A State in the Niger Delta Region of Nigeria. Atmospheric and Climate Sciences, 9, 159-171. https://doi.org/10.4236/acs.2019.91011</mixed-citation></ref><ref id="scirp.116483-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">National Population Commission (NPC) (2010) Federal Republic of Nigeria (2006) Population and Housing Census. Priority Table Volume IV, Population Distribution by Age and Sex. National Population Commission (NPC), Abuja.</mixed-citation></ref><ref id="scirp.116483-ref17"><label>17</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Akuro</surname><given-names> A. </given-names></name>,<etal>et al</etal>. (<year>2012</year>)<article-title>Air Quality Survey of Some Locations in the Niger Delta Area</article-title><source> Journal of Applied Science and Environmental Management</source><volume> 16</volume>,<fpage> 137</fpage>-<lpage>146</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.116483-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Onakpohor, A., Fakinle, B.S., Sonibare, J.A., Oke, M.A. and Akeredolu, F.A. (2020) Investigation of Air Emissions from Artisanal Petroleum Refineries in the Niger-Delta Nigeria. Heliyon, 6, e05608. https://doi.org/10.1016/j.heliyon.2020.e05608</mixed-citation></ref><ref id="scirp.116483-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Federal Environmental Protection Agency (FEPA) (1991) Guidelines and standards for Environmental pollution control in Nigeria. FEPA, Lagos.</mixed-citation></ref><ref id="scirp.116483-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">EGASPIN (2002) Environmental Guidelines and Standards for the Petroleum Industry in Nigeria (EGASPIN). Department of Petroleum Resources, Lagos, Nigeria.</mixed-citation></ref></ref-list></back></article>