<?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">OALibJ</journal-id><journal-title-group><journal-title>Open Access Library Journal</journal-title></journal-title-group><issn pub-type="epub">2333-9705</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/oalib.1107454</article-id><article-id pub-id-type="publisher-id">OALibJ-109520</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject><subject> Business&amp;Economics</subject><subject> Chemistry&amp;Materials Science</subject><subject> Computer Science&amp;Communications</subject><subject> Earth&amp;Environmental Sciences</subject><subject> Engineering</subject><subject> Medicine&amp;Healthcare</subject><subject> Physics&amp;Mathematics</subject><subject> Social Sciences&amp;Humanities</subject></subj-group></article-categories><title-group><article-title>
 
 
  Aviation Noise and Air Pollution: Results of a Study at Entebbe International Airport, Uganda
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Austine</surname><given-names>Omolo</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>Christopher</surname><given-names>Angiro</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Waganesh</surname><given-names>Admase Wagaye</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Elly</surname><given-names>Olomo</given-names></name><xref ref-type="aff" rid="aff4"><sup>4</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Jasper</surname><given-names>Okino</given-names></name><xref ref-type="aff" rid="aff5"><sup>5</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Timothy</surname><given-names>Omara</given-names></name><xref ref-type="aff" rid="aff6"><sup>6</sup></xref></contrib></contrib-group><aff id="aff3"><addr-line>Department of Mechanical Engineering, Arba Minch University, Arba Minch, Ethiopia</addr-line></aff><aff id="aff5"><addr-line>Department of Mechanical, Production and Energy Engineering, School of Engineering, Moi University, Eldoret, Kenya</addr-line></aff><aff id="aff2"><addr-line>National Livestock Resources Research Institute, National Agricultural Research Organization, Kampala, Uganda</addr-line></aff><aff id="aff6"><addr-line>Department of Chemistry and Biochemistry, School of Sciences and Aerospace Studies, Moi University, Eldoret, Kenya</addr-line></aff><aff id="aff4"><addr-line>Africa Center of Excellence II in Phytochemicals, Textile and Renewable Energy (ACE II PTRE), Moi University, Eldoret, Kenya</addr-line></aff><aff id="aff1"><addr-line>Department of Chemistry, Faculty of Science, Kyambogo University, Kampala, Uganda</addr-line></aff><pub-date pub-type="epub"><day>06</day><month>05</month><year>2021</year></pub-date><volume>08</volume><issue>05</issue><fpage>1</fpage><lpage>13</lpage><history><date date-type="received"><day>25,</day>	<month>April</month>	<year>2021</year></date><date date-type="rev-recd"><day>25,</day>	<month>May</month>	<year>2021</year>	</date><date date-type="accepted"><day>28,</day>	<month>May</month>	<year>2021</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>
 
 
  For a landlocked country like Uganda, air transport is centermost to its import-export trade. As such, the aviation industry is important for its economic and political survival since it guarantees access to the outside world. This study reports on the noise and air pollution levels at Entebbe International Airport, Uganda. We found that the airport experiences irregular noise frequencies with the midday having the highest noise intensities that exceed permissible limits of 60 decibels. Carbon dioxide is the highest air pollutant produced at the airport probably due to anthropogenic emissions from both aviation and vehicular activities. Based on particulate matter (PM2.5 and PM10) the air quality index was less than 50, indicating that the air quality was good. Therefore, the aviation authorities need to ensure that these air pollutants are monitored and controlled continuously. The expansion of EBB alongside the development of residential areas might amplify noise and air pollution if cleaner technologies are not embraced. Further studies should perform audiogram assessments (acoustic estimation of noise-induced hearing loss) at the airport.
 
</p></abstract><kwd-group><kwd>Ambient Air Quality</kwd><kwd> Carbon Monoxide</kwd><kwd> Hydrogen Sulphide</kwd><kwd> Particulate Matter</kwd><kwd> Volatile Organic Compounds</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Pollution is a pressing multi-sectoral challenge implicated in the progression of the decadal climate change [<xref ref-type="bibr" rid="scirp.109520-ref1">1</xref>]. Particularly, air and noise pollution present health, economic and social threats to countries globally [<xref ref-type="bibr" rid="scirp.109520-ref1">1</xref>]. There are now growing concerns by global aviation authorities and environmentalists that airports have substantial contributions to environmental pollution [<xref ref-type="bibr" rid="scirp.109520-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref3">3</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref5">5</xref>]. They have been implicated for various ecological issues relating to acid rain, climate change, tropospheric ozone and potential risks linked to regional, ecological, environmental and public health [<xref ref-type="bibr" rid="scirp.109520-ref6">6</xref>]. For example, aircraft emissions of pollutants such as carbon dioxide, sulphur dioxide and volatile organic compounds are known to contribute to the atmospheric pool of greenhouse gases [<xref ref-type="bibr" rid="scirp.109520-ref3">3</xref>]. Aircraft air pollutant emissions are grossly categorized into 1) emissions during the landing and take-off (LTO) cycle and 2) those during the non-LTO flight cycle [<xref ref-type="bibr" rid="scirp.109520-ref3">3</xref>]. The former produce emissions with prominent impacts compared with the latter [<xref ref-type="bibr" rid="scirp.109520-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref9">9</xref>]. Increase in air transport volumes and expansion of airports to meet future capacity needs have made aircraft emissions during the LTO more prominent and of general research interest [<xref ref-type="bibr" rid="scirp.109520-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref12">12</xref>].</p><p>Previous advances to establish air quality in Uganda and East Africa at large have been impeded by inadequate regulatory grade equipment required to record long term data and track vacillations in air pollution both temporally and spatially, as well as assess their influences on public health [<xref ref-type="bibr" rid="scirp.109520-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref14">14</xref>]. This is primarily due to the prohibitive cost of air quality monitoring equipment, and the difficulty in obtaining appropriate calibration and certification services [<xref ref-type="bibr" rid="scirp.109520-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref17">17</xref>]. Despite the paucity of air quality data, previous studies indicate that air pollution is an environmental concern that has undermined the development of safe, inclusive, resilient and sustainable cities [<xref ref-type="bibr" rid="scirp.109520-ref13">13</xref>]. A Systems Approach to Air Pollution (ASAP)-East Africa team has supplemented available long-term air quality monitoring with spot measurement campaigns at selected sites including outdoor and indoor locations in Uganda [<xref ref-type="bibr" rid="scirp.109520-ref14">14</xref>].</p><p>On the other hand, aircrafts contribute to noise pollution particularly during take-off and landing [<xref ref-type="bibr" rid="scirp.109520-ref18">18</xref>]. Ideally, airports should be away from human habitation so that people are not affected by the noise caused by the air traffic [<xref ref-type="bibr" rid="scirp.109520-ref19">19</xref>]. However, this is not the case in many countries, where human habitation is in close proximity to airports [<xref ref-type="bibr" rid="scirp.109520-ref20">20</xref>]. People who live away from airports but under the flight path may also get disturbed by high noise levels [<xref ref-type="bibr" rid="scirp.109520-ref21">21</xref>]. Noise arising from aviation activities has been implicated in the etiology and aggravation of cardiovascular diseases, hypertension, psychological ill-health, lowering of cognitive ability in children, annoyance and sleep disturbances [<xref ref-type="bibr" rid="scirp.109520-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref23">23</xref>]. In the current study, we report on the concentration of some priority air pollutants and noise pollution levels at Entebbe International Airport (EBB), Uganda.</p></sec><sec id="s2"><title>2. Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p>Entebbe Airport is the principal and only Ugandan international airport. It is situated approximately six kilometers Southwest of Entebbe town at coordinates 00˚02'33&quot;N 32˚26'37&quot;E [<xref ref-type="bibr" rid="scirp.109520-ref24">24</xref>]. Located on the Northern shores of Lake Victoria (<xref ref-type="fig" rid="fig1">Figure 1</xref>), the airport is more than 30 kilometers away and South West of the central business district and capital city of Uganda (Kampala) [<xref ref-type="bibr" rid="scirp.109520-ref25">25</xref>]. The airport is straddled by equator at latitude 00.020 North and longitude 320 East, for which reason it is described as the “Airport on the Equator” [<xref ref-type="bibr" rid="scirp.109520-ref26">26</xref>]. At about 3782 feet above sea level, the airport is part of a peninsular bordering Africa’s biggest fresh water-Lake Victoria.</p></sec><sec id="s2_2"><title>2.2. Determination of Noise Levels</title><p>Noise levels were determined using a Castle GA112 octave band sound level meter (Castle Advanced Solutions, UK). Noise levels were measured thrice daily by giving a time range of 4 hours from the initial test (i.e. at 8:00 am, 12:00 pm and 4:00 pm). This is because noise intensity is dispersed very easily and therefore it cannot be taken at close intervals [<xref ref-type="bibr" rid="scirp.109520-ref27">27</xref>].</p></sec><sec id="s2_3"><title>2.3. Measurement of Air Pollutant Levels</title><p>Particulate matter with diameters less than 2.5 and 10 microns (PM<sub>2.5</sub> and PM<sub>10</sub>, respectively) in air were measured using a BR-SMART-126 Particle Counter</p><p>(Blatn Science &amp; Technology Co. Ltd., Beijing, China) [<xref ref-type="bibr" rid="scirp.109520-ref28">28</xref>]. Aeroqual S500L portable air quality monitor (Aeroqual Limited, Auckland, New Zealand) was used for measuring carbon dioxide, carbon monoxide, hydrogen sulphide, sulphur dioxide, ozone and volatile organic compounds (VOCs) concentration. The free Series 500 6.4 PC Software was used for data extraction from the monitor. Testing for all the air pollutant parameters was done after every 1 hour for 8 hours (8:00 am to 4:00 pm, East African Standard Time). All handheld devices employed in this study were pre-calibrated before usage for effectiveness and quality assurance purposes.</p></sec><sec id="s2_4"><title>2.4. Risk Assessment</title><p>Mean values of PM<sub>2.5</sub> and PM<sub>10</sub> were compared with the World Health Organization guidelines i.e. annual mean for PM<sub>2.5</sub> is 10 μg/m<sup>3</sup>, 24-hour mean = 25 μg/m<sup>3</sup> while PM<sub>10</sub> = 20 μg/m<sup>3</sup> and 24-hour mean = 50 μg/m<sup>3</sup> [<xref ref-type="bibr" rid="scirp.109520-ref29">29</xref>]. The mean values were harnessed to compute the air quality index (AQI). The indices for each pollutant (average of the total sum from each sampling location) were calculated using Equation (1) [<xref ref-type="bibr" rid="scirp.109520-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref32">32</xref>].</p><p>AQI pollutant = Air pollutant concentration WHO standard &#215; 100 % (1)</p><p>The AQI according to United State Environmental Protection Agency (US EPA) is an index for reporting daily air quality as it indicates how clean or unhealthy the air is, the level of concern and the health effects [<xref ref-type="bibr" rid="scirp.109520-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref32">32</xref>]. The AQI focuses on “health effects an individual may experience within a few hours or days after breathing unhealthy air”. <xref ref-type="table" rid="table1">Table 1</xref> shows the air quality index rating [<xref ref-type="bibr" rid="scirp.109520-ref33">33</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref34">34</xref>] and the AQI pollutant concentration specific range for PM<sub>2.5</sub> and PM<sub>10</sub>. Generally, lower AQI values indicate better air quality [<xref ref-type="bibr" rid="scirp.109520-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref32">32</xref>].</p></sec><sec id="s2_5"><title>2.5. Data Analysis</title><p>Quantitative data were presented as means &#177; standard deviation of replicates. The analyses were done using GraphPad Prism statistical software (version 9.1.0, GraphPad Software, USA). Results obtained were compared with international compliance guidelines.</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Air quality index (AQI), PM<sub>2.5</sub> and PM<sub>10</sub> concentration color codes and the air pollutant level of health concern</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >AQI value of index</th><th align="center" valign="middle" >Level of health concern</th><th align="center" valign="middle" >PM<sub>2.5</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >PM<sub>10</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >Daily AQI colour</th><th align="center" valign="middle" >Pollution level</th></tr></thead><tr><td align="center" valign="middle" >0 to 50</td><td align="center" valign="middle" >Good</td><td align="center" valign="middle" >0 to 12</td><td align="center" valign="middle" >0 to 54</td><td align="center" valign="middle" >GREEN</td><td align="center" valign="middle" >Level 1</td></tr><tr><td align="center" valign="middle" >51 to 100</td><td align="center" valign="middle" >Moderate</td><td align="center" valign="middle" >12.1 to 35.4</td><td align="center" valign="middle" >55 to 154</td><td align="center" valign="middle" >YELLOW</td><td align="center" valign="middle" >Level 2</td></tr><tr><td align="center" valign="middle" >101 to 150</td><td align="center" valign="middle" >Unhealthy for sensitive groups</td><td align="center" valign="middle" >35.5 to 55.4</td><td align="center" valign="middle" >155 to 254</td><td align="center" valign="middle" >ORANGE</td><td align="center" valign="middle" >Level 3</td></tr><tr><td align="center" valign="middle" >151 to 200</td><td align="center" valign="middle" >Unhealthy</td><td align="center" valign="middle" >55.5 to 150.4</td><td align="center" valign="middle" >255 to 354</td><td align="center" valign="middle" >RED</td><td align="center" valign="middle" >Level 4</td></tr><tr><td align="center" valign="middle" >201 to 300</td><td align="center" valign="middle" >Very unhealthy</td><td align="center" valign="middle" >150.5 to 250.4</td><td align="center" valign="middle" >355 to 424</td><td align="center" valign="middle" >PURPLE</td><td align="center" valign="middle" >Level 5</td></tr><tr><td align="center" valign="middle" >&gt;300</td><td align="center" valign="middle" >Hazardous</td><td align="center" valign="middle" >&gt;250.4</td><td align="center" valign="middle" >&gt;424</td><td align="center" valign="middle" >MAROON</td><td align="center" valign="middle" >Level 6</td></tr></tbody></table></table-wrap></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Noise Pollution Levels</title><p>Aviation activities have become one of the causes of acoustic degradation of the environment [<xref ref-type="bibr" rid="scirp.109520-ref35">35</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref36">36</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref37">37</xref>]. <xref ref-type="fig" rid="fig2">Figure 2</xref> shows that Entebbe International Airport experiences irregular noise frequencies with the midday having the highest noise intensities. The international standards for aviation noise levels are estimated at 60 decibels (dB) for daytime (6:00 am - 10:00 pm). Therefore, the levels did not match with the International Aviation Standards for sometimes of the day. This causes discomposure at the airport especially at the terminal which is a public area all the times. However, the noise levels were also increased due to surface traffic and construction works following the current expansion of the airport. A study in Turkey reported that the rush hour for Van Ferit Melen airport is between 10:00 and 14:00 hours. The measured noise level average was 96.0 &#177; 8.4 dB in the apron and 86.0 &#177; 8.7 dB in the terminal area [<xref ref-type="bibr" rid="scirp.109520-ref27">27</xref>].</p><p>Previous studies linked aviation noise to sleep disturbances, hypertension, heart diseases, cognitive and learning deficits in children [<xref ref-type="bibr" rid="scirp.109520-ref38">38</xref>]. According to ISO standards, 0 - 26 dB hearing value is the normal hearing range, 27 - 40 dB can cause very mild hearing loss, 41 - 55 dB to mild hearing loss, 56 - 70 dB causes moderate hearing loss, 71 - 90 dB causes advanced hearing loss while 90 dB and above may cause more advanced hearing loss [<xref ref-type="bibr" rid="scirp.109520-ref39">39</xref>].</p></sec><sec id="s3_2"><title>3.2. Air Pollutants Concentration</title><p>The levels of air pollutants determined are shown in <xref ref-type="table" rid="table2">Table 2</xref>. Particulate matter (PM<sub>2.5</sub> and PM<sub>10</sub>) ranged from 3.0 to 17.0 μg/m<sup>3</sup> and 3.0 to 21.0 μg/m<sup>3</sup>, respectively. This implies that the particulate matter levels at EBB were all below the World Health Organization recommended levels of PM<sub>2.5</sub> and PM<sub>10</sub> (i.e. daily mass concentrations of 25 μg/m<sup>3</sup> and 50 μg/m<sup>3</sup>) [<xref ref-type="bibr" rid="scirp.109520-ref40">40</xref>]. Particulate matter is a common proxy indicator for air pollution as it has effects on people more than</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Average concentration of air pollutants at Entebbe International Airport, Uganda</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Location</th><th align="center" valign="middle" >Time</th><th align="center" valign="middle" >PM<sub>2.5</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >PM<sub>10</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >VOC (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >CO<sub>2</sub> (ppm)</th><th align="center" valign="middle" >Ozone (ppm)</th><th align="center" valign="middle" >CO (ppm)</th><th align="center" valign="middle" >H<sub>2</sub>S (ppm)</th><th align="center" valign="middle" >SO<sub>2</sub> (ppm)</th></tr></thead><tr><td align="center" valign="middle"  rowspan="9"  >Airstrip</td><td align="center" valign="middle" >08:00 am</td><td align="center" valign="middle" >5.00 &#177; 0.10</td><td align="center" valign="middle" >6.00 &#177; 0.04</td><td align="center" valign="middle" >0.49 &#177; 0.01</td><td align="center" valign="middle" >583.00 &#177; 0.03</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >3.40 &#177; 0.10</td><td align="center" valign="middle" >0.20 &#177; 0.01</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >09:00 am</td><td align="center" valign="middle" >7.00 &#177; 0.13</td><td align="center" valign="middle" >8.00 &#177; 0.10</td><td align="center" valign="middle" >0.42 &#177; 0.05</td><td align="center" valign="middle" >585.00 &#177; 0.10</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >1.70 &#177; 0.01</td><td align="center" valign="middle" >0.10 &#177; 0.00</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >10:00 am</td><td align="center" valign="middle" >6.00 &#177; 0.05</td><td align="center" valign="middle" >7.00 &#177; 0.02</td><td align="center" valign="middle" >0.43 &#177; 0.01</td><td align="center" valign="middle" >580.00 &#177; 2.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.03</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >11:00 am</td><td align="center" valign="middle" >12.00 &#177; 0.01</td><td align="center" valign="middle" >14.00 &#177; 0.11</td><td align="center" valign="middle" >0.38 &#177; 0.03</td><td align="center" valign="middle" >563.00 &#177; 0.50</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >12:00 pm</td><td align="center" valign="middle" >10.00 &#177; 0.02</td><td align="center" valign="middle" >15.00 &#177; 0.05</td><td align="center" valign="middle" >0.47 &#177; 0.05</td><td align="center" valign="middle" >571.00 &#177; 0.04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >01:00 pm</td><td align="center" valign="middle" >6.00 &#177; 0.06</td><td align="center" valign="middle" >9.00 &#177; 0.03</td><td align="center" valign="middle" >0.35 &#177; 0.01</td><td align="center" valign="middle" >558.00 &#177; 0.10</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >02:00 pm</td><td align="center" valign="middle" >4.00 &#177; 0.10</td><td align="center" valign="middle" >5.00 &#177; 0.01</td><td align="center" valign="middle" >0.32 &#177; 0.01</td><td align="center" valign="middle" >556.00 &#177; 0.02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >03:00 pm</td><td align="center" valign="middle" >9.00 &#177; 0.46</td><td align="center" valign="middle" >11.00 &#177; 0.01</td><td align="center" valign="middle" >0.33 &#177; 0.02</td><td align="center" valign="middle" >563.00 &#177; 0.15</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >04:00 pm</td><td align="center" valign="middle" >14.00 &#177; 0.06</td><td align="center" valign="middle" >14.00 &#177; 0.06</td><td align="center" valign="middle" >0.37 &#177; 0.03</td><td align="center" valign="middle" >561.00 &#177; 0.04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.90 &#177; 0.01</td><td align="center" valign="middle" >0.10 &#177; 0.02</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle"  rowspan="9"  >Airport terminal</td><td align="center" valign="middle" >08:00 am</td><td align="center" valign="middle" >17.00 &#177; 0.11</td><td align="center" valign="middle" >21.00 &#177; 0.07</td><td align="center" valign="middle" >0.42 &#177; 0.04</td><td align="center" valign="middle" >631.00 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >2.90 &#177; 0.04</td><td align="center" valign="middle" >0.30 &#177; 0.01</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >09:00 am</td><td align="center" valign="middle" >12.00 &#177; 0.02</td><td align="center" valign="middle" >15.00 &#177; 0.05</td><td align="center" valign="middle" >0.38 &#177; 0.01</td><td align="center" valign="middle" >629.00 &#177; 0.05</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.80 &#177; 0.02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >10:00 am</td><td align="center" valign="middle" >10.00 &#177; 0.04</td><td align="center" valign="middle" >11.00 &#177; 0.03</td><td align="center" valign="middle" >0.60 &#177; 0.00</td><td align="center" valign="middle" >606.00 &#177; 0.03</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >11:00 am</td><td align="center" valign="middle" >11.00 &#177; 0.10</td><td align="center" valign="middle" >11.00 &#177; 0.10</td><td align="center" valign="middle" >0.44 &#177; 0.01</td><td align="center" valign="middle" >584.00 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >12:00 pm</td><td align="center" valign="middle" >4.00 &#177; 0.02</td><td align="center" valign="middle" >5.00 &#177; 0.02</td><td align="center" valign="middle" >0.49 &#177; 0.03</td><td align="center" valign="middle" >562.00 &#177; 0.02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.02</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >01:00 pm</td><td align="center" valign="middle" >8.00 &#177; 0.08</td><td align="center" valign="middle" >10.00 &#177; 0.20</td><td align="center" valign="middle" >0.37 &#177; 0.00</td><td align="center" valign="middle" >548.00 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.20 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >02:00 pm</td><td align="center" valign="middle" >12.00 &#177; 0.01</td><td align="center" valign="middle" >13.00 &#177; 0.04</td><td align="center" valign="middle" >0.43 &#177; 0.01</td><td align="center" valign="middle" >560.00 &#177; 0.04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >03:00 pm</td><td align="center" valign="middle" >14.00 &#177; 0.05</td><td align="center" valign="middle" >18.00 &#177; 0.06</td><td align="center" valign="middle" >0.39 &#177; 0.03</td><td align="center" valign="middle" >559.00 &#177; 0.25</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.30 &#177; 0.05</td><td align="center" valign="middle" >0.10 &#177; 0.00</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >04:00 pm</td><td align="center" valign="middle" >10.00 &#177; 0.02</td><td align="center" valign="middle" >13.00 &#177; 0.01</td><td align="center" valign="middle" >0.41 &#177; 0.01</td><td align="center" valign="middle" >583.00 &#177; 0.42</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.90 &#177; 0.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle"  rowspan="9"  >CAA Headquarters</td><td align="center" valign="middle" >08:00 am</td><td align="center" valign="middle" >10.00 &#177; 0.08</td><td align="center" valign="middle" >11.00 &#177; 0.05</td><td align="center" valign="middle" >0.48 &#177; 0.04</td><td align="center" valign="middle" >586.00 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >1.60 &#177; 0.01</td><td align="center" valign="middle" >0.20 &#177; 0.03</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >09:00 am</td><td align="center" valign="middle" >11.00 &#177; 0.05</td><td align="center" valign="middle" >14.00 &#177; 0.01</td><td align="center" valign="middle" >0.40 &#177; 0.01</td><td align="center" valign="middle" >552.00 &#177; 0.80</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >1.80 &#177; 0.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >10:00 am</td><td align="center" valign="middle" >7.00 &#177; 0.10</td><td align="center" valign="middle" >8.00 &#177; 0.01</td><td align="center" valign="middle" >0.45 &#177; 0.03</td><td align="center" valign="middle" >567.00 &#177; 4.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.01</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >11:00 am</td><td align="center" valign="middle" >8.00 &#177; 0.03</td><td align="center" valign="middle" >8.00 &#177; 0.01</td><td align="center" valign="middle" >0.39 &#177; 0.01</td><td align="center" valign="middle" >573.00 &#177; 2.00</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.20 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >12:00 pm</td><td align="center" valign="middle" >6.00 &#177; 0.00</td><td align="center" valign="middle" >9.00 &#177; 0.03</td><td align="center" valign="middle" >0.41 &#177; 0.01</td><td align="center" valign="middle" >581.0 &#177; 0.04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >01:00 pm</td><td align="center" valign="middle" >9.00 &#177; 0.10</td><td align="center" valign="middle" >14.00 &#177; 0.04</td><td align="center" valign="middle" >0.40 &#177; 0.00</td><td align="center" valign="middle" >562.00 &#177; 0.05</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >02:00 pm</td><td align="center" valign="middle" >12.00 &#177; 0.03</td><td align="center" valign="middle" >16.00 &#177; 0.10</td><td align="center" valign="middle" >0.36 &#177; 0.01</td><td align="center" valign="middle" >579.00 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >03:00 pm</td><td align="center" valign="middle" >11.00 &#177; 0.01</td><td align="center" valign="middle" >14.00 &#177; 0.01</td><td align="center" valign="middle" >0.47 &#177; 0.00</td><td align="center" valign="middle" >569.00 &#177; 0.14</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >04:00 pm</td><td align="center" valign="middle" >17.00 &#177; 0.04</td><td align="center" valign="middle" >20.00 &#177; 0.05</td><td align="center" valign="middle" >0.41 &#177; 0.01</td><td align="center" valign="middle" >603.00 &#177; 0.20</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.60 &#177; 0.01</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle"  rowspan="9"  >Upper Hill of the Airport</td><td align="center" valign="middle" >08:00 am</td><td align="center" valign="middle" >6.00 &#177; 0.01</td><td align="center" valign="middle" >8.00 &#177; 0.02</td><td align="center" valign="middle" >0.48 &#177; 0.03</td><td align="center" valign="middle" >548.00 &#177; 0.24</td><td align="center" valign="middle" >0.009 &#177; 0.001</td><td align="center" valign="middle" >0.90 &#177; 0.02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >09:00 am</td><td align="center" valign="middle" >7.00 &#177; 0.03</td><td align="center" valign="middle" >8.00 &#177; 0.15</td><td align="center" valign="middle" >0.41 &#177; 0.00</td><td align="center" valign="middle" >550.00 &#177; 0.16</td><td align="center" valign="middle" >0.001 &#177; 0.000</td><td align="center" valign="middle" >0.70 &#177; 0.01</td><td align="center" valign="middle" >0.10 &#177; 0.04</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >10:00 am</td><td align="center" valign="middle" >5.00 &#177; 0.06</td><td align="center" valign="middle" >7.00 &#177; 0.01</td><td align="center" valign="middle" >0.35 &#177; 0.00</td><td align="center" valign="middle" >540.00 &#177; 0.01</td><td align="center" valign="middle" >0.003 &#177; 0.000</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >11:00 am</td><td align="center" valign="middle" >3.00 &#177; 0.06</td><td align="center" valign="middle" >3.00 &#177; 0.03</td><td align="center" valign="middle" >0.39 &#177; 0.02</td><td align="center" valign="middle" >554.00 &#177; 0.30</td><td align="center" valign="middle" >0.002 &#177; 0.001</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.01</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >12:00 pm</td><td align="center" valign="middle" >4.00 &#177; 0.02</td><td align="center" valign="middle" >5.00 &#177; 0.01</td><td align="center" valign="middle" >0.45 &#177; 0.10</td><td align="center" valign="middle" >562.00 &#177; 0.44</td><td align="center" valign="middle" >0.001 &#177; 0.000</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >01:00 pm</td><td align="center" valign="middle" >6.00 &#177; 0.11</td><td align="center" valign="middle" >6.00 &#177; 0.02</td><td align="center" valign="middle" >0.41 &#177; 0.01</td><td align="center" valign="middle" >548.00 &#177; 0.04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >02:00 pm</td><td align="center" valign="middle" >10.00 &#177; 0.04</td><td align="center" valign="middle" >11.00 &#177; 0.03</td><td align="center" valign="middle" >0.46 &#177; 0.03</td><td align="center" valign="middle" >542.00 &#177; 0.10</td><td align="center" valign="middle" >0.001 &#177; 0.000</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >0.10 &#177; 0.00</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >03:00 pm</td><td align="center" valign="middle" >11.00 &#177; 0.01</td><td align="center" valign="middle" >11.00 &#177; 0.06</td><td align="center" valign="middle" >0.38 &#177; 0.01</td><td align="center" valign="middle" >538.00 &#177; 0.50</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr><tr><td align="center" valign="middle" >04:00 pm</td><td align="center" valign="middle" >9.00 &#177; 0.03</td><td align="center" valign="middle" >10.00 &#177; 0.06</td><td align="center" valign="middle" >0.42 &#177; 0.00</td><td align="center" valign="middle" >550.00 &#177; 0.64</td><td align="center" valign="middle" >0.002 &#177; 0.001</td><td align="center" valign="middle" >0.20 &#177; 0.02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >ND</td></tr></tbody></table></table-wrap><p><sup>a</sup>ND: Not detected.</p><p>any other pollutant. Particulate matter is a complex mixture of solid and liquid particles of organic and inorganic substances (sulphates, nitrates, ammonia, sodium chloride, black carbon, mineral dust and water) suspended in the air. PM<sub>10</sub> have the potential to penetrate and lodge deep inside the lungs. Fine particulate matter (PM<sub>2.5</sub>) is a concerning air pollutant, particularly if it exceeds the WHO limit of 25 μg/m<sup>3</sup> 24-hour mean [<xref ref-type="bibr" rid="scirp.109520-ref40">40</xref>] because they can penetrate the lung barrier and enter the blood system. Chronic exposure to PM contributes to the risk of developing cardiovascular and respiratory diseases as well as of lung cancer [<xref ref-type="bibr" rid="scirp.109520-ref41">41</xref>].</p><p>Toxic volatile organic compounds (VOCs) like benzene, toluene, ethyl benzene and xylenes (BTEX) are atmospheric pollutants that present serious threats to human health [<xref ref-type="bibr" rid="scirp.109520-ref42">42</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref43">43</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref44">44</xref>]. Their emissions related to aircraft are not only during combustions but also result from resting losses from aircraft fuel tanks and during refuelling of the aircraft [<xref ref-type="bibr" rid="scirp.109520-ref45">45</xref>]. In this study, the concentration of VOCs was lower than the limit of 500 μg/m<sup>3</sup> [<xref ref-type="bibr" rid="scirp.109520-ref46">46</xref>]. VOCs such as 1,3-butadiene, benzene and vinyl chloride were classified by the International Agency for Research on Cancer in Group 1 as carcinogenic for humans [<xref ref-type="bibr" rid="scirp.109520-ref47">47</xref>]. They also cause eye and respiratory irritations, headache, dizziness, visual disorders as well as memory impairment [<xref ref-type="bibr" rid="scirp.109520-ref48">48</xref>]. At least 14 single or complex compounds are listed as hazardous by the Federal Aviation Administration, which in addition to polyaromatic hydrocarbons comprise acetaldehyde, 1,3-butadiene, n-hexane, acrolein, benzene, styrene, xylene, toluene, propionaldehyde, ethylbenzene, formaldehyde and lead compounds [<xref ref-type="bibr" rid="scirp.109520-ref49">49</xref>]. A recent study assessed 46 VOCs in the indoor air of the control tower maintenance room, potentially affecting employees, where a correlation was found between aircraft number and concentrations of light aldehydes/ketones [<xref ref-type="bibr" rid="scirp.109520-ref44">44</xref>].</p><p>Carbon monoxide and hydrogen sulphide concentrations were low (undetected in some cases) as compared to carbon dioxide concentrations. While the global trend is aiming at zero carbon dioxide emissions, the current study indicated that EBB produces substantial amounts of carbon dioxide which is a greenhouse gas. On the other hand, the current Occupational Safety and Health Administration permissible exposure limit for carbon monoxide is 50 ppm as an 8-hour time-weighted average concentration [<xref ref-type="bibr" rid="scirp.109520-ref50">50</xref>]. Carbon monoxide with its ability to combine with iron in haemoglobin may lead to carbon monoxide poisoning, a condition typified by headache, dizziness and drowsiness. Excessive exposure may cause loss of consciousness (coma) and ultimately death at high concentrations [<xref ref-type="bibr" rid="scirp.109520-ref51">51</xref>]. The 8-hour limit for hydrogen sulphide is 10 ppm and was not exceeded in this study. Exposure to this gas may cause eye, throat and nose irritations, bronchial constriction in asthmatic patients, spontaneous abortion, increased blood lactate concentration, decreased skeletal muscle citrate synthase activity, headache, dizziness, nausea, vomiting, coughing, difficulty in breathing, olfactory paralysis, convulsions and death in severe cases [<xref ref-type="bibr" rid="scirp.109520-ref52">52</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref53">53</xref>].</p><p>Serious health risks also arise from exposure to ozone and sulphur dioxide. The WHO set 100 μg/m<sup>3</sup> 8-hour mean as the guideline for ozone [<xref ref-type="bibr" rid="scirp.109520-ref41">41</xref>], which was not exceeded at EBB in this study (<xref ref-type="table" rid="table2">Table 2</xref>). Ground level ozone is one of the</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Average PM concentrations and AQI for the different locations studied at EEB</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Location</th><th align="center" valign="middle" >PM<sub>2.5</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >PM<sub>10</sub> (&#181;g/m<sup>3</sup>)</th><th align="center" valign="middle" >AQI (PM<sub>2.5</sub>)</th><th align="center" valign="middle" >AQI (PM<sub>10</sub>)</th></tr></thead><tr><td align="center" valign="middle" >Airstrip</td><td align="center" valign="middle" >8.1</td><td align="center" valign="middle" >9.88</td><td align="center" valign="middle" >0.810</td><td align="center" valign="middle" >0.494</td></tr><tr><td align="center" valign="middle" >Airport terminal</td><td align="center" valign="middle" >10.88</td><td align="center" valign="middle" >13.0</td><td align="center" valign="middle" >1.088</td><td align="center" valign="middle" >0.650</td></tr><tr><td align="center" valign="middle" >CAA headquarters</td><td align="center" valign="middle" >9.88</td><td align="center" valign="middle" >12.67</td><td align="center" valign="middle" >0.988</td><td align="center" valign="middle" >0.634</td></tr><tr><td align="center" valign="middle" >Upper hill of the airport</td><td align="center" valign="middle" >6.78</td><td align="center" valign="middle" >7.67</td><td align="center" valign="middle" >0.678</td><td align="center" valign="middle" >0.384</td></tr></tbody></table></table-wrap><p>reactants in the formation of photochemical smog, along with nitrogen oxides (NOx) from vehicle and industry emissions and volatile organic compounds (VOCs) emitted by automobiles [<xref ref-type="bibr" rid="scirp.109520-ref54">54</xref>]. It is one of the six criteria air pollutants prescribed by the United States Environmental Protection Agency. At high concentrations in the air, ozone can trigger asthma, bronchitis and emphysema, cause breathing problems, reduce lung function or cause lung diseases [<xref ref-type="bibr" rid="scirp.109520-ref41">41</xref>] [<xref ref-type="bibr" rid="scirp.109520-ref55">55</xref>]. The WHO guideline for SO<sub>2</sub> is 200 μg/m<sup>3</sup> 1-hour mean or 40 &#181;g/m<sup>3</sup> (annual mean). This pollutant has effects on the respiratory system (the lungs) and causes eye irritation. Its ability to trigger inflammation of the respiratory tract causes coughing, mucus secretion, aggravation of asthma and chronic bronchitis if inhaled at higher concentrations [<xref ref-type="bibr" rid="scirp.109520-ref41">41</xref>].</p></sec><sec id="s3_3"><title>3.3. Health Risk Assessment Results</title><p>As indicated in <xref ref-type="table" rid="table3">Table 3</xref>, the results of risk assessment based on particulate matter indicated that the air quality indices were all less than 50, which corresponds to good air quality. A recent report indicated that the air quality index of EBB is 60, with the dominant air pollutant being PM<sub>2.5</sub> [<xref ref-type="bibr" rid="scirp.109520-ref56">56</xref>]. In the neighboring Kampala, monitored PM<sub>2.5</sub> data indicated that air quality of the city is typically at levels considered “unhealthy for sensitive groups” to “unhealthy” according to the United States Environment Protection Agencies Air Quality Index (AQI) [<xref ref-type="bibr" rid="scirp.109520-ref14">14</xref>].</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>Airports form part of an interconnected world but also have many accrued environmental footprints. This study established that Entebbe International Airport experiences irregular noise frequencies with the midday having the highest noise intensities. Though some of the air pollutants are below recommended threshold, carbon dioxide was recorded at higher concentrations. Therefore, the aviation authorities need to ensure that these air pollutants are monitored and controlled continuously. The expansion of EBB concurrent with the development of residential areas might increase the noise and air pollution if cleaner technologies are not embraced. Further studies should perform audiogram assessments (acoustic estimation of noise-induced hearing loss) at the airport.</p></sec><sec id="s5"><title>Acknowledgements</title><p>The authors are grateful to the World Bank, the Inter-University Council of East Africa (IUCEA) for the scholarship awarded to Waganesh Admase and Timothy Omara through the Africa Center of Excellence II in Phytochemicals, Textiles and Renewable Energy (ACE II PTRE) at Moi University (Kenya) which made this study possible. Elly Olomo and Jasper Okino are grateful to the Mobility for Innovative Renewable Energy Technologies (MIRET) scheme (under the Intra-Africa Academic Mobility Scheme of the European Union Funding) hosted at Moi University for the scholarships awarded to them that made this collaboration possible.</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>Omolo, A., Angiro, C., Wagaye, W.A., Olomo, E., Okino, J. and Omara, T. (2021) Aviation Noise and Air Pollution: Results of a Study at Entebbe International Airport, Uganda. Open Access Library Journal, 8: e7454. https://doi.org/10.4236/oalib.1107454</p></sec></body><back><ref-list><title>References</title><ref id="scirp.109520-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Singh, A., Pope, F. and Avis, W.R. 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