<?xml version="1.0" encoding="UTF-8"?>
<rss version="2.0">
<channel>
<title> Iranian Journal of Health and Environment </title>
<link>http://ijhe.tums.ac.ir </link>
<description>Iranian Journal of Health and Environment - Journal articles for year 2013, Volume 6, Number 1</description>
<generator>Yektaweb Collection - https://yektaweb.com</generator>
<language>en</language>
<pubDate>2013/5/11</pubDate>

					<item>
						<title>Introducing an Appropriate Model using Support Vector Machine for Predicting Carbon Monoxide Daily Concentration in Tehran Atmosphere </title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5133&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;b&gt;Backgrounds and Objectives&lt;/b&gt;: Precise air pollutants prediction, as the first step in facing air pollution problem, could provide helpful information for authorities in order to have appropriate actions toward this challenge. Regarding the importance of carbon monoxide (CO) in Tehran atmosphere, this study aims to introduce a suitable model for predicting this pollutant. &lt;b&gt;
&lt;br&gt;Materials and Method:&lt;/b&gt; We used the air pollutants and meteorological data of Gholhak station located in the north of Tehran these data provided 12 variables as inputs for predicting the average CO concentration of the next day. First, support vector machine (SVM) model was used for forecasting CO daily average concentration. Then, we reduced the SVM inputs to seven variables using forward selection (FS) method. Finally, the hybrid model, FS-SVM, was developed for CO daily average concentration forecasting.
&lt;br&gt;&lt;b&gt;Result&lt;/b&gt;: In the research, we used correlation coefficient to evaluate the accuracy of both SVM and FS-SVM models. Findings indicated that correlation coefficient for both models in testing step was equal (R~0.88). It means that both models have proper accuracy for predicting CO concentration. However, it is noteworthy that FS-SVM model charged fewer amounts of computational and economical costs due to fewer inputs than SVM model.
&lt;b&gt;&lt;br&gt;Conclusion:&lt;/b&gt; Results showed that although both models have relatively equal accuracy in predicting CO concentration, FS-SVM model is the superior model due to its less number of inputs and therefore, less computational burden. 

</description>
						<author>Roohollah  Noori</author>
						<category></category>
					</item>
					
					<item>
						<title>Sensitivity Analysis of the Effective Input Parameters upon the Ozone Concentration using Artificial Neural Networks</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5104&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;b&gt;Background and Objectives:&lt;/b&gt; Weather pollution, caused by Ozone (O3) in metropolitans, is one of the major components of pollutants, which damage the environment and hurt all living organisms. Therefore, this study attempts to provide a model for the estimation of O3 concentration in Tabriz at two pollution monitoring stations: Abresan and Rastekuche.
&lt;br&gt;&lt;b&gt;Materials and Methods&lt;/b&gt;: In this research, Artificial neural networks (ANNs) were used to consider the impact of the meteorological and weather pollution parameters upon O3 concentration, and weight matrix of ANNs with Garson equation were used for sensitivity analysis of the input parameters to ANNs.&lt;br&gt; &lt;b&gt;Results&lt;/b&gt;: The results indicate that the O3 concentration is simultaneously affected by the meteorological and the weather pollution parameters. Among the meteorological parameters used by ANNs, maximum temperature and among the air pollution parameters, carbon monoxide had the maximum effect.
&lt;br&gt;&lt;b&gt;Conclusion&lt;/b&gt;: The results are representative of the acceptable performance of ANNs to predict O3 concentration. In addition, the parameters used in the modeling process could assess variations of the ozone concentration at the investigated stations.

</description>
						<author>Mohammadali  Ghorbani</author>
						<category></category>
					</item>
					
					<item>
						<title>Evaluation of Bioaerosol in a Hospital in Tehran</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5134&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;b&gt;Background and Objectives&lt;/b&gt;: Microorganisms are the agents that can cause disruption in the biochemical and physiological reactions through mechanisms such as infection, allergy or toxic properties in the case of entering human body and if the body’s immune system be unable to destroy and eliminate biological agents, illness and even death will occur. This study evaluates air pollution (aerosol and bioaerosol) in different parts of a hospital in Tehran.
&lt;br&gt;&lt;b&gt;Materials and Methods&lt;/b&gt;: We assessed and evaluated bioaerosols by applying  0800 NIOSH method using Bacterial sampler and  specific cultures for bacteria and fungi separately in ICU (intensive care unit), Pathology laboratory, Operating room, Recovery, and CSR (Central Service Room) of a hospital.
&lt;br&gt;&lt;b&gt;Results:&lt;/b&gt; The assessment showed that the average density of bacteria in the hospital studied was in the range of 1226.88 - 294.47 CFU/m3 the highest density was observed in the CSR and the lowest density measured was in the operating room. The bacteria identified included gram-positive bacillus (50.6%), Staphylococcus epidermis (20.29%), Staphylococcus Saprophyticus (2.6%), Staphylococcus aureus (7.03%), other Staphylococcus (5.9%) and Micrococcus (13.43%). Moreover, it was found that the average density of fungi was in the range of 0-188.45 CFU/m3 the maximum density in ICU and the minimum density in operating room and recovery room. The fungi identified included Aspergillus flavus (31.65%), Aspergillus fomigatus (25.17%), Aspergillus niger (15.82%), and penicilliom (27.33%) .
&lt;b&gt;&lt;br&gt;Conclusion&lt;/b&gt;: Comparison of bacteria density in different parts of the hospital with the recommended limits of ACGIH (500 CFU/m3) showed that density exceeded the limits in all units except in operating room whereas, density of fungi was less than the recommended limits of ACGIH (100 CFU/m3) in all units of hospital.

</description>
						<author>Farideh  Golbabaee</author>
						<category></category>
					</item>
					
					<item>
						<title>Analysis of Tehran Air Pollution Data in Recent Decade (2000-2009)</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5135&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives:&lt;/b&gt; Exceeding the standard level in most cases, Tehran air pollution has become a national environmental challenge. Therefore, it is crucial to analyze Tehran air-pollution data set during 2000-2009 for trend analysis.&lt;br&gt;
&lt;b&gt;Materials and Methods&lt;/b&gt;: In this study, we collected the hourly data of Tehran air pollution during 2000-2009 recorded by monitoring station of Tehran Air Pollution Control Company and statistical methods was used to determine the trend of the five pollutants, including: CO, PM10, SO2, NO2 and O3.&lt;br&gt;
&lt;b&gt;Results&lt;/b&gt;: The results indicate that average annual concentration of PM10, CO, NO&lt;sub&gt;2&lt;/sub&gt;, SO&lt;sub&gt;2&lt;/sub&gt; and O&lt;sub&gt;3&lt;/sub&gt; has changed from 91, 11.18, 102.6, 46.8, and 22.1 at monitoring station in 2000 to 88 &amp;micro;g/m3, 3.64 ppm, 66.1 ppb, 21.4 ppb, and 83 ppb in 2009 respectively.&lt;br&gt;
&lt;b&gt;Conclusion:&lt;/b&gt; Our findings revealed that although the air quality in Tehran has improved in term of particulate matter, SO2 and NO2 during this decade as a result of government&amp;#39;s recent program in air pollution control, ozone concentration has increased.&lt;/p&gt;
</description>
						<author>Parviz  Mahmoudi</author>
						<category></category>
					</item>
					
					<item>
						<title>Assessing Electrocyclone Performance in Collecting Smaller than 1 µm Silica Airborne Particles </title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5136&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives:&lt;/b&gt; Cyclone is one of the most utilized dust collectors for airborne particles control. It separates particles from airflow by centrifugal force. However, it is not effective in collecting very fine particles smaller than 10 &amp;mu;m in diameter. The aim of this study was to assess the performance of charging particles on cyclone efficiency in collecting particles smaller than 1 &amp;mu;m.&lt;br&gt;
&amp;nbsp;&lt;b&gt;Materials and&lt;/b&gt; &lt;b&gt;Methods:&lt;/b&gt; To achieve the above aim, a pilot air conditioning system equipped with conventional cyclone of Lapple model was designed and installed. A high voltage (18 KV) DC power supply was used for charging silica particle in corona charger. Isokinetic probe was used for particles sampling at upstream and downstream of cyclone under different study conditions and measurement was carried out using Grimm 1.08 dust counter.&lt;br&gt;
&lt;b&gt;Results:&lt;/b&gt; Charging fine airborne silica particles caused a significant increase in collection efficiency. There is a direct relationship between collection efficiency and charging voltage, so that the total particles collection efficiency was increased from 2.7 to about 72% with respect of increasing charging voltage from zero to 18 Kv. However, inlet air velocity has a negative effect on the collection efficiency of particles charged.&lt;br&gt;
&lt;b&gt;Conclusion&lt;/b&gt;: Applying electrocyclone in collecting fine particles smaller than 1 &amp;micro;m is more efficient compared with that of conventional cyclones.&lt;/p&gt;
</description>
						<author>Farshid  Ghormani shahna</author>
						<category></category>
					</item>
					
					<item>
						<title>Qualitative and quantitative assessment and management of hospital waste in Zanjan, Iran in 2011</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5226&amp;sid=1&amp;slc_lang=en</link>
						<description>Backgrounds and Objectives: Medical waste management is one of the important issues in solid waste managment in each community. This research was carried out to study the quantity, quality and the management practices of solid wastes of hospitals in Zanjan City in 2011.
Materials and Methods: In the present study, the hospital wastes were categoried and weighted into four main categories. Waste management pattern was studied based on a checklist extracted from national guidelines. Then, hospitals were ranked from very poor to excellent classes. For data analysis, Excel soft ware was used. 
Results: Waste generation rate was on average 2.402± 0.163 Kg/bed.day in the studied hospitals. The generation rate of domestic waste, infectious waste, sharp wastes, and chemical - pharmacological waste was 1.432±0.059, 0.926±0.096, 0.029±0.0055, and 0.015±0.002 kg/day.bed respectively. The status of the waste management practices was determined as average.
Conclusion: Waste generation rate in the hospitals of Zanjan was lower compared with the expected average value in other cities (e.g. 2.71 Kg/bed.day in Tehran). The percentage of medical waste in Zanjan hospitals was 34, which is higher than W.H.O. recommendations. Therefore, it is strongly recommended to reform and monitor certain solid waste management practices in order to reduce health and environmental issues.

</description>
						<author>Jalil Nassiri </author>
						<category></category>
					</item>
					
					<item>
						<title>Dust Phenomenon Affects on Cardiovascular and Respiratory Hospitalizations and Mortality “A Case Study in Kermanshah, during March-September 2010-2011</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5106&amp;sid=1&amp;slc_lang=en</link>
						<description>

&lt;p style=&quot;text-align: justify direction: ltr unicode-bidi: embed&quot; class=&quot;BasicParagraph&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;Background
and Objectives&lt;/span&gt;&lt;/b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;:
Dust phenomenon has adverse effects on the health of the population.Due to the
increasing concentration of Kermanshah dust phenomenon in recent years, The aim
of this study was to measure the concentration of the sensitivity coefficients
between dust phenomenon hospitalization and mortality rates for heart and
respiratory.&lt;/span&gt;&lt;/p&gt;

&lt;p style=&quot;text-align: justify direction: ltr unicode-bidi: embed&quot; class=&quot;BasicParagraph&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;Materials
and Methods&lt;/span&gt;&lt;/b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;:
This was a descriptive study in which we studied the sensitivity coefficient of
hospitalization and mortality rates for heart disease and respiratory to
changes of dust concentration.. The study duration was during March-September
2010 and 2011.&lt;span&gt; &lt;/span&gt;We collected the dust
phenomenon data from Kermanshah Province Environmental Protection Department.
The admissions and mortality of the cardiovascular and respiratory sufferers
was collected from the&lt;span&gt; &lt;/span&gt;Imam Ali, Imam
Reza, and Imam Khomeini governmental hosiptals in Kermanshah.&lt;/span&gt;&lt;/p&gt;

&lt;p style=&quot;text-align: justify direction: ltr unicode-bidi: embed&quot; class=&quot;BasicParagraph&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;Results&lt;/span&gt;&lt;/b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;: 1% increase in air pollution
caused by the dust phenomenon will result in increasing about 0.5 % of the&lt;span&gt; &lt;/span&gt;respiratory patients, 1% cardiac patients,
and about 0.3% of the heart disease mortality. The relationship between dust
phenomenon and respiratory sufferers was statistically not significant.&lt;/span&gt;&lt;/p&gt;

&lt;p style=&quot;text-align: justify direction: ltr unicode-bidi: embed&quot; class=&quot;BasicParagraph&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;Conclusions&lt;/span&gt;&lt;/b&gt;&lt;span style=&quot;font-family: &quot;Times New Roman&quot;,&quot;serif&quot;&quot;&gt;: We found that respiratory and
cardiovascular hospital admission has a high sensitivity to dust phenomenon.
This sensitivity has increased from 2010 to 2011. This sensitivity was greater
for males than females.&lt;span&gt; &lt;/span&gt;At least, during
March-September 2010, for every 100% increase in the concentration of dust
phenomenon, cardiovascular mortality increased by 29%.&lt;/span&gt;&lt;/p&gt;

&lt;!--stripped--&gt;
 &lt;w:LatentStyles DefLockedState=&quot;false&quot; DefUnhideWhenUsed=&quot;true&quot;
  DefSemiHidden=&quot;true&quot; DefQFormat=&quot;false&quot; DefPriority=&quot;99&quot;
  LatentStyleCount=&quot;267&quot;&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;0&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Normal&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;heading 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 7&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 8&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;9&quot; QFormat=&quot;true&quot; Name=&quot;heading 9&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 7&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 8&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; Name=&quot;toc 9&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;35&quot; QFormat=&quot;true&quot; Name=&quot;caption&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;10&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Title&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;1&quot; Name=&quot;Default Paragraph Font&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;11&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Subtitle&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;22&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Strong&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;20&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Emphasis&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;59&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Table Grid&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; UnhideWhenUsed=&quot;false&quot; Name=&quot;Placeholder Text&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;1&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;No Spacing&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; UnhideWhenUsed=&quot;false&quot; Name=&quot;Revision&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;34&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;List Paragraph&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;29&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Quote&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;30&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Intense Quote&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 1&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 2&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 3&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 4&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 5&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;60&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Shading Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;61&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light List Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;62&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Light Grid Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;63&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 1 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;64&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Shading 2 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;65&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 1 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;66&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium List 2 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;67&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 1 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;68&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 2 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;69&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Medium Grid 3 Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;70&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Dark List Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;71&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Shading Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;72&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful List Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;73&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; Name=&quot;Colorful Grid Accent 6&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;19&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Subtle Emphasis&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;21&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Intense Emphasis&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;31&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Subtle Reference&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;32&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Intense Reference&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;33&quot; SemiHidden=&quot;false&quot;
   UnhideWhenUsed=&quot;false&quot; QFormat=&quot;true&quot; Name=&quot;Book Title&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;37&quot; Name=&quot;Bibliography&quot;/&gt;
  &lt;w:LsdException Locked=&quot;false&quot; Priority=&quot;39&quot; QFormat=&quot;true&quot; Name=&quot;TOC Heading&quot;/&gt;
 &lt;/w:LatentStyles&gt;
&lt;!--stripped--&gt;&lt;!--stripped--&gt; !mso]&gt;&lt;ob&lt;illegal tag&gt;ject classid=&quot;clsid:38481807-CA0E-42D2-BF39-B33AF135CC4D&quot; id=ieooui&gt;&lt;/object&gt;
&lt;style&gt;
st1:*{behavior:url(#ieooui) }
&lt;/style&gt;
&lt;!--stripped--&gt;&lt;!--stripped--&gt;
&lt;style&gt;
 /* Style Definitions */
 table.MsoNormalTable
	{mso-style-name:&quot;Table Normal&quot;
	mso-tstyle-rowband-size:0
	mso-tstyle-colband-size:0
	mso-style-noshow:yes
	mso-style-priority:99
	mso-style-qformat:yes
	mso-style-parent:&quot;&quot;
	mso-padding-alt:0cm 5.4pt 0cm 5.4pt
	mso-para-margin:0cm
	mso-para-margin-bottom:.0001pt
	mso-pagination:widow-orphan
	font-size:11.0pt
	font-family:&quot;Calibri&quot;,&quot;sans-serif&quot;
	mso-ascii-font-family:Calibri
	mso-ascii-theme-font:minor-latin
	mso-fareast-font-family:&quot;Times New Roman&quot;
	mso-fareast-theme-font:minor-fareast
	mso-hansi-font-family:Calibri
	mso-hansi-theme-font:minor-latin
	mso-bidi-font-family:Arial
	mso-bidi-theme-font:minor-bidi}
&lt;/style&gt;
&lt;!--stripped--&gt;

</description>
						<author>Sohrab  Delangizan</author>
						<category></category>
					</item>
					
					<item>
						<title>Dispersion Modeling of NOx and SO2 Emissions from Tous Gas Power Plant, Mashhad</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5137&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives: &lt;/b&gt;Tous gas power plant as an emission source of gas pollutants is located in the northwest of Mashhad City. This power plant is located in the neighborhood of various (linear, point and area) sources of pollution including Tous thermal power plant, Tous industrial town and motor vehicles hence, it is not possible to determine precisely and accurately the share of these gases emission contribution at this power plant using conventional instruments. Therefore, we used modeling in order to estimate the dispersion of the pollutants emitted from this power plant.&lt;br&gt;
&lt;b&gt;Materials and Methods:&lt;/b&gt; we used Screen 3 software using data of exhaust fume concentration, mass emission, chimney features of each unit, meteorology data, and fuel types consumed in order to model dispersion of NOx and SO2 emitted from Tous gas power plant having V94.2 turbine equipped with DLN torches.&lt;br&gt;
&lt;b&gt;Results&lt;/b&gt;: Maximum concentration of NOx and SO2 at the distance about 30 km from the power plant was 1.08 and 3.69 &amp;micro;g/L respectively. The results of dispersion modeling of pollutants indicated that in most cases emission of air pollutants towards southeast. &lt;b&gt;Conclusion&lt;/b&gt;: The NOx and SO2 concentration measured revealed that the concentration of these pollutants is lower than the standards of Clean Air Act.&lt;/p&gt;
</description>
						<author>Edris  Bazrafshan</author>
						<category></category>
					</item>
					
					<item>
						<title>Estimation of Number of Cardiovascular Death, Myocardial Infarction and Chronic Obstructive Pulmonary Disease (COPD) from NO2 Exposure using Air Q Model in Ahvaz City During 2009</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5149&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives: &lt;/b&gt;According to the WHO estimates, air pollution is accounted for about 800000 premature death of cardiovascular and respiratory disease and lung cancer resulted from air pollution throughout the world approximately 150000 cases of those deaths occur in south Asia. The studies conducting on short-term and long-term effects are reported in terms of admission rate, consulting with a physician, number of a particular disease, death, and years of the lost life (YOLL). We used Air Q2.2.3 (Air Quality Health Impact Assessment) Model to evaluate adverse health effects caused by NO2 exposure in Ahvaz City during 2009. NO&lt;sub&gt;2&lt;/sub&gt; reacts with ammonia, moisture, and other compounds to form small particles. These small particles penetrate deeply into sensitive parts of the lungs and can cause or worsen respiratory disease, such as emphysema and bronchitis, and can aggravate existing heart disease, leading to increased hospital admissions and premature death.&lt;br&gt;
&lt;b&gt;Materials and Methods&lt;/b&gt;: First the data required was collected from Ahvaz Environment Organization and Meteorological Organization. Then, this data were processed by Excel software through correcting temperature and pressure, coding, averaging and filtering. Finally, the data processed were entered to Air Q model. This model is a valid and reliable WHO-proved tool to estimate the potential short term effects of air pollution. This model includes four screen inputs (Supplier, AQ data, Location, Parameter) and two output screens (Table and Graph).&lt;br&gt;
&lt;b&gt;Results:&lt;/b&gt; It was found that the Meteorological and Environment Organization stations have had the maximum and minimum NO2 concentration respectively. Moreover, the annual, summer, and winter average and 98cile of this pollutant was 27, 6, 43, and 115 &amp;micro;g/m&lt;sup&gt;3&lt;/sup&gt; respectively. The cumulative number of myocardial infarction resulted from NO&lt;sub&gt;2&lt;/sub&gt; exposure was estimated to be nine persons per year. This value for the cardiovascular death was found to be 19 cases. Finally, the COPD cases was estimated to be seven per year.&lt;br&gt;
&lt;b&gt;Conclusion&lt;/b&gt;: Air Q software calculated relative risks, attributable proportion, and baseline incidence using data processed by Excel and presents the output as the cause specific deaths. It is noteworthy that there is no model that can estimate all of the pollutants health effects simultaneously. Cumulative number of persons for acute MI attributed to NO&lt;sub&gt;2&lt;/sub&gt; exposure was 9 in 2009. Moreover, 51% of this number occurred in the days with concentrations lower than 60 &amp;micro;g/m&lt;sup&gt;3&lt;/sup&gt;. It should be noted that 72% of this value are corresponded to the days with concentrations below 90 &amp;micro;g/m&lt;sup&gt;3&lt;/sup&gt;. The total cumulative number of cardiovascular death attributed to exposure with NO2 during one year of monitoring was 19 persons. 60% of these cases have occurred in days with NO2 levels not exceeding 90 &amp;micro;g/m&lt;sup&gt;3&lt;/sup&gt;. Cumulative number of hospital admission of COPD attributed to exposure with NO&lt;sub&gt;2&lt;/sub&gt; during one year of monitoring was 7 persons.87 % of these cases have occurred in days with NO2 levels not exceeding 110 &amp;micro;g/m&lt;sup&gt;3&lt;/sup&gt;.&lt;/p&gt;
</description>
						<author>Mohamadjavad   Mohammadi</author>
						<category></category>
					</item>
					
					<item>
						<title>Relationship between the Particulate Matter Concentrations in the Indoor and Ambient Air of the Tehran Children Hospital in 2007</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5150&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives: &lt;/b&gt;In recent years exposure to fine airborne particles has been identified as an important factor affecting human health. Epidemiological studies have showed that the aerosol laden air can be an agent for microorganisms&amp;rsquo; dispersion. Ignoring internal sources, ambient air quality significantly affects indoor air quality. Since people spend most of their times in the indoor spaces and little data are available on the general understanding of the indoor air quality, therefore, the aim of this study is to determine the particulate matter concentrations in indoor and ambient air of Tehran Children Medical Center Hospital.&lt;br&gt;
&lt;b&gt;Materials and Method:&lt;/b&gt; PM&lt;sub&gt;10&lt;/sub&gt;/PM&lt;sub&gt;2.5&lt;/sub&gt; samples were collected in the indoor environment of the Tehran Children Medical Center Hospital and its adjacent outdoor environment by a portable GRIMM dust monitor model 1.108 from November 26 to March 10, 2007. The places of sampling for indoor and ambient air were in the patient room and the roof of the hospital respectively.&lt;br&gt;
&lt;b&gt;Results:&lt;/b&gt; The results showed that indoor PM&lt;sub&gt;10&lt;/sub&gt; level was higher than WHO standards in 80% cases in patient room, whereas, for indoor PM&lt;sub&gt;2.5&lt;/sub&gt; level, this value was 42 and 64% more than the EPA standards and WHO standards respectively. The relationship between outdoor and indoor particulate matters was examined by linear regression analysis. The indoor particulate matter levels were correlated with the corresponding ambient air ones.&lt;br&gt;
&lt;b&gt;Conclusion:&lt;/b&gt; Our analysis revealed that infiltration of ambient air could substantially increased indoor pollutants and thereby influences the indoor air quality.&lt;/p&gt;
</description>
						<author>Soheila Rezaei</author>
						<category></category>
					</item>
					
					<item>
						<title>Investigating Density and Type of Bioaerosols in a Petrochemical Wastewater Treatment Plant: Mahshar - Iran, 2013</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5155&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives&lt;/b&gt;: Wastewater contains various pathogens including viruses, bacteria, fungi, etc. These microorganisms can easily become airborne during normal operations of wastewater treatment plant and contaminate the neighborhood environment. The aim of this study was to investigate the type and density of bioaerosols in a petrochemical wastewater treatment plant in Iran.&lt;br&gt;
&lt;b&gt;Materials and Methods:&lt;/b&gt; In this cross sectional study, bioaerosols density was measured in different units of a petrochemical wastewater treatment plant according to the NIOSH 0800 method and the values measured were compared with background level (control area). For this purpose, air samples were collected on blood agar and dextro agar in Andersen single-stage sampler with air flow of 28.3 l/min for 10 minutes. Samples collected were shipped to the laboratory immediately and were incubated for 48 hours. Then, incubated samples were counted for colonies concentration.&lt;br&gt;
&amp;nbsp;&lt;b&gt;Results&lt;/b&gt;: Average concentration of bacteria and fungi bioaerosols measured were 731.70&amp;plusmn;185.49 and 28.43&amp;plusmn;10.58 (M&amp;plusmn;SD) CFU/m3 respectively throughout the wastewater treatment plant units. These values were 35 and 1.45 times higher than background level (Control area). The differences between average concentrations of bacteria in all units of wastewater treatment plant with control area were statistically significant.&lt;br&gt;
&lt;b&gt;Conclusions&lt;/b&gt;: Generally, it was found that the density of bioaerosols, especially bacteria was much higher than the background level. The maximum density was measured at aeration chamber, where the emission of bioaerosols could be reduced through replacing nozzle diffused aeration system.&lt;/p&gt;
</description>
						<author>Masoud  Neghab</author>
						<category></category>
					</item>
					
					<item>
						<title>Survey of Air Pollution Effect on Variation of Glycosylated Hemoglobin A1C (HbA1C) level in Diabetic Patients in Tehran</title>
						<link>http://journals.tums.ac.ir/ijhe/browse.php?a_id=5156&amp;sid=1&amp;slc_lang=en</link>
						<description>&lt;p&gt;&lt;b&gt;Background and Objectives:&lt;/b&gt; Air pollution and its effects on human health had become a major concern of many healthcare centers decision makers. In this study, air pollution effect on variation of Glycosylated Hemoglobin A1C (HbA1C) level in diabetic patients was evaluated, which is a unique study in Iran and Middle East region.&lt;br&gt;
&lt;b&gt;Materials and Methods:&lt;/b&gt; During November-January 2010-11, Tehran, capital of Iran, was exposed with high levels of air pollution. A retrospective cohort study was carried out on 330 patients diagnosed with diabetes mellitus for at least 12 months referring to 3 endocrinal care clinics. A questionnaire in two demographic and diabetic related sections was prepared. The patients&amp;#39; HbA1C level recorded on November-January 2009-10 was compared with November-January 2010-11. Descriptive analysis and paired t-test were carried out using SPSS 18 software.&lt;br&gt;
&lt;b&gt;Results:&lt;/b&gt; The patients investigated were divided into two groups. The first group was composed of 108 patients (53.7% female and 46.3% male) with diabetes mellitus type I (Insulin Dependent), age mean of 17.22, and SD of 11.57. The second group was composed of 222 patients (58.6% female and 41.4% male) with diabetes mellitus type II (Noninsulin Dependent), age mean of 53.91, and SD of 12.12. The change of HbAIC level in both groups wa not statistically significant in first group, HbA1C level increased from 7.71 to 7.75 mg / 100 ml (P =0.828) and in second group, it increased from 7.06 to 7.08 mg / 100 ml (P = 0.798).&lt;br&gt;
&lt;b&gt;Conclusion&lt;/b&gt;: According to the results obtained, it can be concluded that relation of air pollution and HbA1C mean variation in diabetic patients was insignificant.&lt;/p&gt;
</description>
						<author>Giti  Kashi</author>
						<category></category>
					</item>
					
	</channel>
</rss>
