<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1402</YEAR>
<VOL>11</VOL>
<NO>2</NO>
<MOSALSAL>43</MOSALSAL>
<PAGE_NO>255</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>ارزیابی آلودگی فلزات سنگین با استفاده از نشانگرهای زیستی درختان کهور (Prosopis juliflora) و نخل(Phoenix dactylifera) در اطراف کارخانه فولاد شادگان اهواز</TitleF>
		<TitleE>Evaluation of heavy metal pollution using biological markers of Prosopis juliflora and palm Phoenix dactylifera trees around Ahvaz Shadgan Steel Factory</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: درختان یکی از شاخص&#173;های زیستی مناسب در مناطق صنعتی و کارخانه&#173;ها هستند که با استفاده از پایش آن&#173;ها می&#173;توان وضعیت آلودگی فلزات سنگین منابع خاک را تعیین کرد. این تحقیق با هدف پایش زیستی فلزات سنگین سرب، کادمیوم، نیکل و آهن با استفاده از نشانگرهای زیستی گیاهی کهور (Prosopis juliflora) و نخل (Phoenix dactylifera) در کارخانه فولاد شادگان انجام شد.
مواد و روش ها: با توجه به موقعیت جغرافیایی کارخانه تعداد 4 ایستگاه انتخاب شد که 24 نمونه خاک و 72 نمونه برگ به صورت تصادفی با 3 تکرار، از 4 جهت مختلف جغرافیایی جمع&#173;آوری شد. به منظور بررسی انباشت زیستی فلزات در برگ درختان از ضریب تجمع زیستی استفاده گردید.
یافته ها: نتایج تحلیل واریانس (ANOVA) نشان می دهد تفاوت معنی&#173;داری بین گروه&#173;های خاک، درخت نخل و کهور برای غلظت فلزات سرب، کادمیوم، نیکل و آهن وجود داشت (P&#60;0.05). بیشترین غلظت فلز کادمیوم در ایستگاه 1 به ترتیب در نخل شسته نشده، نخل شسته شده، کهور شسته نشده و کهور شسته شده بود. در ایستگاه 2 و 4 غلظت فلزات کادمیوم، آهن و نیکل در نخل شسته نشده بیش از شسته شده می باشد و تنها فلز سرب در نخل شسته شده دارای غلظتی بیش از نخل شسته نشده می باشد. در ایستگاه 3 در گیاه کهور نیز غلظت فلزات کادمیوم، آهن و نیکل در نمونه های شسته نشده بیشتر از برگ شسته شده بود، فقط غلظت فلز سرب در گیاه شسته شده بیش از کهور شسته نشده به دست آمد. 
نتیجه گیری: غلظت فلزات سنگین در نمونه های خاک نسبت به برگ درختان نخل و کهور بالاتر به دست آمد، بنابراین با توجه به اینکه جذب از طریق خاک کم بوده احتمال ورود آلاینده ها از طریق نزولات خشک اتمسفری وجود دارد. به نظر می رسد کشت گیاه نخل و کهور در صنعت فولاد پتانسیل&#8204;هایی دارد که می&#8204;تواند به بهبود کیفیت خاک و پالایش آن کمک کند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: Trees are one of the appropriate biological indicators in industrial areas and factories, and by monitoring them; it is possible to determine the state of heavy metal contamination of soil resources. This research was carried out with the aim of biological monitoring of heavy metals lead, cadmium, nickel and iron using plant biomarkers of Prosopis juliflora and Phoenix dactylifera in Shadgan Steel Factory.
Methods: According to the geographical location of the factory, 4 stations were selected, where 24 soil samples and 72 leaf samples were collected randomly with 3 repetitions, from 4 different geographical directions. In order to investigate the bioaccumulation of metals in tree leaves, the bioaccumulation coefficient was used.
Results: The results of analysis of variance (ANOVA) show that there was a significant difference between soil, palm tree and mesquite groups for the concentration of lead, cadmium, nickel and iron metals (P&#60;0.05). The highest concentration of cadmium metal in station 1 was in unwashed palm, washed palm, unwashed Prosopis juliflora and washed Prosopis juliflora, respectively. In stations 2 and 4, the concentration of cadmium, iron and nickel metals in unwashed Phoenix dactylifera is more than that of washed Phoenix dactylifera, and only lead metal in washed Phoenix dactylifera has a concentration higher than that of unwashed Phoenix dactylifera. In station 3, the concentration of cadmium, iron and nickel metals in unwashed leaves was higher than in washed leaves, only the concentration of lead metal in the washed plant was higher than unwashed Prosopis juliflora.
Conclusion: There was no significant difference for lead metal between washed and unwashed leaves (P&#62;0.05) and this could be due to the accumulation in the lower parts of the plant, hence Phoenix dactylifera tree leaves and Prosopis juliflora is not a suitable biomarker for this metal. Considering that absorption through the soil is low, there is a possibility of pollutants entering through dry atmospheric precipitation. The accumulation potential of lead, cadmium, nickel and iron heavy metals was higher in Phoenix dactylifera tree than in Prosopis juliflora.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>130</FPAGE>
			<TPAGE>145</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/26
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/12/7
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سیدعلیرضا</Name>
				<MidName></MidName>
				<Family>کلبتی موسوی</Family>
				<NameE>Seyed Alireza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Kalbati Mosavi</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، واحد اهواز، دانشگاه آزاد اسلامی، اهواز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mousavi.a@ssico.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مریم</Name>
				<MidName></MidName>
				<Family>محمدی روزبهانی</Family>
				<NameE>Maryam</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi Rouzbahani</FamilyE>
				<Organizations>
				<Organization>گروه محیط‌ زیست، واحد اهواز، دانشگاه آزاد اسلامی، اهواز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Mmohammadiroozbahani@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سینا</Name>
				<MidName></MidName>
				<Family>عطارروشن</Family>
				<NameE>Sina</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Attar roshan</FamilyE>
				<Organizations>
				<Organization>گروه محیط‌ زیست، واحد اهواز، دانشگاه آزاد اسلامی، اهواز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>sina_2934@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>heavy metals</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>biological markers</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>plant treatment</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>mesquite tree</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>palm tree</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فلزات سنگین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نشانگرهای زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گیاه پالایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>درخت کهور</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>درخت نخل</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Khatun J, Intekhab A, Dhak D. Effect of uncontrolled fertilization and heavy metal toxicity associated with arsenic (As), lead (Pb) and cadmium (Cd), and possible remediation. Toxicology. 2022;26:153274.##Kumar D, Malik S, Rani R, Kumar R, Duhan JS. Behavior, risk, and bioremediation potential of heavy metals/metalloids in the soil system. Rendiconti Lincei. Scienze Fisiche e Naturali. 2023;2:1-23.##Selahvarzi M, Sobhanardakani S, Hemmasi A H, Taghavi L, Ghoddousi J. Contamination and source apportionment of iron, zinc, cadmium and chromium elements in surface soil of Khorramabad county, Iran. Iranian Journal of Health and Environment. 2023;15(4):651-670. [In Persian].##Torbati S, Esmailbegi Kermani S. Determining the concentration of Ag, Pb and Zn elements in some indigenous plant species grown in Zarshouran mining area, northwestern Iran. Iranian Journal of Health and Environment. 2022;15(3):379-398. [In Persian].##Khan I, Awan SA, Rizwan M, Ali S, Zhang X, Huang L. Arsenic behavior in soil-plant system and its detoxification mechanisms in plants: A review. Environmental Pollution. 2021;286:117389.##Abbaszadeh H, Mohammadi Roozbahani M, Sobhanardakani S. Use of Ziziphus spina-christi and Prosopis cineraria leaves as bio-indicators of environmental pollution emitted from industrial areas. Iranian Journal of Health and Environment. 2019;12(1):87-100. [In Persian].##Yaashikaa PR, Kumar PS, Jeevanantham S, Saravanan R. A review on bioremediation approach for heavy metal detoxification and accumulation in plants. Environmental Pollution. 2022;301:119035.##Farahmandian P, Mohammadian-Hafshejani A, Fadaei A, Sadeghi R. Relationship between cadmium exposure and breast cancer risk: a systematic review and meta-analysis. Iranian Journal of Health and Environment. 2023;16(2):393-412. [In Persian].##Saadaoui W, Gamboa-Rosales H, Sifuentes-Gallardo C, Duran-Munoz H, Abrougui K, Mohammadi A, Tarchoun N. Effects of Lead, Copper and Cadmium on Bioaccumulation and Translocation Factors and Biosynthesis of Photosynthetic Pigments in Vicia faba L.(Broad Beans) at Different Stages of Growth. Applied Sciences. 2022;12(18):8941.##Gong Y, Zhao D, Wang Q. An overview of field-scale studies on remediation of soil contaminated with heavy metals and metalloids: Technical progress over the last decade. Water research. 2018;147:440-460.##Schaumloffel D. Nickel species: analysis and toxic effects. Journal of Trace Elements in Medicine and Biology. 2012;26(1):1-6.##Hassan MU, Chattha MU, Khan I, Chattha MB, Aamer M, Nawaz M, Ali A, Khan MA, Khan TA. Nickel toxicity in plants: reasons, toxic effects, tolerance mechanisms, and remediation possibilities-a review. Environmental Science and Pollution Research. 2019;26:12673-88.##Das KK, Reddy RC, Bagoji IB, Das S, Bagali S, Mullur L, Khodnapur JP, Biradar MS. Primary concept of nickel toxicity-an overview. Journal of basic and clinical physiology and pharmacology. 2018;30(2):141-52.##Awa SH, Hadibarata T. Removal of heavy metals in contaminated soil by phytoremediation mechanism: a review. Water, Air, &#38; Soil Pollution. 2020;231(2):47.##Alizadeh S, Hashemi M. Phytoremediation to Remove ethylbenzene from Contaminated Media. Journal of Environmental Health Engineering. 2022;9(3):399-416. [In Persian].##Lorestani B, Cheraghi M, Soheil S A. Effect of traffic density on heavy metal content of soils and vegetation cover along roadsides, case study: City of Hamedan. Journal of Environmental Health Engineering. 2023;10(2):100-113. [In Persian].##Thalassinos G, Petropoulos SA, Grammenou A, Antoniadis V. Potentially toxic elements: A review on their soil behavior and plant attenuation mechanisms against their toxicity. Agriculture. 2023;13(9):1684.##Solgi E, Zamanian ‎ A, Beigmohammadi F. Investigating the effect of distance from source and species type on the absorption ability of heavy metals by tree species around Nahavand cement factory. Journal of Plant Ecosystem Conservation. 2020;8(16):321-343. [In Persian].##Zoufan P, Saadatkhah A, Rastegharzadeh S. Comparison of potentiality of heavy metals accumulation in the plants surrounding steel industries in the Mahshahr-Bandar Imam road, Ahvaz. Iranian Journal of Plant Biology. 2013;5(16):41-56. [In Persian].##Torkashvand V, Mohammadi Rouzbahni M, Babaeinezhad T. Survey of heavy metals (Pb,Ni,Cr,Cd ) bio-accumulation in the leaves of (Albizia lebbek and Eucalyotus camadulensis) (case stady: Iran National Steel Industrial Group). Journal of Neyshabur University of Medical Sciences. 2018;6(1):33-43. [In Persian].##Rafati M, Mohammadi Rozbahani M, Naseri Monfared H. Accumulation of heavy metals (lead and nickel) by the soil and leaves of Albizia lebbeck and Conocarpus erectus from the city of Ahwaz. Journal of Forest and Wood Products. 2021;73(4):379-387. [In Persian].##Rafati M, Mohammadi Roozbahani M, Pirmoradi Z. Bioaccumulation of some heavy metals by the soil and leaves of Ziziphus spina-christi in Khouzestan Oxin Steel Company. Iranian Journal of Forest and Range Protection Research. 2020;17(2):173-184. [In Persian].##Kolah Kaj A, Mohammadi Rozbahani M. Survey Effectiveness of Althea officinal in Pb Heavy Metal Accumulation. Journal of Environmental Science and Technology. 2017;19(1):93-102. [In Persian].##Bahemuka TE, Mubofu EB. Heavy metals in edible green vegetables grown along the sites of the Sinza and Msimbazi rivers in Dar es Salaam, Tanzania. Food Chemistry. 1999;66(1):63-6.##Johnson CM, Ulrich A. 2. Analytical methods for use in plant analysis. Bulletin of the California agricultural experiment station. 1959.##Kimbrough DE, Wakakuwa JR. Acid digestion for sediments, sludges, soils, and solid wastes. A proposed alternative to EPA SW 846 Method 3050. Environmental Science &#38; Technology. 1989;23(7):898-900.##Yoon J, Cao X, Zhou Q, Ma LQ. Accumulation of Pb, Cu, and Zn in native plants growing on a contaminated Florida site. Science of the Total Environment. 2006;368(2-3):456-464.##Abass MH, Hassan ZK, Al-Jabary KM. Assessment of heavy metals pollution in soil and date palm (Phoenix dactylifera L.) leaves sampled from Basra/Iraq governorate. Advances in Environmental Sciences. 2015;7(1):52-9. ‌##Akensous FZ, Anli M, Meddich A. Biostimulants as innovative tools to boost date palm (phoenix dactylifera L.) performance under drought, salinity, and heavy metal (Oid) s' stresses: a concise review. Sustainability. 2022;14(23):15984.##Hassan I, Cotrozzi L, Haiba NS, Basahi J, Ismail I, Almeelbi T, Hammam E. Trace elements in the fruits of date palm (Phoenix dactylifera L.) in Jeddah City, Saudi Arabia. Agrochimica. 2017;61(1):75-93.##Usman K, Abu-Dieyeh MH, Al-Ghouti MA. Evaluating the invasive plant, Prosopis juliflora in the two initial growth stages as a potential candidate for heavy metal phytostabilization in metalliferous soil. Environmental pollutants and Bioavailability. 2019;31(1):145-55.##El-Keblawy A. Causes and consequences of the invasion of the exotic Prosopis juliflora in the environment of the UAE. InThird Annual Conference for Research Funded by UAE University, Al-Ain: UAE University Press 2002 (pp. B5-B8).##Sulaiman M, Purayil FT, Krishankumar S, Kurup SS, Pessarakli M. Accumulation of toxic elements in soil and date palm (Phoenix dactylifera L.) through fertilizer application. Journal of Plant Nutrition. 2021;44(7):958-69.##Arpanaei A, Attarroshan S, Sabzalipour S, Arpanaei I. Bioaccumulation of some heavy metals (Copper, Nickel, and Lead) and air pollution tolerance index of Prosopis juliflora and Conocarpus erectus species in Mahshahr, Iran. Iranian Journal of Health and Environment. 2021;13(4):747-766. [In Persian].##Maleki S, Jems H, Derikvand S, Nasiri A. Evaluation of heavy metal pollution levels in leaves, soil and dust samples of Prosopis‎ cineraria Druce (L.) in the Bandar Abbas. Forest Research and Development. 2023;9(1):95-114. [In Persian].##Mirdadi M, Nohegar A. Investigating the Effect of Air Pollution on the Accumulation of Heavy Metals in Plant Species in Arid and Desert Areas (Case Study: Acacia, Prosopis and Ziziphus C, in Kahouristan, Hormozgan Province). Environmental Erosion Research Journal. 2022;12(2):1-18. [In Persian].##Angulo-Bejarano PI, Puente-Rivera J, Cruz-Ortega R. Metal and metalloid toxicity in plants: An overview on molecular aspects. Plants. 2021;10(4):635.##Phuong HT, Ba VN, Thien BN, Hong LT. Accumulation and distribution of nutrients, radionuclides and metals by roots, stems and leaves of plants. Nuclear Engineering and Technology. 2023;55(7):2650-5.##Hassan I, Cotrozzi L, Haiba NS, Basahi J, Ismail I, Almeelbi T, Hammam E. Trace elements in the fruits of date palm (Phoenix dactylifera L.) in Jeddah City, Saudi Arabia. Agrochimica. 2017;61(1):75-93.##Khudhur NS, Khudhur SM, Ahmad IN. An Assessment of heavy metal soil contamination in a Steel Factory and the surrounding area in Erbil City. Jordan Journal of Earth and Environmental Sciences. 2018;9(1):1-1.##Gajewska E, Skłodowska M. Nickel-induced changes in nitrogen metabolism in wheat shoots. Journal of Plant Physiology. 2009;166(10):1034-44.##Li S, Yang D, Tian J, Wang S, Yan Y, He X, Du Z, Zhong F. Physiological and transcriptional response of carbohydrate and nitrogen metabolism in tomato plant leaves to nickel ion and nitrogen levels. Scientia Horticulturae. 2022;292:110620.##Sistani N, Moeinaddini M, Khorasani N, Hamidian A, Ali-Taleshi M, Azimi Yancheshmeh R. Heavy metal pollution in soils nearby Kerman steel industry: metal richness and degree of contamination assessment. Iranian Journal of Health and Environment. 2017;10(1):75-86. [In Persian].##Habib HR, Awadh SM, Muslim MZ. Toxic heavy metals in soil and some plants in Baghdad, Iraq. Al-Nahrain Journal of Science. 2012;15(2):1-6.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>شاخص های خطر سلامت و بوم شناسی عناصر بالقوه سمی در خاک های سطحی میدان نفتی منصوری در جنوب شرق اهواز</TitleF>
		<TitleE>Health and ecological risk indicators of potentially toxic elements in the surface soils of the Mansouri oil field in the southeast of Ahvaz</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: : عناصر بالقوه سمی&#160;جزء آلاینده&#173;های خطرناک محیط&#173;زیست هستند و برای انسان سرطان&#173;زا می باشند. این تحقیق در سال 1399 با هدف برآورد و ارزیابی خطرات سلامتی انسان و بوم شناسی محیط زیست عناصر بالقوه سمی در خاک&#173;های سطحی میدان نفتی منصوری انجام شد.
مواد و روش ها: در این پژوهش در مجموع از هفت منطقه مورد مطالعه نمونه خاک تهیه گردید. در هر ایستگاه، پنج نمونه تصادفی از یک منطقه 5 متر مربعی در یک نمونه مرکب مخلوط شدند و 1 کیلوگرم خاک سطحی (عمق 0 تا 20 سانتیمتر) در کیسه&#173;های پلی&#173;اتیلن جمع&#173;آوری شد، بنابراین 105 نمونه خاک تهیه گردید. 
یافته ها: میانگین غلظت کادمیوم، سرب، نیکل، کروم، وانادیوم، مس و روی در خاک های سطحی میدان نفتی منصوری به ترتیب 05/1، 11/69، 79/86، 14/99، 76/23، 34/65 و 22/118 میلی&#173;گرم بر کیلوگرم به دست آمد. بالاترین و پایین ترین مقادیر شاخص ریسک اکولوژیکی بالقوه، مربوط به کادمیوم (50/157) و وانادیوم (34/0) بود. شاخص خطر سرطان زایی برای عنصر کروم درمورد بزرگسالان (5-10&#215;25/5) و کودکان (4-10&#215;91/3) بالاتر از کادمیوم، سرب، نیکل و وانادیوم به دست آمد.
نتیجه گیری: شاخص های آلودگی عناصر سمی بالقوه نظیر مقادیر فاکتور آلودگی، فاکتور غنی شدگی و شاخص زمین انباشت نشان داد که سرب و کادمیوم بیشترین تاثیر را بر روی آلودگی خاک داشتند که سطوح عناصر بالقوه سمی غلظت بالایی را در مقایسه با مقادیر زمینه و میانگین جهانی داشت که این نشان دهنده این است که نشت نفت خام، تردد وسایل نقلیه سبک و سنگین و فعالیت های انسانی مرتبط در این منطقه به میزان قابل توجهی در افزایش سطوح عناصر بالقوه سمی در این خاک ها کمک کرده است. به نظر می رسد عناصر بالقوه سمی که سلامت انسان را تهدید نمی کنند و مشکلات بهداشتی و بیماری&#173;زایی را به وجود نمی آورند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: Potentially toxic elements are part of dangerous environmental pollutants and are carcinogenic to humans. This research was conducted in 2019 with the aim of estimating and evaluating human health risks and environmental ecology of potentially toxic elements in the surface soils of Mansouri oil field.
Methods: In this research, soil samples were prepared from seven study areas. In each station, five random samples from an area of 5 square meters were mixed in a composite sample and 1 kg of surface soil (depth 0 to 20 cm) was collected in polyethylene bags, thus 105 soil samples were prepared.
Results: The average concentration of cadmium, lead, nickel, chromium, vanadium, copper and zinc in the surface soils of Mansouri oil field were obtained 1.05, 69.11, 86.79, 99.14, 23.76, 34.05, 65 and 118.22 mg/kg respectively. The highest and lowest values of the potential ecological risk index were related to cadmium (157.50) and vanadium (0.34). The carcinogenic risk index for chromium element was higher than cadmium, lead, nickel and vanadium for adults (5.25&#215;10-5) and children (3.91&#215;10-4).
Conclusion: The pollution indices of potentially toxic elements such as the values of the pollution factor, enrichment factor and land accumulation index showed that lead and cadmium had the greatest impact on soil pollution and the levels of potentially toxic elements were high in concentration compared to the background values and had a global average, which indicates that crude oil spills, light and heavy vehicle traffic, and related human activities in this area have significantly contributed to the increase in the levels of potentially toxic elements in these soils. It seems that there are potentially toxic elements that do not threaten human health and do not cause health problems or pathogenicity.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>146</FPAGE>
			<TPAGE>162</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/23
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/2/4
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/29
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>ولایت زاده</Family>
				<NameE>mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>velayatzadeh</FamilyE>
				<Organizations>
				<Organization>گروه ایمنی صنعتی، موسسه آموزش عالی کاسپین، قزوین، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mv.5908@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمدرضا</Name>
				<MidName></MidName>
				<Family>مودی</Family>
				<NameE>Mohammad Reza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moudi</FamilyE>
				<Organizations>
				<Organization>کارشناس بهداشت کار و محیط زیست، واحد HSE، نیروگاه گازی زاهدان، زاهدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>میرنیا</Family>
				<NameE>Mahdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mirnia</FamilyE>
				<Organizations>
				<Organization>دانش آموخته مهندسی صنایع، واحد زاهدان، دانشگاه آزاد اسلامی، زاهدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>potentially toxic elements</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>toxic metals</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>soil pollution</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>human health</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>carcinogenic risk index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عناصر بالقوه سمی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فلزات سمی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آلودگی خاک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سلامت انسان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص خطر سرطان‌زایی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Gan L, Wang J, Xie M, Yang B. Ecological risk and health risk analysis of soil potentially toxic elements from oil production plants in central China. Scientific Reports. 2022;12(1):17077.##Azimi-Yancheshmeh R, Moeinaddini M, Mazloomi S, Feyz Nia S, Shahbazi R. Health Risk Assessment of Metals in Street Dust of Karaj City in 2018. Journal of Environmental Health Engineering. 2022; 9 (3): 313-332. [In Persian].##Lorestani B, Cheraghi M, Soheil S A. Effect of traffic density on heavy metal content of soils and vegetation cover along roadsides, case study: City of Hamedan. Journal of Environmental Health Engineering. 2023; 10 (2): 100-113. [In Persian].##Nikfar F, Sabzalipour S, Gholami A, Nazarpour A. Assessment of carcinogenic and non-carcinogenic hazards of heavy metals in surface soils of Bandar Mahshahr industrial zone in 1398. Journal of Environmental Health Engineering. 2021; 8 (3): 245-256. [In Persian].##Ke W, Li C, Zhu F, Luo X, Feng J, Li X, Jiang Y, Wu C, Hartley W, Xue S. Effect of potentially toxic elements on soil multifunctionality at a lead smelting site. Journal of Hazardous Materials. 2023;454:131525.##Lajmiri Orak Z, Sabzalipour S, Panahpour E, Attarroshan S, Tavakkoli H. Investigation of Ecological Risk (ER) and Available Ratio (AR) of some heavy metals in drill cutting of Ahvaz Oil Field in 2019. Journal of Environmental Health Engineering 2021; 8 (3): 329-342. [In Persian].##Miao X, Hao Y, Zhang F, Zou S, Ye S, Xie Z. Spatial distribution of heavy metals and their potential sources in the soil of Yellow River Delta: a traditional oil field in China. Environmental geochemistry and health. 2020;42:7-26.##https://doi.org/10.1007/s10653-019-00243-4##Saleh HM, Eskander SB, Mahmoud HH, Abdelaal SA. Study on rare earth elements, heavy metals and organic contents in the soil of oil exploration site at Matruh Governorate, Egypt. Results in Geophysical Sciences. 2022;9:100039.##Jiang HH, Cai LM, Hu GC, Wen HH, Luo J, Xu HQ, Chen LG. An integrated exploration on health risk assessment quantification of potentially hazardous elements in soils from the perspective of sources. Ecotoxicology and Environmental Safety. 2021;208:111489.##Luo H, Wang Q, Guan Q, Ma Y, Ni F, Yang E, Zhang J. Heavy metal pollution levels, source apportionment and risk assessment in dust storms in key cities in Northwest China. Journal of Hazardous Materials. 2022;422:126878.##Wang HZ, Cai LM, Wang QS, Hu GC, Chen LG. A comprehensive exploration of risk assessment and source quantification of potentially toxic elements in road dust: A case study from a large Cu smelter in central China. Catena. 2021;196:104930.##Baltas H, Sirin M, Gökbayrak E, Ozcelik AE. A case study on pollution and a human health risk assessment of heavy metals in agricultural soils around Sinop province, Turkey. Chemosphere. 2020;241:125015.##Fedele D, De Francesco A, Riso S, Collo A. Obesity, malnutrition, and trace element deficiency in the coronavirus disease (COVID-19) pandemic: an overview. Nutrition. 2021;81:111016.##Nazarpour A, Ghanavati N, Babaenejad T. Evaluation of the level of pollution and potential ecological risk of some heavy metals in surface soils in the Ahvaz oil-field. Iranian Journal of Health and Environment. 2017; 10 (3): 391-400. [In Persian].##Shahidi Kaviani I, Paykanpoufard P. Study of The Rate of Soil Pollution to Heavy Metals Cadmium, Lead and Copper in Oil Industries Land at West Karun Region, Khuzestan Province, Iran. Journal of Research in Environmental Health. 2020;6(2): 161-172. [In Persian].##Sawaedi F, Cheraghi M. Study the concentration of heavy metals in the North Yaran oilfield sediments in the Hur Al-Azim wetland, Khuzestan. Journal of New Approaches in Water and Environmental Engineering. 1 (2): 103-111. [In Persian].##Aswal RS, Prasad M, Patel NK, Srivastav AL, Egbueri JC, Kumar GA, Ramola RC. Occurrences, sources and health hazard estimation of potentially toxic elements in the groundwater of Garhwal Himalaya, India. Scientific Reports. 2023;13(1):13069.##Chhimwal M, Kaur S, Srivastava RK, Hagare D, Shiva Prasad HJ. Water quality of springs and lakes in the Kumaon Lesser Himalayan Region of Uttarakhand, India. Journal of Water and Health. 2022;20(4):737-54.##Agency for Toxic Substances and Disease Registry (ATSDR). Toxicologial Profiles, Toxic Substances Portal. 2015.##International Agency for Research on Cancer (IARC). IARC monographs on the evaluation of carcinogenic risks to humans. 1-115; 2016.##Soleimani B, Moradi M, Ghabeishavi A, Mousavi A. Permeability variation modeling and reservoir heterogeneity of Bangestan carbonate sequence, Mansouri oilfield, SW Iran. Carbonates and Evaporites. 2019;34:143-57.##Kong F, Chen Y, Huang L, Yang Z, Zhu K. Human health risk visualization of potentially toxic elements in farmland soil: A combined method of source and probability. Ecotoxicology and Environmental Safety. 2021;211:111922.##United States Environmental Protection Agency (USEPA). Method 3050B: Acid digestion of sediments sludge's and soils (revision 2), 1996.##EPA US. Risk assessment guidance for superfund volume I: human health evaluation manual (Part F, Supplemental guidance for inhalation risk assessment). Washington DC. 2009.##EPA US. Exposure factors handbook. Office of research and Development, Washington, DC. 2011 Feb 13;20460:2-6.##Hakanson L. An ecological risk index for aquatic pollution control. A sedimentological approach. Water research. 1980;14(8):975-1001.##Abrahim, G.M.S. Holocene sediments of Tamaki Estuary: Characterization and impact of recent human activity on an urban estuary in Auckland, New Zealand, Ph.D. thesis, University of Auckland, Auckland, New Zealand, 2005; 361 p.##Muller G. Index of geo-accumulation in sediments of the Rhine River Geology Journal. 1969;2:109-18.##Rudnick RL, Gao S. Composition of the continental crust. Treatise on Geochemistry, vol. 3. Treat Geochem. 2003:1-64.##Sparks DL, Singh B, Siebecker MG. Environmental soil chemistry. Elsevier; 2022 Dec 23.##Iwegbue CMA, Williams ES, Isirimah NO. Study of heavy metal distribution in soils impacted with crude oil in Southern Nigeria. Soil and Sediment Contamination. 2009;18:136-143.##Alhassan M. Potentials of rice husk ash for soil stabilisation assumption university. Journal of Technology. 2008;14(4):245-250.##Douglas RK. Perspective Chapter: Rapid Measurement of Potentially Toxic Elements (PTEs) in Petroleum Hydrocarbons Polluted Soils by X-Ray Fluorescence (XRF) Spectroscopy. In Heavy Metals-Recent Advances 2022; IntechOpen.##Babaei B, Sobhanardakani S. Determination of heavy metals contamination in children's toys marketed in Hamedan City in 2015. Journal of Research in Environmental Health. 2(2): 165-172. [In Persian].##Bouida L, Rafatullah M, Kerrouche A, Qutob M, Alosaimi AM, Alorfi HS, Hussein MA. A review on cadmium and lead contamination: Sources, fate, mechanism, health effects and remediation methods. Water 14 (21), 3432.##Cai LM, Wang QS, Luo J, Chen LG, Zhu RL, Wang S, Tang CH. Heavy metal contamination and health risk assessment for children near a large Cu-smelter in central China. Science of the Total Environment. 2019;650:725-733.##Yuswir NS, Praveena SM, Aris AZ, Ismail SN, Hashim Z. Health risk assessment of heavy metal in urban surface soil (Klang District, Malaysia). Bulletin of Environmental Contamination and Toxicology. 2015;95:80-9.##Gan L, Wang J, Xie M, Yang B. Ecological risk and health risk analysis of soil potentially toxic elements from oil production plants in central China. Scientific Reports. 2022;12(1):17077.##Azimi-Yancheshmeh R, Moeinaddini M, Mazloomi S, Feyz Nia S, Shahbazi R. Health Risk Assessment of Metals in Street Dust of Karaj City in 2018. Journal of Environmental Health Engineering. 2022; 9 (3): 313-332. [In Persian].##Lorestani B, Cheraghi M, Soheil S A. Effect of traffic density on heavy metal content of soils and vegetation cover along roadsides, case study: City of Hamedan. Journal of Environmental Health Engineering. 2023; 10 (2): 100-113. [In Persian].##Nikfar F, Sabzalipour S, Gholami A, Nazarpour A. Assessment of carcinogenic and non-carcinogenic hazards of heavy metals in surface soils of Bandar Mahshahr industrial zone in 1398. Journal of Environmental Health Engineering. 2021; 8 (3): 245-256. [In Persian].##Ke W, Li C, Zhu F, Luo X, Feng J, Li X, Jiang Y, Wu C, Hartley W, Xue S. Effect of potentially toxic elements on soil multifunctionality at a lead smelting site. Journal of Hazardous Materials. 2023;454:131525.##Lajmiri Orak Z, Sabzalipour S, Panahpour E, Attarroshan S, Tavakkoli H. Investigation of Ecological Risk (ER) and Available Ratio (AR) of some heavy metals in drill cutting of Ahvaz Oil Field in 2019. Journal of Environmental Health Engineering 2021; 8 (3): 329-342. [In Persian].##Miao X, Hao Y, Zhang F, Zou S, Ye S, Xie Z. Spatial distribution of heavy metals and their potential sources in the soil of Yellow River Delta: a traditional oil field in China. Environmental geochemistry and health. 2020;42:7-26.##https://doi.org/10.1007/s10653-019-00243-4##Saleh HM, Eskander SB, Mahmoud HH, Abdelaal SA. Study on rare earth elements, heavy metals and organic contents in the soil of oil exploration site at Matruh Governorate, Egypt. Results in Geophysical Sciences. 2022;9:100039.##Jiang HH, Cai LM, Hu GC, Wen HH, Luo J, Xu HQ, Chen LG. An integrated exploration on health risk assessment quantification of potentially hazardous elements in soils from the perspective of sources. Ecotoxicology and Environmental Safety. 2021;208:111489.##Luo H, Wang Q, Guan Q, Ma Y, Ni F, Yang E, Zhang J. Heavy metal pollution levels, source apportionment and risk assessment in dust storms in key cities in Northwest China. Journal of Hazardous Materials. 2022;422:126878.##Wang HZ, Cai LM, Wang QS, Hu GC, Chen LG. A comprehensive exploration of risk assessment and source quantification of potentially toxic elements in road dust: A case study from a large Cu smelter in central China. Catena. 2021;196:104930.##Baltas H, Sirin M, Gökbayrak E, Ozcelik AE. A case study on pollution and a human health risk assessment of heavy metals in agricultural soils around Sinop province, Turkey. Chemosphere. 2020;241:125015.##Fedele D, De Francesco A, Riso S, Collo A. Obesity, malnutrition, and trace element deficiency in the coronavirus disease (COVID-19) pandemic: an overview. Nutrition. 2021;81:111016.##Nazarpour A, Ghanavati N, Babaenejad T. Evaluation of the level of pollution and potential ecological risk of some heavy metals in surface soils in the Ahvaz oil-field. Iranian Journal of Health and Environment. 2017; 10 (3): 391-400. [In Persian].##Shahidi Kaviani I, Paykanpoufard P. Study of The Rate of Soil Pollution to Heavy Metals Cadmium, Lead and Copper in Oil Industries Land at West Karun Region, Khuzestan Province, Iran. Journal of Research in Environmental Health. 2020;6(2): 161-172. [In Persian].##Sawaedi F, Cheraghi M. Study the concentration of heavy metals in the North Yaran oilfield sediments in the Hur Al-Azim wetland, Khuzestan. Journal of New Approaches in Water and Environmental Engineering. 1 (2): 103-111. [In Persian].##Aswal RS, Prasad M, Patel NK, Srivastav AL, Egbueri JC, Kumar GA, Ramola RC. Occurrences, sources and health hazard estimation of potentially toxic elements in the groundwater of Garhwal Himalaya, India. Scientific Reports. 2023;13(1):13069.##Chhimwal M, Kaur S, Srivastava RK, Hagare D, Shiva Prasad HJ. Water quality of springs and lakes in the Kumaon Lesser Himalayan Region of Uttarakhand, India. Journal of Water and Health. 2022;20(4):737-54.##Agency for Toxic Substances and Disease Registry (ATSDR). Toxicologial Profiles, Toxic Substances Portal. 2015.##International Agency for Research on Cancer (IARC). IARC monographs on the evaluation of carcinogenic risks to humans. 1-115; 2016.##Soleimani B, Moradi M, Ghabeishavi A, Mousavi A. Permeability variation modeling and reservoir heterogeneity of Bangestan carbonate sequence, Mansouri oilfield, SW Iran. Carbonates and Evaporites. 2019;34:143-57.##Kong F, Chen Y, Huang L, Yang Z, Zhu K. Human health risk visualization of potentially toxic elements in farmland soil: A combined method of source and probability. Ecotoxicology and Environmental Safety. 2021;211:111922.##United States Environmental Protection Agency (USEPA). Method 3050B: Acid digestion of sediments sludge's and soils (revision 2), 1996.##EPA US. Risk assessment guidance for superfund volume I: human health evaluation manual (Part F, Supplemental guidance for inhalation risk assessment). Washington DC. 2009.##EPA US. Exposure factors handbook. Office of research and Development, Washington, DC. 2011 Feb 13;20460:2-6.##Hakanson L. An ecological risk index for aquatic pollution control. A sedimentological approach. Water research. 1980;14(8):975-1001.##Abrahim, G.M.S. Holocene sediments of Tamaki Estuary: Characterization and impact of recent human activity on an urban estuary in Auckland, New Zealand, Ph.D. thesis, University of Auckland, Auckland, New Zealand, 2005; 361 p.##Muller G. Index of geo-accumulation in sediments of the Rhine River Geology Journal. 1969;2:109-18.##Rudnick RL, Gao S. Composition of the continental crust. Treatise on Geochemistry, vol. 3. Treat Geochem. 2003:1-64.##Sparks DL, Singh B, Siebecker MG. Environmental soil chemistry. Elsevier; 2022 Dec 23.##Iwegbue CMA, Williams ES, Isirimah NO. Study of heavy metal distribution in soils impacted with crude oil in Southern Nigeria. Soil and Sediment Contamination. 2009;18:136-143.##Alhassan M. Potentials of rice husk ash for soil stabilisation assumption university. Journal of Technology. 2008;14(4):245-250.##Douglas RK. Perspective Chapter: Rapid Measurement of Potentially Toxic Elements (PTEs) in Petroleum Hydrocarbons Polluted Soils by X-Ray Fluorescence (XRF) Spectroscopy. In Heavy Metals-Recent Advances 2022; IntechOpen.##Babaei B, Sobhanardakani S. Determination of heavy metals contamination in children's toys marketed in Hamedan City in 2015. Journal of Research in Environmental Health. 2(2): 165-172. [In Persian].##Bouida L, Rafatullah M, Kerrouche A, Qutob M, Alosaimi AM, Alorfi HS, Hussein MA. A review on cadmium and lead contamination: Sources, fate, mechanism, health effects and remediation methods. Water 14 (21), 3432.##Cai LM, Wang QS, Luo J, Chen LG, Zhu RL, Wang S, Tang CH. Heavy metal contamination and health risk assessment for children near a large Cu-smelter in central China. Science of the Total Environment. 2019;650:725-733.##Yuswir NS, Praveena SM, Aris AZ, Ismail SN, Hashim Z. Health risk assessment of heavy metal in urban surface soil (Klang District, Malaysia). Bulletin of Environmental Contamination and Toxicology. 2015;95:80-9.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی  میزان مواجهه شغلی سیلیس کریستالی و رابطه آن با ظرفیت ریوی کارگران شاغل در معادن استان البرزدر مقایسه با گروه کنترل</TitleF>
		<TitleE>Investigating of occupational exposure to crystalline silica and its relationship with the lung capacity of workers working in the mines of Alborz province compared to the control group.</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: تماس با عوامل زیان&#173;آور از قبیل گردوغبار در معادن امری معمولی است. با توجه به چالش&#173;های اندازه&#173;گیری سیلیس کریستالی هدف این مطالعه بررسی میزان مواجهه شغلی کارگران شاغل در معادن روزباز استان البرز با سیلیس کریستالی و رابطه آن با ظرفیت ریوی آنان می&#173;باشد.
مواد و روش ها: این مطالعه به صورت مقطعی- تحلیلی در معادن استان البرز انجام گرفت. پایش فردی 97 نفر ازکارگران شاغل در معادن با استفاده از روشNIOSH0600 و روش بهینه NIOSH7602 انجام گرفت. اسپیرومتری 97 نفر از کارگران شاغل در معادن استان و 97 نفر ازکارگران یک شرکت صنایع غذایی به عنوان گروه کنترل همزمان با پایش فردی انجام شد. داده&#173;ها توسط نرم افزار SPSS22 موردتجزیه و تحلیل قرار گرفت. 
یافته ها: میانگین گردوغبار سیلیس کریستالی حدود 2 برابر و گردوغبار کلی تنفسی 4/5 برابر استاندارد ایران بود. بین پارامترهای ریوی &#160;FEV1%,FVC%, PEF%بین دوگروه اختلاف معنی دار مشاهده شد. بین میزان گردوغبار سیلیس کریستالی و گردوغبار کلی تنفسی با ظرفیت&#173;های ریوی FEV1/FVC%&#160; و FEV1% نیز ارتباط معنی دار مشاهده شد. 
نتیجه گیری: قرارگرفتن در معرض گردوغبار شغلی کنترل شده یک پیش نیاز قطعی برای کاهش مشکلات تنفسی در بین کارگران معدن است.&#160; با توجه به یافته های مطالعه حاضر و کاهش عملکرد ریوی کارگران در مواجهه بیش از حد تماس شغلی با گردوغبار سیلیس کریستالی و گردوغبار کلی تنفسی ، احتمال بروز مشکلاتی در سلامت کارگران معادن درآینده متصور است. به نظر می رسد که راهبردهای فعلی مهندسی بهداشت حرفه&#173;ای برای حفاظت از کارگران کافی نبوده است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: In mines, it is common to come into contact with harmful substances like dust. Considering the challenges of crystalline silica measurement, this study was designed to investigate the relationship between occupational exposure to crystalline silica and lung capacity in miners working in Open pit mines of Alborz province.
Methods: A cross-sectional analytical study was carried out in Alborz province&#39;s mines. The monitoring of 97 workers working in mines was done using the NIOSH0600 method and the NIOSH7602 optimal method. At the same time as individual monitoring, 97 workers in mines in the province and 97 workers in a food industry company were monitored through spirometry. SPSS22 software was used to analyze the data.
Results: : The average amount of crystalline silica dust was approximately twice the Iranian standard, and the total respirable dust was 4.5 times the Iranian standard. The pulmonary parameters FEV1%, FVC%, and PEF% were observed to have a significant difference between two groups. The amount of crystalline silica dust and total respirable dust had a significant correlation with pulmonary capacities (FEV1/FVC% and FEV1%).
Conclusion: Controlled occupational dust exposure is a prerequisite for reducing respiratory problems among mine workers. The study found that workers who were exposed to excessive occupational contact with crystalline silica dust and respirable general dust decreased their lung function, which suggests that there could be problems with the health of mine workers in the future. In terms of protecting workers, it seems that the current occupational health engineering strategies were not sufficient.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>163</FPAGE>
			<TPAGE>177</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/18
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/11/29
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/16
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/28
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سیده آذر</Name>
				<MidName></MidName>
				<Family>موسوی فرد</Family>
				<NameE>Seyedeh Azar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>mousavifard</FamilyE>
				<Organizations>
				<Organization>دکتری مهندسی محیط زیست، گروه مهندسی بهداشت حرفه ای و ایمنی کار، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، البرز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فاطمه</Name>
				<MidName></MidName>
				<Family>زارعی</Family>
				<NameE>Fatemeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>zarei</FamilyE>
				<Organizations>
				<Organization>کارشناس ارشدمهندسی بهداشت حرفه ای، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، البرز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>zarei65@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>زهرا</Name>
				<MidName></MidName>
				<Family>صفایی</Family>
				<NameE>zahra</NameE>
				<MidNameE></MidNameE>
				<FamilyE>safaei</FamilyE>
				<Organizations>
				<Organization>کارشناس مهندسی بهداشت حرفه ای، معاونت بهداشتی، دانشگاه علوم پزشکی البرز، البرز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سکینه</Name>
				<MidName></MidName>
				<Family>احمدی</Family>
				<NameE>sakineh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ahmadi</FamilyE>
				<Organizations>
				<Organization>کارشناس مهندسی بهداشت حرفه ای، معاونت بهداشتی، دانشگاه علوم پزشکی البرز، البرز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Silica</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Pulmonary Capacity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Total dust</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>mine</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سیلیس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ظرفیت ریوی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گردوغبارکلی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>معدن</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Saamadi S, Badri sadat J. Measuring the duct concentration and its free silica at Emarat lead and zinc surface mine. FeyzMSJ 2004;7(4): [in persian].##Safinejad M, R Azari M, Zendehdel R, et al. Occupational and biological monitoring of workers exposed to airborne dust in Gol-e-Gohar Iron Ore mine: A Case-Control Study. . IOH 2019 16(1 ): 23-32[in persian].##Steenland Kyle, Mannetje Andrea, Boffett P, et al. Pooled exposure-response analyses and risk assessment for lung cancer in 10 cohorts of silica-exposed workers: an IARC multicentre study. CCC 2001;12: 773-84.##Zarei F, R. Azari M, Salehpour S, et al. Exposure assessment of core making workers to respirable crystalline silica dust. JHSW 2017;7(1): 1-8 [in persian].##Majdi Mr, Rafieimanesh E, Ehteshamfar M, et al. Investigating occupational lung diseases in turquoise mine workers. IOH 2010;2(6 ): 31-7[in persian].##Chen W, Zhuang Z, Attfield M, et al. Exposure to silica and silicosis among tin miners in China: exposure-response analyses and risk assessment. OEM 2001;58(1): 31-7.##IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. 1997. volume:68.##NIOSH. 7602 Silica, Crystalline by IR. NIOSH Manual of Analytical Methods NMAM. 4th edn. Cincinnati, OH; 1994.##American Conference of Governmental Industrial Hygienists. 2010 Threshold limit values and biological exposure indices. ACGIH, Cincinnati, OH.2010.##Ministry of Health and Medical Education. Occupational exposure level. 3th ed. Tehran: Institute for Environmental Research Publication, 2012. [In Persian].##Kakooei H, Fani M, Sadeghi N, et al. Assessment of occupational exposure to crystalline silica dust in an iron-stone mine, and comparing the results with standards. J Rostamineh Zabol Univ Med Sci 2014;3(3 ): 45-54 [in persian].##Kakouei H, Rezazadeh Azari M, Panahi D, et al. Evaluation of the occupational exposure of workers to free silica and total dust Underground Tunnel Digging Workshop of Tehran Metro Line 1. JHSW 2013;1(1): 25-30 [in pesian].##Azari M, Rokni M, Salehpour S, et al. Risk assessment of workers exposed to crystalline silica aerosols in the east zone of Tehran. NRITLD 2009;8(3): 43-5.##Zarei F, Rezazadeh Azari M, Salehpour S, et al. Respiratory Effects of Simultaneous Exposure to Respirable Crystalline Silica Dust, Formaldehyde, and Triethylamine of a Group of Foundry Workers. J Res Health Sci 2017;1(1): 371-81.##Hosseini Nasab M, Mohammaddoost O. Evaluation of pulmonary function capacity and respiratory disorders caused by dust in the workers of building stone mines of Nehbandan city. JESM 2023;1(1): 36-46.##Kakoei H, Nourmohammadi M, Mohammadian Y, et al. Assessment of occupational exposure to crystalline silica during demolition of buildings in Tehran. ijoh 2014;11(2): 63-9.##Samadi S, Jonaid B. Measuring the duct concentration and its free silica at Emarat lead and zinc surface mine. 2004;7.##Naghizadeh A, Mahvi A.H, Jabbari H, et al. Determination the level of dust and free silica in air of Khaf iron stone quarries. IJHE 2008;1(1): 37-44.##Golbabaei F, Gholami A, Teimori-Boghsani G, et al. Evaluation of occupational exposure to silica dust in mining workers in eastern Iran. OJER 2019;12(1 ): 1-6.##Gomes J, Lloyd O, Norman N, Pahwa P. Dust exposure and impairment of lung function at a small iron foundry in a rapidly developing country. OEM 2001;58(10): 656.##Meijer E, Kromhout H, Heederik D. Respiratory effects of exposure to low levels of concrete dust containing crystalline silica. Am J Ind 2001;40(2): 133-40.##Gholami A, Tajik Reza, Atif Khaula, et al. Respiratory symptoms and diminished lung functions associated with occupational dust exposure among iron ore mine workers in iran. Open Respir Med J 2020;14(1): 23-32.##Huang Y, Bao M, Xiao J, et al. Effects of PM2. 5 on cardio-pulmonary function injury in open manganese mine workers. IJERPH 2019;16(11): 2017.##Al-Shamma Y, Dinana F, Dosh B. Physiological study of the effect of employment in old brick factories on the lung functions of their employees. J Environ Sci Stud 2009;1(1): 39-46.##Hertzberg VS, Rosenman KD, Reilly MJ, Rice CH. Effect of occupational silica exposure on pulmonary function. Chest 2002;122(2): 721-8.##Hnizdo E, Baskind E, Sluis-Cremer, Gerhard K. Combined effect of silica dust exposure and tobacco smoking on the prevalence of respiratory impairments among gold miners. Scand J Work Environ Health 1990: 411-22.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی برگشت‌پذیری آلودگی هوای اصفهان پس از وقوع بارش</TitleF>
		<TitleE>Investigating the revertability of air pollution in Isfahan after precipitation</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: افزایش روزافزون جمعیت و صنعتی شدن جوامع باعث افزایش آلودگی محیط&#8204;زیست به ویژه آب و هوا شده است. در چند دهه اخیر، آلودگی هوا در کلانشهرها به عنوان یک چالش جدی که سلامت جامعه را تهدید می&#8204;کند، مطرح شده است. از سوی دیگر، کمبود آب و خشک شدن رودخانه&#8204;ها، دریاچه&#8204;ها و تالاب&#8204;ها باعث افزایش کانون&#8204;های گرد و غبار در اطراف شهرها شده که این خود باعث تشدید آلودگی هوا گردیده است. عوامل اقلیمی نیز بر تغییرات آلودگی هوا تاثیرگذارند. بارش یکی از پدیده&#8204;هایی است که می&#8204;تواند به طور ناگهانی آلودگی هوا را کاهش دهد و تا مدتی بعد از اتمام بارش، کیفیت هوا در وضعیت مطلوب باقی می&#8204;ماند. هدف از این مطالعه، بررسی زمان برگشت غلظت آلودگی هوا به شرایط پیش از وقوع بارش می&#8204;باشد.
مواد و روش ها: در حال حاضر آلودگی هوای کلانشهر اصفهان با استفاده از 9 ایستگاه پایش کیفیت هوا توسط حمل و نقل ترافیک شهرداری اصفهان به صورت لحظه&#8204;ای مورد آمایش قرار می&#8204;گیرد. در این مطالعه، از میان این 9 ایستگاه که به صورت پراکنده در سرتاسر اصفهان مستقر شده&#8204;اند، ایستگاه فیض که جزء مناطق پر تردد به لحاظ عبور و مرور وسایل نقلیه می&#8204;باشد، انتخاب شد. سپس آلودگی هوای ایستگاه فیض بر اساس میزان غلظت آلاینده&#8204;ها با توجه به استاندارد&#8204;های ارائه شده توسط آژانس حفاظت محیط&#8204;زیست آمریکا مورد ارزیابی قرار گرفت. در نهایت تاثیر وقوع بارش بر آلودگی هوای منطقه&#8204; مورد مطالعه بررسی گردید.
یافته ها: بر اساس میزان CO موجود در هوا، بیشترین زمان برگشت&#8204;پذیری به آلودگی پایه پس از بارش، مربوط به رویدادهای بارش 20 اسفند، 12 بهمن و 19 اسفند 1400 به ترتیب با 46، 37 و 31 ساعت می&#8204;باشد. این در حالی است که با در نظر داشتن PM2.5، بیشترین زمان برگشت&#8204;پذیری آلودگی مربوط به 13 اردیبهشت، 7 بهمن و 25 دی می&#8204;باشد که به ترتیب زمان برگشت&#8204;پذیری این آلاینده به آلودگی پایه به ترتیب 59، 51 و 49 ساعت بوده است. با در نظر گرفتن NO2، بیشترین زمان برگشت&#8204;پذیری آلودگی مربوط به 19 و 16 اسفندماه می&#8204;باشد که به ترتیب 64 و 47 ساعت پس از اتمام بارش میزان NO2 به مقدار پایه خود بازگشته است. این درحالی است که با در نظر داشتن آلاینده SO2، بارشی که در 15 آبان&#8204;ماه رخ داده است، تاثیر خود را حدوداً تا سه روز بعد بر روی SO2 گذاشته است، بنابراین طبق آمار موجود در تمام ساعات روز 16 آبان میزان SO2 کمتر از آلودگی پایه بوده است.
نتیجه گیری: نتایج نشان داد که در سال 1400، با در نظر گرفتن CO موجود در هوا 99 درصد از موارد ثبت شده در ایستگاه فیض در وضعیت کیفیت هوای خوب و 1 درصد از موارد ثبت شده در شرایط کیفیت هوای متوسط قرار دارند و با مد نظر قرار دادن میزان SO2 موجود در هوا، حدوداً 8/99 درصد از موارد ثبت شده در وضعیت کیفیت هوای خوب و حدوداً 2/0 درصد در حالت کیفیت هوای متوسط قرار دارند. بررسی میزان NO2 موجود در هوا نشان داد که 98 درصد موارد ثبت شده در وضعیت کیفیت هوای خوب و 2 درصد در شرایط کیفیت هوای متوسط قرار دارند. با توجه به PM2.5 موجود در هوا 26 درصد در حالت خوب، 48 درصد در وضعیت کیفیت هوای متوسط، 18 درصد در حالت کیفیت هوای غیربهداشتی برای گروه&#8204;های حساس، 7 درصد در شرایط کیفیت هوای غیربهداشتی و 1 درصد در وضعیت هوای بسیار غیربهداشتی قرار دارند. لازم به توضیح است در ساعات محدود و بسیار اندکی شاخص PM2.5 در حالت وضعیت کیفیت هوای خطرناک قرار داشت. نهایتاً نتایج این مطالعه نشان داد که در برخی از روزها وقوع بارش تاثیر قابل توجهی بر کاهش آلودگی هوا نداشته است، در حالی که در برخی از روزها، بارش موجب کاهش قابل توجه آلودگی هوا شده است و حتی پس از گذشت 215 ساعت، آلودگی هوا به مقدار پایه نرسیده است. هر چند ممکن است پس از قطع بارش عوامل دیگری از جمله وزش باد هم بر پایین ماندن غلظت آلودگی هوا موثر بوده باشند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: The ever-growing population and the industrialization of societies have led to an increase in environmental pollution, especially water and air pollution. In recent decades, air pollution in large cities has become a serious challenge that threatens the health of society. On the other hand, the water deficiency and the drying up of rivers, lakes and wetlands have led to an increase in dust production around cities, which in turn has worsened air pollution. Climatic factors also have an impact on changes in air pollution. Precipitation is one of the phenomena that can abruptly reduce air pollution, and air quality remains in a favorable state for some time after precipitation ceases. The aim of this study is to investigate the time when air pollution returns to the conditions before the occurrence of precipitation.
Methods: Currently, air pollution in the Isfahan metropolitan area is measured at 9 air quality monitoring stations by the Transportation and Traffic Department of Isfahan Municipality. In this study, Faiz station, which is located in an area with high traffic volume in terms of vehicle traffic, was selected among these 9 stations, which are scattered throughout Isfahan. In this study, the air pollution of Faiz station was evaluated based on the concentration of pollutants according to the standards of the US Environmental Protection Agency. Finally, the influence of precipitation on air pollution in the study area was examined.
Results: looking at the CO concentration in the air, it was observed that the maximum time of reversal of baseline pollution after precipitation is associated with the precipitation events of March 11, February 1 and March 10 with 46, 37 and 31 hours, respectively. For PM2.5 concentrations, the maximum reversibility of pollution was recorded on May 3, January 27 and January 15, with the reversibility of this pollutant to baseline pollution being 59, 51 and 49 hours, respectively. For NO2, the maximum reversibility of pollution was recorded on March 10 and 7, which respectively 64 and 47 hours after the end of the precipitation, the amount of NO2 returned to its baseline value. As for the pollutant SO2, the effect of the precipitation of November 6 on SO2 lasted until about 3 days later, so that according to the available data, the amount of SO2 is lower than the baseline pollution at all hours of November 7.
Conclusion: The results show that in terms of CO in the air, there was good air quality in 99% of the cases recorded at the Faiz station and average air quality in 1% of the cases, and that in terms of SO2 in air, there was good air quality in about 99.8% of the cases recorded and average air quality in about 0.2% of the recorded cases. The study of the NO2 concentration in the air showed that 98% of the recorded cases classified in good air quality and 2% in average air quality. As for PM2.5 concentration, 26% of the time was in good condition, 48% in average air quality, 18% in unhealthy air quality for sensitive groups, 7% in unhealthy air quality and 1% in very unhealthy air quality. It should be mentioned that the PM2.5 concentration reached a hazardous air quality condition in some hours. Finally, the results of this study showed that on some days the occurrence of precipitation had no significant effect on the reduction of air pollution, while on other days precipitation caused a significant reduction in air pollution and air pollution had not reached the baseline level even after 215 hours. It is possible that after the rain stopped, other factors such as wind were effective in keeping air pollution low.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>178</FPAGE>
			<TPAGE>200</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/182024/02/2
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/11/13
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/162024/04/8
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/20
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سیدعلی</Name>
				<MidName></MidName>
				<Family>شاهرضائی</Family>
				<NameE>Sayyed Ali</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shahrezaie</FamilyE>
				<Organizations>
				<Organization>دانش‌آموخته کارشناسی‌ارشد مهندسی منابع آب، دانشکده کشاورزی، دانشگاه شهرکرد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>sayyed.ali.shahrezaie@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رسول</Name>
				<MidName></MidName>
				<Family>میرعباسی نجف آبادی</Family>
				<NameE>Rasoul</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mirabbasi Najafabadi</FamilyE>
				<Organizations>
				<Organization>دانشیار، گروه مهندسی آب، دانشکده کشاورزی، دانشگاه شهرکرد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mirabbasi@sku.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سیدمجتبی</Name>
				<MidName></MidName>
				<Family>موسوی</Family>
				<NameE>Seyyed Mojtaba</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mousavi</FamilyE>
				<Organizations>
				<Organization>مدیر بهره‌برداری و نگهداری از سد و نیروگاه زاینده‌رود و کوهرنگ، شرکت آب منطقه‌ای اصفهان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>naeini1976@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نفیسه سادات</Name>
				<MidName></MidName>
				<Family>شاهرضائی</Family>
				<NameE>Nafiseh Sadat</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shahrezaie</FamilyE>
				<Organizations>
				<Organization>دانش‌آموخته کارشناسی، مهندسی عمران، دانشکده فنی مهندسی، دانشگاه ملایر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Nafiseshahrezaie@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>شراره</Name>
				<MidName></MidName>
				<Family>محمودی</Family>
				<NameE>Sharareh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mahmoudi</FamilyE>
				<Organizations>
				<Organization>دانش‌آموخته کارشناسی ارشد محیط‌زیست گرایش مهندسی آلودگی هوا، دانشکده محیط‌زیست، دانشگاه آزاد اسلامی واحد خوراسگان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Mahmoudi_sarareh@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Air pollution</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Precipitation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Isfahan city</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>revertability</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>air quality index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>AQI</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آلودگی هوا</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بارش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>برگشت‌پذیری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شهر اصفهان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص کیفیت هوا</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>AQI</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Haj Rasouliha S, Amini H, Hodji M and Najafi P. (2006). Biotracing of air and soil pollution in Isfahan region. Journal of Research in Agricultural Sciences. 2(2): 39-54. (In Persian).##Vafa-Arani, H., Jahani, S., Dashti, H, Heydar, J and Moazen, S. (2014). A system dynamics modeling for urban air pollution: A case study of Tehran, Iran. Transportation Research Part. 31, 21-36. (In Persian).##Mahboobfar M, Ramesht M, Yazdanpanah H and Azani M. (2018). Investigating the process of changes in the Air Quality Index in order to manage the air pollution crisis in the City of Isfahan. Urban Management. 17(50): 323-336. (In Persian).##Safavy, S.N, Mousavi, M, Dehghanzadeh Reihani, R, Shakeri, M. (2016). Seasonal and spatial zoning of Air Quality Index and Ambient Air Pollutants by Arc-GIS for Tabriz City and assessment of the current executive problem. Journal of Health. 7(2): 77-158. (In Persian).##Azizifar M, Naddafi K, Mohammadian M, Safdari M and Khazaei M. (2011). Air Pollution Quality Index (AQI) and density of PM1, PM2.5 and PM10 in the air of Qom. Qom University of Medical Sciences Journal. 5(2): 59-63. (In Persian).##Kermani M. (2002). Study of TSP and PM10 Quantities and Constitutive Material in the Ambient Air Shariati Hospital in Tehran, MSc. Thesis, Tehran University of Medical Sciences. (In Persian).##Wark K, Warner C. (1998). Air Pollution, Its Origin and Control. 3rd ed. Addison Wesley Longman: Inc.##USEPA. Characteristics of Particles. 2007. Available From: http://www.epa.gov/eogapti1/module3/distribu/distribu.htm.##USEPA. What is Visibility Important. 2006. Available From: http://www.Airinfonow.org/html/visibility.html.##Assari R, Modaresi M.R, Haghjouy Javanmard S.H, Lahijanzadeh A.R, Poursafa P, Sadeghian B and Kelishadi R. (2010). The relationship between air pollution and serum level of Thrombomodulin and Tissue Factor in a representative sample of adolescents aged 10-18 years in Isfahan, Iran. Journal of Isfahan Medical School. 28(109): 425-436. (In Persian).##Modarres R, Khosravi Dehkordi A. (2005). Daily air pollution time series analysis of Isfahan city. Int J Environ Sci Technol, 2(2593): 62. (In Persian).##Talebi SM, Tavakoli Ghinani T. Levels of PM10 and its chemical composition in the atmosphere of the city of Isfahan. Ir J Chem Engin 5(3): 62-7. (In Persian).##Mokhtari M, Jafari N, Hajizadeh Y, Mohammadi A, Miri M, Abdollahnejad A. (2017). Estimation of health effects of PM2.5 exposure using Air Q model in Isfahan during 2013. Health and Development Journal. 6(1): 74-84. (In Persian).##Malekizad F, Mirzahosseini A and Moattar F. (2019). Air quality assessment around Mehrabad Airport. Journal of Environmental Science and Technology. 21(5): 95-107. (In Persian).##Tulabi A, Zare MR, Zare M, Mahvi A, Shahriari A, Sarkhosh M et al. (2011). Assessment of air quality index in proximity of Bandar Abbas oil refinery. Medical Journal of Hormozgan University. 16(2): 123-133. (In Persian).##Seiday SE, Hedayati Moghadam Z, Fathi E, Jamshidi M. and Jamshidi A. (2012). Stratification and analysis of housing indicators of rural areas of Isfahan province using factor and cluster analyses. Urban Regional Studies and Research. 4(15): 37-52. (In Persian).##Hosseini S, Nader Khani Z and Yazdanbakhs B.A. (2017). Evaluation of the environmental sustainability of Ahvaz with an emphasis on air pollution (Using FPPSI method). 70(2): 309-317. (In Persian).##Tavakoli A. (2020). Evaluation of indoor air pollution in traditional bazaars- Case study in Naqsh-e-Jahan square of Isfahan in 2018-2019. Journal of Research in Environmental Health. 5(4): 273-282. (In Persian).##Shokati H, Sojoodi Z and Mashal M. (2022). Optimization and feasibility of using rainwater harvesting systems in Ardabil. Journal of Water and Soil. 36(3): 351-363. (In Persian).##Abdmanafi D, Mashkouti A.H. and Hejam S. (2016). A case study of the effect of acute air pollution on cloud physics and rainwater quality in Tehran. The sixth National Conference on Air and Noise Pollution Management. Tehran. Iran. (In Persian).##Shahrezaie, S.A., Radfar, M., Mirabbasi Najafabadi, R., Moughadas, M., Shahrezaie, N.S and Mahmoudi, S. (2023). Investigating the quality of Isfahan city rainwater under the influence of air pollution 2018-2019. Journal of Environmental Health Engineering. 10(4): 412-433. (In Persian).##Piri H and Mobarki M. (2022). Determining cultivation pattern of Isfahan agricultural crops using water footprint and virtual water. Environment and Water Engineering. 8(2): 507-518. (In Persian).##Iran's Population and Housing Census-2016. (2016). The Statistical Center of Iran.##Zarrabi A, Mohammadi J and Abdulahi, A.A. (2009). Investigation and evaluation of land use in fourteen areas of Isfahan using comparative method and LQi model using GIS software. Applied Research Journal of Geographical Sciences. 10(13): 173-202. (In Persian).##U.S. Environmental Protection Agency (1999). Air Quality Index Reporting; Final Rule. Part III. 40 CFR Part 58. EPA, Washington. 42530-42549.##Shahrezaie S.A, Mirabbasi R, Shahrezaie N.S and Khosravi M. (2022). Investigating air pollution in metropolitan Isfahan metropolitan in 2021-2022 based on AQI index. Journal of Environmental Health Engineering. 9(4): 442-456. (In Persian).##U.S. Environmental Protection Agency (2012). Technical Assistance Document for the Reporting of Daily Air Quality- the Air Quality Index (AQI). National Service Center for Environmental Publications (NSCEP). 29 pp.##U.S. Environmental Protection Agency (2009). Air Quality Index: AGuide to Air Quality and Your Health. National Service Center for Environmental Publications (NSCEP). 12 pp.##Mohammadian Y., Gorgani Firoozjani M. and Javadi Kahriz I. (2021). The evaluation of Tabriz mega-city air quality according to air quality index (AQI), in 2011. Human and Environment. 18(4): 95-107. (In Persian).##Segal C. 2015. Climate Regulation under the Clean Air Act in the Wake of Utility Air Regulatory Group V. EPA. Harvard Environmental Law Review. 39(1): 1-8.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی کیفیت میکروبی فراورده‌های غذایی، آرایشی- بهداشتی، پساب صنعتی و پسماند‌های بیمارستانی در استان همدان</TitleF>
		<TitleE>Investigation of the microbial quality of food products, cosmetics, industrial effluents and hospital wastes in Hamedan province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: بررسی سلامت میکروبی فراورده&#173;های غذایی، محصولات آرایشی- بهداشتی، پساب&#173;های صنعتی و پسماند&#173;های بیمارستانی، به دلیل مرتبط بودن با سلامت و بهداشت انسان در جامعه، حائز اهمیت هستند. هدف اصلی در این مطالعه، بررسی کیفیت میکروبی در مواد صنایع غذایی، آرایشی- بهداشتی، پساب&#173;های کارخانجات صنعتی و پسماند&#173;های بیمارستانی در استان همدان بود.
مواد و روش ها: در این مطالعه آزمون&#173;های میکروبی در تشخیص و شمارش باکتری&#173;ها، کپک&#173;ها و مخمر&#173;ها بر پایه&#173;ی کشت، در 15محصول غذایی و 5 محصول آرایشی- بهداشتی، انجام شد. همچنین آزمون&#173;های میکروبی پسماند&#173;های صنعتی (شمارش توتال و فکال کلیفرم&#173;ها) از روش MPN در38 واحد استفاده شد. آزمون&#173;های میکروبی 14 واحد بیمارستانی، از تست ویال بیولوژیک و تست کلاس 6 میکروبی، استفاده شد. 
یافته ها: براساس نتایج بدست آمده، تست&#173;های میکروبی در 4 محصول غذایی بیش از حد مجاز مصرف بودند و مابقی محصولات منفی گزارش شد. از 5 محصول آرایشی- بهداشتی، تنها یک محصول درای بار میکروبی غیر مجاز بود. همچنین نتایج آزمون&#173;های میکروبی در پسماند&#173;های صنعتی در زمستان 1401، 6 واحد صنعتی به صورت مثبت گزارش شد و فصل بهار 1402، 2 واحد صنعتی به صورت مثبت گزارش شد. در بررسی&#173;های پسماند&#173;های بیمارستانی، در زمستان 1401، تست&#173;های میکروبی کلیه&#173;ی واحد&#173;ها، منفی و در بهار 1402، دو واحد بیمارستانی مثبت شدند. 
نتیجه گیری: با توجه به اهمیت سلامت در جامعه، الزام بررسی&#173; آزمون&#173;های میکروبی در سطح بیمارستان&#173;ها و صنایع باید مورد توجه قرار گیرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: The Study of the microbial health of food products, cosmetic products, industrial effluents, and hospital wastes is important because they are related to human health and hygiene in society. The main purpose of this study was to investigate the microbial quality in food, cosmetics, industrial effluents, and hospital wastes in Hamadan province.
Methods: In this study, microbial tests were performed for the detection and counting of bacteria, molds, and yeasts based on the culture method in 15 food products and 5 cosmetic products. Also, industrial waste microbial tests (counting total and fecal coliforms) were used by MPN method in 38 units. Microbial tests of 14 hospital units were performed by biological vial test, and class 6 microbial test.
Results: Based on the obtained results, the microbial tests in 4 food products exceeded the permissible consumption limit and the rest of the products were reported as negative. Out of 5 cosmetic-sanitary products, was not allowed only one product with microbial load. Also, were reported the results of microbial tests in industrial wastes in the winter of 1401, 6 industrial units as positive, and in the spring of 1402, 2 industrial units were reported as positive. In the investigations of hospital waste, in the winter of 1401, the microbial tests of all units were negative, and in the spring of 1402, two hospital units were positive. 
Conclusion: Considering the importance of health in society, the requirement of microbial tests at the level of hospitals and industries should be taken into consideration.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>201</FPAGE>
			<TPAGE>215</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/182024/02/22024/02/20
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/12/1
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/162024/04/82024/04/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>حدیث</Name>
				<MidName></MidName>
				<Family>طوافی</Family>
				<NameE>Hadis</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Tavafi</FamilyE>
				<Organizations>
				<Organization>گروه زیست شناسی، دانشکده علوم پایه، دانشگاه ملایر، ملایر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>hadistavafi@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سارا</Name>
				<MidName></MidName>
				<Family>نوروزی</Family>
				<NameE>Sara</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Norouzi</FamilyE>
				<Organizations>
				<Organization>مدیر فنی بخش میکروبی، آزمایشگاه شیمی تجزیه راک، همدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>saranoroozi27@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Cosmetic-sanitary</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>microbial test</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>hospital waste</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>industrial waste</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>food</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آرایشی- بهداشتی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آزمون میکروبی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پسماند بیمارستانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پسماند صنعتی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مواد غذایی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Eslami H, Haider Z, Mohammad Taghizadeh F. Investigating the quantity, quality and management of hospital waste in Rafsanjan city in 2019: a descriptive study. J Rafsanjan Univ Med Sci. 2021; 20: 1297-1308 [In Persian].##Gorgani J, Nabizadeh R, Gholami M, et al. Management of hospital wastes in Mazandaran province with emphasis on genotoxic wastes. Iran J Health Environ. 2018; 12(3): 351-364 [In Persian].##Allegranzi B, Pittet D. Healthcare-associated infection in developing countries: simple solutions to meet complex challenges. Infect. Control Hosp. Epidemiol. 2007; 28(12):1323-1327.##Shirazi AR, Oryad HM, Malekzadeh J. Solid Wastes Management of Yasuj Hospitals, Iran 2006. Armaghane Danesh J. 2008; 13(1):105- 13.##Mohammadi P, Habibian M, Soudi MR, et al. Detection of Escherichia coli and Enterococcus faecalis indicators in water sources. Nova Biologica Reperta. 2013; 1(2): 10-15 [In Persian].##Khamisabadi A, Parwank K, Nasrabadi M. The effect of the use of sewage effluent on the microbial contamination of urban green space soils. J Environ Health Eng. 2018; 7(1): 42-52 [In Persian].##Masiha AR, Majid Khosh Khalq MR, Iszadeh KH, et al. Studying the microbial quality of some food items collected from the eastern region of Gilan. J Food Microbiology. 2014; 1(1): 1-13 [In Persian].##Nosrat Abadi L, Kavousi H R, Hajimohammadi Farimani R, et al. Investigating the microbial population of Astamran, Zahedi, Shahani, Kabkab, Mardarsang, Mozafati and Halila date varieties. Iran J Nutr Sci Food Technol. 2018; 89(16): 275-285[In Persian].##Mansouri B, Maleki A, Mahmoudi M, et al. Risk assessment of heavy metals in lipstick and hair dye cosmetics distributed in Sanandaj city in 2014. Sci J Kurdistan Univ Med Sci. 2016; 22: 31-39 [In Persian].##Radmanesh R, Nabi Meybodi M, Ramadan V, et al. Investigating the physicochemical properties and microbial contamination of combined drugs in Yazd pharmacies. Ofogh Danesh. 2018; 26(1): 82-93 [In Persian].##https://standard.inso.gov.ir/Search.aspx?standardnumber=5272.##https://standard.inso.gov.ir/Search.aspx?standardnumber=2946.##https://standard.inso.gov.ir/Search.aspx?standardnumber=10899.##https://standard.inso.gov.ir/StandardFiles/3759.htm.##https://standard.inso.gov.ir/Search.aspx?standardnumber=6806 .##https://standard.inso.gov.ir/Search.aspx?standardnumber=2197.##https://standard.inso.gov.ir/Search.aspx?standardnumber=1810.##https://standard.inso.gov.ir/Search.aspx?standardnumber=2198.##https://standard.inso.gov.ir/Search.aspx?standardnumber=11804.##https://standard.inso.gov.ir/Search.aspx?standardnumber=9933.##https://standard.inso.gov.ir/Search.aspx?standardnumber=11169.##https://standard.inso.gov.ir/Search.aspx?standardnumber=9934.##https://standard.inso.gov.ir/Search.aspx?standardnumber=9793.##Farzadkia M, Ansari AR, Imam Juma MM. Investigating waste management in one of Tehran's specialized hospitals. J Qazvin Univ Med Sci. 2012; 16(4): 107-109 [In Persian].##Zazouli MA, Alaviniya M, Bai A. Investigating the production of hospital waste in Gorgan hospitals, 2013. J Mazandaran Univ Med Sci. 2014; 25(132): 304-308 [In Persian].##Yousefi E, Karimzadeh Motlag Z, Doagoyan F, et al. Assessment of Quantity and Management on Medical Wastes of South Khorasan Province During 2014 -2015. Human and Environment. 2021; 58: 57- 68 [In Persian].##Momeniha F, Kouhkan M, Safamanesh H, et al. Investigating the efficiency of disinfecting and encapsulating device for medical sharps waste. Iran. J. Health &#38; Environ. 2023; 16(2): 245- 256 [In Persian].##Alinezhadian A, Karimi A, Mohammadi J, et al. Study of soil bacterial and crop quality irrigated with treated. Irani J Health Environ. 2014; 6 (3):365-376 [In Persian].##Tavakoli, H.R, Riazipour, M. Microbial quality of cooked meat foods in Tehran University's restaurants. Pak J Med Sci. 2008; 24: 595-599 [In Persian].##Qazvini K, Safdari H. Investigating the bacterial contamination of cosmetic products used around the eyes before and after use in Iran. Pajouhesh Dar Pezeshki. 2016; 31(2): 159- 162 [In Persian].## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی میزان پراکسید و ترکیبات قطبی در روغن های خوراکی مصرف شده در واحدهای فست فودی: مطالعه موردی شهر نورآباد</TitleF>
		<TitleE>Investigation of Peroxide Level and Polar Compounds in Edible Oils Used in Fast Food Units: A Case Study in Noorabad City</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: با توسعه صنعت رستوران&#8204;ها و افزایش مصرف غذاهای فست فود، بهداشت مواد غذایی و کیفیت روغن&#8204;های مورد استفاده در فرآیند سرخ کردن اهمیت زیادی پیدا کرده است. این مقاله به بررسی میزان پراکسید و ترکیبات قطبی در روغن&#8204;های خوراکی مورد استفاده در واحدهای فست فود شهر نورآباد می&#8204;پردازد. 
مواد و روش ها: با استفاده از فرمول کوکران 27 واحد انتخاب شد. نمونه&#8204;برداری از واحدهای انتخاب شده در دو مرحله به صورت دوره&#8204;ای در روزهای غیرتعطیل صورت گرفت. نمونه های گرفته شده به آزمایشگاه انتقال داده شده و مطابق استاندارد 4179 موسسه استاندارد وتحقیقات صنعتی ایران آنالیز شدند. داده های جمع آوری شده با استفاده از نرم افزار SPSS و آزمون های ANOA و پس آزمون توکی آنالیز شدند. &#160;
یافته ها: در مرحله اول نمونه برداری 7/40 درصد و در مرحله دوم 6/29درصد از نمونه ها&#160; داری ترکیبات قطبی بالاتر از حد مجاز بودند. بین میزان تولید ترکیبات قطبی، دما، زمان و نوع ظرف مورد استفاده ارتباط معنا داری وجود دارد (p&#60;0.05). با افزایش زمان استفاده از روغن به بیشتر از 20 دقیقه مقدار ترکیبات قطبی افزایش یافته است. ظرف&#160; چدنی بیشترین تاثیر را در افزایش مقدار ترکیبات قطبی به نسبت ظروف مسی و روی داشته است. همچنین بین میزان تولید پراکسید و نوع ظرف، زمان و برند مورد استفاده&#160; تفاوت معنا داری مشاهده شد (p&#60;0.05). ظرف چدنی کمترین تاثیر را در میزان تولید پراکسید داشته است. &#160;
نتیجه گیری: مدت زمان استفاده از روغن، نوع ظرف، و برند مورد استفاده تأثیر مهمی بر کیفیت روغن&#8204;های مورد استفاده در فست فودها دارند. این اطلاعات می&#8204;توانند به بهبود فرآیندها و استانداردهای بهداشتی در این واحدها کمک کنند و در نهایت، سلامت مصرف&#8204;کنندگان را تضمین نمایند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: With the expansion of the restaurant industry and the increased consumption of fast food, the hygiene of food ingredients and the quality of oils used in the frying process have gained significant importance. This article explores the levels of peroxides and polar compounds in edible oils used in fast food establishments in Noorabad city.
Methods: Twenty-seven units were selected using the Cochran formula. Sampling from the selected units was conducted in two stages periodically on non-holiday days. The collected samples were transferred to the laboratory and analyzed according to the Iranian Industrial Standards and Research Institute Standard 4179. The collected data were analyzed using SPSS software, ANOVA, and post-hoc tests.
Results: In the first sampling stage, 40.7% of the samples, and in the second stage, 29.6% exceeded the permissible limits for polar compounds. Significant correlations were found between the production of polar compounds, temperature, time, and the type of container used (p &#60; 0.05). The amount of polar compounds increased with the use of oil for more than 20 minutes, with cast iron containers having the most significant impact compared to copper and aluminum containers. Additionally, significant differences were observed in peroxide production based on the type of container, time, and brand used (p &#60; 0.05), with cast iron having the least impact
Conclusion: Based on the obtained results, it can be concluded that the duration of oil usage, the type of container, and the brand used significantly affect the quality of oils used in fast food establishments. This information can contribute to improving processes and hygiene standards in these units, ultimately ensuring consumer health.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>216</FPAGE>
			<TPAGE>227</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/182024/02/22024/02/202023/12/19
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/9/28
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/162024/04/82024/04/72024/04/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فرامرز</Name>
				<MidName></MidName>
				<Family>عظیمی</Family>
				<NameE>Faramarz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Azimi</FamilyE>
				<Organizations>
				<Organization>مرکر تحقیقات بهداشت محیط، دانشگاه علوم پزشکی لرستان، خرم آباد ،ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>وحید</Name>
				<MidName></MidName>
				<Family>محمدی</Family>
				<NameE>Vahid</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi</FamilyE>
				<Organizations>
				<Organization>مرکر تحقیقات بهداشت محیط، دانشگاه علوم پزشکی لرستان، خرم آباد ،ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>الهه</Name>
				<MidName></MidName>
				<Family>عسکری</Family>
				<NameE>Elaheh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Askari</FamilyE>
				<Organizations>
				<Organization>مرکز تحقیقات بهداشت تغذیه، دانشکده بهداشت و تغذیه، دانشگاه علوم پزشکی لرستان، خرم آباد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمدامین</Name>
				<MidName></MidName>
				<Family>کرمی</Family>
				<NameE>Mohammad Amin</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Karami</FamilyE>
				<Organizations>
				<Organization>مرکر تحقیقات بهداشت محیط، دانشگاه علوم پزشکی لرستان، خرم آباد ،ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Fast Food</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Polar Compounds</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Peroxide</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Noorabad</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فست فود</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ترکیبات قطبی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پراکسید</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نور  آباد</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Abadi Arani Ahmad SM, Jadi Arani Taibeh Sadat, Gilasi Hamid Reza, Jahed Khaniki Gholamreza. A Study of the Awareness and Attitudes of Healthcare Workers in Kashan Health Centers Regarding Food Hygiene and Safety in the Year. Nasim-e Tandorosti Quarterly 2014;3(3): 7-1.##Mahdieh RA. The effect of heat processing on the nutritional quality of food materials. The third International Congress and the twenty-sixth National Congress of Food Science and Technology in Iran; Tehran2019.##Farazmand H, Hallafi H. The demand for away from home food in Iranian households: An application of box-cox double hurdle model. Economic Modelling 2016;9(32): 65-85.##KHOUSHTINAT K, Kavousi P, Zandi P. Determination of Fry-life of two formulated frying oils produced in pilot scale. IJFST 2005;2(3).##Moulodi F, Qajarbeigi P, Rahmani K, et al. Effect of Fatty Acid Composition on Thermal Stability of Extra Virgin Olive Oil. Journal of Food Quality &#38; Hazards Control 2015;2(2).##Relation of Fatty Acids Composition with Stability of Sunflower and Canola Oil Blends. Journal of food science and technology(Iran) 2007;4(13): 67-76.##Jahed Khaniki G, Safaei P, Barik Gugjlu R, Mohajer A. Determination of peroxide value of edible oils used in sandwich and falafel shops in Tehran. Iranian Journal of Health and Environment 2018;10(4): 501-10.##Kharghani M, Kariminezhad F, Afzal Aghaee Naeein M, et al. Investigation of cooking oil quality at fast food restaurants in Mashhad City. International Journal of Environmental Health Engineering 2019;8(November): 1-6.##Shariatzadeh MA, Goodarzi M. Stereological study on the protective effect of royal jelly on kidney tissue following silver nanoparticles-induced toxicity in the NMRI mouse. Journal of Animal Research (Iranian Journal of Biology) 2021;34(3): 166-80.##ISIRI. Oils and fat of animal and herbaceous, peroxide measurement. Tehran: Institute of Standards and Industrial Research of Iran; 2008.##Sajjadi SA, Moteallemi A, Bargard ZR, et al. Investigation of cooking oil quality at fast food restaurants in Mashhad City. International Journal of Environmental Health Engineering 2019;8(1): 6.##Kaviani M, Niazmand R, Shahidi Noghabi M. Discarding time evaluation of canola oil based on oxidation indexes during potato deep frying. Research and Innovation in Food Science and Technology 2013;2(1): 37-50.##RahimzadehBarzoki H, Beirami S, Mansourian M, et al. Determination of Peroxide Value of Edible Oils Used in Confectionary, Restaurants and Sandwich Shops in Gorgan in 2011. Tolooebehdasht 2014;13(1): 40-7.##Delavar M, Navabi A, Abdollahi A, et al. Investigation of peroxide, acidity, and thermal stability of oils used to Make Falafel in Arak, Iran in 2018. Journal of health research in community 2020;6(2): 61-8.##Bolourian S, Movahhed GG, Afshari M, et al. Evaluation of Heat Stability and Performance of Palm Olein and Colza Oils Blends in Frying of Potato Chips. JOURNAL OF FOOD RESEARCH (UNIVERSITY OF TABRIZ),[online] 2010;3(20): 1.##Khalili N, Akrami Mohajeri F, Ramroudi F, et al. Quality assessments of the fried oils in fast food restaurants of Yazd, Iran. Journal of Nutrition and Food Security 2020;5(3): 201-8.##Innawong B, Mallikarjunan P, Irudayaraj J, Marcy JE. The determination of frying oil quality using Fourier transform infrared attenuated total reflectance. LWT-Food Science and Technology 2004;37(1): 23-8.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی مدیریت آب و فاضلاب در مشاغل کوچک شهر قم با نگرش خشکسالی و تهدید‌های زیست محیطی ناشی از کمبود آب</TitleF>
		<TitleE>Investigation of water and wastewater management in small businesses in Qom city with a focus on drought and environmental threats caused by water scarcity</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: در حال حاضر به منظور سازگاری با بحران آب موجود در کشور و مدیریت پایدار تامین و توزیع آب، اعمال شیوه&#8204;های مدیریتی صحیح مبتنی بر اصول پایداری یکی از اساسی&#8204;ترین نیاز&#8204;ها است. این مطالعه با هدف بررسی مدیریت آب و فاضلاب در مشاغل کوچک شهر قم با نگرش خشکسالی و تهدید&#8204;های زیست محیطی ناشی از کمبود آب در سال 1400 انجام شد .
مواد و روش ها: پژوهش حاضر یک مطالعه توصیفی &#8211; مقطعی است که پس از پیمایش میدانی و آمار اخذ شده از اداره آب و فاضلاب بر روی 223 صنف مرتبط با 67 اتحادیه اصناف شهر قم به انجام رسید و میزان مصارف آب و تولید فاضلاب و نحوه مدیریت آب و فاضلاب مشاغل با نگرش خشکسالی و تهدید&#8204;های زیست محیطی ناشی از کمبود آب مورد مطالعه قرار گرفت و نتایج حاصله بصورت توصیفی گزارش شد.
یافته ها: با توجه به میزان مصارف آب مشاغل به چهار درجه طبقه&#8204;بندی شدند و مشخص شد که مشاغل درجه یک، 96/82 درصد مشاغل و با میانگین مصرف 246/2&#177;574/2، مشاغل درجه دو 174/7 درصد و با میانگین 6142/3 &#177; 2823/19، مشاغل درجه سه 036/4 درصد و با میانگین 121/2 &#177; 5/40 و مشاغل درجه چهار 83/5 درصد مشاغل و با میانگین مصرف آب 821/215 &#177; 28/355 مترمکعب در ماه می&#8204;باشند از نظر وضعیت صرفه&#8204;جویی به ترتیب در مشاغل درجه یک تا چهار، 08/61، 25/56، 33/33 و 46/38 درصد مشاغل فاقد برنامه مشخص برای صرفه جویی در آب بودند.
نتیجه گیری: نتایج نشان داد نحوه مدیریت آب و فاضلاب در مشاغل شهر قم شرایط مطلوبی ندارد با توجه به کاهش نزولات جوی و خشکسالی به نظر می&#8204;رسد مسئله تامین آب بزرگ&#8204;ترین چالش پیش روی در این شهر باشد. اکثر مشاغل مورد مطالعه فاقد برنامه مشخص برای صرفه&#8204;جویی آب هستند، که بایستی مدیران منابع آب ضمن برآورد و ارزیابی دقیق منابع و مصارف آب، تصمیم&#8204;های در زمینه جبران کمبود کمی و تخریب کیفی آب اخذ نمایند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: Currently, in order to adapt to the existing water crisis in the country and ensure sustainable water supply and distribution management, the implementation of proper management methods based on sustainability principles is one of the most fundamental needs. This study was conducted with the aim of investigating water and wastewater management in small businesses in Qom city with the perspective of drought and environmental threats caused by water shortage in 2021.
Methods: The present research is a descriptive-cross-sectional study that was conducted after field survey and statistics obtained from the Water and Wastewater Department on 223 trades related to 67 guilds in the city of Qom. The amount of water consumption, wastewater production, and the management of water and wastewater in businesses were studied with a focus on drought and environmental threats resulting from water scarcity, and the results were reported descriptively.
Results: Considering the amount of water consumption, businesses were classified into four categories. It was determined that businesses in category one, 96.82% of businesses with an average consumption of 246.2 &#177; 574.2, category two businesses, 17.47% with an average of 6142.3 &#177; 2823.19, category three businesses, 36.4% with an average of 121.2 &#177; 5.40, and category four businesses, 83.5% with an average water consumption of 821.215 &#177; 28.355 cubic meters per month, were in terms of efficiency, respectively, in businesses from one to four, 08.61, 25.56, 33.33, and 46.38% of businesses lacked a specific plan for water conservation
Conclusion: The results show that the management of water and wastewater in businesses in the city of Qom does not have favorable conditions. Considering the decrease in rainfall and drought, it seems that the issue of water supply may be the biggest challenge in this city. Most of the businesses under study lack a specific plan for water conservation, and water resource managers should make decisions regarding compensating for water scarcity and preventing water quality degradation while accurately estimating and evaluating water resources and consumption.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>228</FPAGE>
			<TPAGE>238</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/182024/02/22024/02/202023/12/192024/04/24
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/2/5
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/162024/04/82024/04/72024/04/72024/05/8
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/2/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>اکبر</Name>
				<MidName></MidName>
				<Family>اسکندری</Family>
				<NameE>Akbar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Eskandari</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی بهداشت محیط، کمیته تحقیقات دانشجویی، دانشگاه علوم پزشکی تبریز، تبریز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>scandari!12@YAHOO.COM</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>درویش متولی</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Darvishmotevalli</FamilyE>
				<Organizations>
				<Organization>مرکز تحقیقات بهداشت، ایمنی و محیط، دانشگاه علوم پزشکی البرز، کرج، ایران-گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی البرز ، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mohamad.darvish68@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سمیرا</Name>
				<MidName></MidName>
				<Family>بهرامی واله</Family>
				<NameE>Samira</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Bahrami Vale</FamilyE>
				<Organizations>
				<Organization>کارشناس بهداشت عمومی، دانشکده بهداشت، دانشگاه علوم پزشکی قزوین، قزوین، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>samira1989bahrami@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>فهیمی نیا</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Fahiminia</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی قم، قم، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>fahiminia.m@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Water and Wastewater Management</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Drought</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Small Businesses</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Qom City</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدیریت آب و فاضلاب</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خشکسالی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مشاغل کوچک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شهر قم</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Jahangir, M. H.; Khoshmashraban, M.; Yousefi, H. Drought monitoring with Standard Precipitation Index (SPI) and drought forecasting with Multi-layers perceptron (Case study: Tehran and Alborz Provinces). 2016, 2 (4), 417-428(in Persian).##World Disasters Report 2014 - publications and reports-data; Available from: http://www.ifrc.org/en/publications-andreports/world-disasters-report/world-disastersreport-2014/world-disasters-report-2014---data/.##Bazi, K.; khosravy, S.; javadi, M.; Nejad, M. H. Water crisis in the Middle East (challenges and solutions). Proceedings of the Fourth International Congress of Geographers of the Islamic World 2010, 1-15 (in Persian).##Bostani, A.; Ansari, H. Investigating consumption approach in urban water demand management. Journal of Agricultural Engineering and Natural Resources Engineering 2012, 9 (33), 48-52 (in Persian).##Ashourei, A.; Ahadi, A. Implementation of GIS and its application in management and decision-making in water and waste water companies. Journal of Water and Sustainable Development 2016, 2 (2), 1-8(in Persian).##Fatehi Marj, A.; Hydarian, S. A. Climatolgical, Hydrological and Agricultural Drought investigation using Geographic Information System in Ghozestan province, Iran. Iran-Watershed Management Science &#38; Engineering 2014, 7 (23), 19-32)(in Persian).##Salvitabar, A.; Zarghami, M.; Abrishamchi, A. System dynamic model in Tehran urban water management. Water Wastewater J 2006, 17 (3), 12-28(in Persian).##Abdolghafoorian, A.; Tajrishy, M.; Abrishamchi, A. Urban water management considering reclaimed wastewater and runoff as a new water resource for city of Tehran, Iran. J. of Water and Wastewater 2011, 84, 29-42 (in Persian).##Rees, J. A. Risk and integrated water management; Global Water Partnership, 2002.##Monavari, M.; Malmasi, S.; Arjmandi, R.; Samadi Tari, Z. To evaluate the environmental impacts of industrial development in the city of Shahriar. Journal of Environmental Sciences and Technology 2008, 10 (2), 63-73(in Persian).##Taghvaie, M.; Shaykh Bayglou, R.; Eshagh Davatgar, L. Analysis of pollutions resulted from jobs in isfahan. Journal of Environmental Studies 2011, 36 (56), 111-122(in Persian).##Changani, F.; Asadi, A.; Haghighat, G. A.; Mahvi, A. H. Characterization of Carpet Cleaning Wastewater in Tehran, Iran. Iranian Journal of Health &#38; Environment 2012, 5 (2), 99-106(in Persian).##Javid, A.; Hassani, A.; Gahvareband, S. Investigation on quality and quantity of food industrial wastewaters and its effect on the wastewater system operation (case study: Minoo industrial company-khorramdarreh. Journal of Environmental Sciences and Technology 2015, 17 (1), 39-47(in Persian).##Farzadkia, M.; Karimaee, M.; Nabizadeh, R.; Kalantary, R.; Gohari, M.; Karami, M. Environmental ranking of industries located at west of Tehran based on the quantitative and qualitative characteristics of industrial wastewaters in 2011. Iran Occupational Health 2013, 9 (4), 13-23(in Persian).##Hagigi, M.; Niri , A. Review of environmental factors on small business marketing plan Iran. Knowledge management 1996, (33and34), (in Persian).##Irannjhad MH, B. H., Bageri H, Naini MR, Srezai A, Atahi MM, et al. Evaluation of the quality and quantity of green space the city of Qom and solutions to achieve optimal situation. The third national conference on green space and urban landscape The National Conference of green space and urban landscape. 2008(in Persian).##Ganadi, M. Replacing the &#34;water quality engineering&#34; management model with &#34;water health&#34; is a way to supply and distribute drinking water. Congress of Iranian Water and Wastewater Engineering Sciences 2017, 1-10 (in Persian).##Yazdandoost, F.; Noruzi, M. M. Role of Non-Conventional Waters in Arid Regions from an Integrated Water Resources Management Perspective. Irrigation and Water Engineering 2020, 10 (3), 127-141(in Persian).##Bazdar, M.; Godini, H.; Tarrahi, M. J.; Zare, S.; Yarahmadi, M.; Mohammadian Zafarabadi, J.; Ahmadifard, T. Investigating the impact of training on water consumption saving in Khorramabad in 2015. Journal of Environmental Health Enginering 2016, 4 (1), 1-9(in Persian).##Maleki Nasab, A.; Abrishamchi, A.; Tajrishy, M. Assessment of Residential Water Conservation due to Using Low-Flow Fixtures. Journal of Water and Wastewater; Ab va Fazilab ( in persian ) 2007, 18 (2), 2-11(in Persian).##Shayegan, J.; Afshari, A. The treatment situation of municipal and industrial wastewater in Iran. J. Water and Wastewater 49: 58-69. Farsi: 2004; pp 58-69 (in Persian).##Velayati, S.; Rassouli, M. B.; Fashaee, M.; Zeynali, M.; Samiee Deloee, M. The Determination of Water Usage of Watering Coolers in Shadow and Sunshine. Iran-Water Resources Research 2011, 7 (3), 85-88 (in Persian).##Changani, F.; Asadi, A.; Haghighat, G. A.; Mahvi, A. H. Characterization of Carpet Cleaning Wastewater in Tehran, Iran. Iranian Journal of Health &#38; Environment 2012, 5 (2), 99-106 (Persian).##TAKDASTAN, A.; AZIMI, A.; SALARI, Z. The use of electrocoagulation process for removal of turbidity, COD, detergent and phosphorus from carwash effluent. Journal of Water &#38; Wastewater 2011, 3 (22), 19-25(in Persian).##Fahiminia, M.; Sadeghi, H.; Bakhtiari, H. Survey of wastewater management status in urban areas In Iran. Journal of Health 2011, 2 (3), 40-47 (in Persian).##Farrokhi, M.; Hajrasoliha, M.; Meemari, G.; Fahiminia, M.; Talebi, M.; Kohansal, M. The creation of management systems for funding priorities in wastewater project in rural communities in the Islamic Republic of Iran. Water Science &#38; Technology 2008, 58 (6), 1181-1186 (in Persian).## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بهینه سازی فرایند اکسیداسیون پیشرفته سونوالکتروشیمیایی با الکترود گرافن-گرافن در ارتقا کیفیت پساب خروجی تصفیه خانه شهر پرند</TitleF>
		<TitleE>Optimization of advanced sonoelectrochemical oxidation process with graphene-graphene electrode in improving the quality of Parand city wastewater treatment plant</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: حضور آلاینده&#173;های نوظهور در فاضلاب، فرایندهای تصفیه&#173; بیولوژیکی را با مشکل مواجهه کرده است. فرایندهای اکسیداسیون پیشرفته، فرایندهایی امیدوارکننده&#173;ای در ارتقای کیفیت پساب هستند. هدف از این مطالعه بهینه&#173;سازی فرایند سونوالکتروشیمیایی در ارتقا کیفیت پساب خروجی تصفیه&#173;خانه شهر پرند بود.
مواد و روش ها: پایلوت مطالعه شامل یک راکتور سونوالکتروشیمیایی به حجم 500 میلی لیتر مجهز به&#160; مولد جریان برق مستقیم، التراسونیک و الکترودهای گرافن بود. متغیرهای pH (4-8)، جریان الکتریکی مستقیم (50-100 میلی آمپر)، زمان واکنش (60-120 دقیقه) و فرکانس (30-50 کیلوهرتز) توسط طراحی ترکیبی مرکزی بهینه&#173;سازی شدند. همچنین سینتیک فرایند، بهره&#173;وری انرژی، تغییرات خصوصیات فیزیکوشیمیایی پساب و اثر هم افزایی مکانیزم&#173;ها مورد سنجش قرار گرفتند. اندازه&#173;گیری پارامترهای تصفیه ای بر اساس روش&#173;های ارائه شده در مرجع آزمایشات آب و فاضلاب انجام شد.
یافته ها: بر اساس شاخص&#173;های P-value و F-value، مدل انتخابی معنادار بود. شرایط بهینه فرایند عبارت است از pH برابر 5/6، شدت جریان الکتریکی برابر 8/82 میلی آمپر، زمان واکنش برابر 113 دقیقه و فرکانس 35 کیلوهرتز. پارامترهای COD، TOC، BOD5، نیتروژن و فسفر به ترتیب 81، 69، 2/93، 96 و 7/94 درصد حذف شدند. سینتیک فرایند از سینتیک درجه اول تبعیت می&#173;کند و ضریب اثر هم&#173;افزایی برابر 62/1 است. میزان بهره&#173;وری انرژی 07/98 میلی&#173;گرم بر لیتر به ازای هرکیلووات ساعت تعیین شد.
نتیجه گیری: فرایند سونوالکتروشیمیایی، قابلیت بکار گیری به&#173;&#8204;عنوان یک فرایند تصفیه پیشرفته را دارد. پیشنهاد می&#8204;شود کارایی فرایند در نمونه پساب واقعی خام نیز، مورد مطالعه و بررسی قرار گیرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background: The presence of emerging-resistant contaminants in wastewater poses challenges to the efficacy of the biological treatment process. Advanced oxidation processes show great potential for enhancing the quality of wastewater. The aim of this study was to enhance the efficacy of the effluent from the Parand City treatment plant through the optimization of the sonoelectrochemical process.
Methods: Pilot used 500 cc sonoelectrochemical reactor with direct current generator, ultrasonic, and graphene electrodes. To determine pH (4&#8211;8), direct electric current (50&#8211;100 mA), reaction time (60&#8211;120 min), and frequency (30&#8211;50 kHz), the central composite design was used. We looked at the process pace, energy utilization, waste physical and chemical qualities, and overall impact. The purification parameters were obtained using water and wastewater testing methods.
Results: The P-value and F-value indicate the selected model was significant. The best process conditions to use are a pH of 6.5, an electric current intensity of 82.8 mA, a reaction time of 113 min, and a frequency of 35 kHz. Under these conditions, the removal of COD, TOC, BOD5, nitrogen, and phosphorus was 81%, 69%, 93.2%, 96%, and 94.7%, respectively. The kinetics of the process follow first-order kinetics, and the synergistic effect coefficient was 1.62. The energy efficiency was determined to be 98.07 mg/kWh.
Conclusion: The utilization of the sonoelectrochemical process can be employed as a sophisticated method for treatment. However, it is imperative to conduct a comprehensive analysis of the process&#39;s efficacy by utilizing raw wastewater samples.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>239</FPAGE>
			<TPAGE>255</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/02/262024/04/232024/02/182024/02/22024/02/202023/12/192024/04/242023/11/30
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/9/9
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/04/72024/04/292024/04/162024/04/82024/04/72024/04/72024/05/82024/04/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/1/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>پرویز</Name>
				<MidName></MidName>
				<Family>عبدی</Family>
				<NameE>Parviz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Abdi</FamilyE>
				<Organizations>
				<Organization>دانشجوی دکتری مهندسی محیط زیست، دانشکده هنر و معماری، واحد تهران غرب، دانشگاه آزاد اسلامی، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>p.abdi21@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>کبری</Name>
				<MidName></MidName>
				<Family>وریج کاظمی</Family>
				<NameE>Kobra</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Vardijkazemi</FamilyE>
				<Organizations>
				<Organization>عضو هیات علمی گروه فنی مهندسی، دانشگاه آزاد اسلامی واحد تنکابن، تنکابن، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Vardijkazemi@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>آرزو</Name>
				<MidName></MidName>
				<Family>نجایی</Family>
				<NameE>Arezo</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Nejaei</FamilyE>
				<Organizations>
				<Organization>دانشگاه آزاد اسلامی واحد تبریز، دانشکده کشاورزی و منابع طبیعی، گروه محیط زیست، تبریز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Arezo.N@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>افشین</Name>
				<MidName></MidName>
				<Family>تکدستان</Family>
				<NameE>Afshin</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Takdastan</FamilyE>
				<Organizations>
				<Organization>مرکز تحقیقات فناوری های زیست محیطی، دانشگاه علوم پزشکی جندی شاپور اهواز، اهواز ،ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Afshin_ir@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Sonoelectrochemical process</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Chemical Oxygen Demand</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Biochemical Oxygen Demand</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Total Organic Carbon</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Wastewater Treatment</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فرایند سونوالکتروشیمیایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اکسیژن خواهی شیمیایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اکسیژن خواهی بیوشیمیایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کل کربن آلی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تصفیه فاضلاب</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Baharvand S, Daneshvar MRM. Impact assessment of treating wastewater on the physiochemical variables of environment: a case of Kermanshah wastewater treatment plant in Iran. Environmental Systems Research. 2019;8(1):18.##Bonomo L, Pastorelli G, Zambon N. Advantages and limitations of duckweed-based wastewater treatment systems. Water Science and technology. 1997;35(5):239.##Mehralipour J, Kermani M. Ultrasonic coupling with electrical current to effective activation of Persulfate for 2, 4 Dichlorophenoxyacetic acid herbicide degradation: modeling, synergistic effect, and a by-product study. Journal of Environmental Health Science and Engineering. 2021;19:625-39.##Amor C, Marchão L, Lucas MS, Peres JA. Application of advanced oxidation processes for the treatment of recalcitrant agro-industrial wastewater: A review. Water. 2019;11(2):205.##Samarghandi M, Rahmani A, Darabi Z, et al. Performance evaluation of electroproxone process in degradation of ceftriaxone pharmaceutical compound from synthetic solution. Iranian Journal of Health and Environment. 2020;12(4):515-30 [In Persian].##Azimzadeh M, Rahaie M, Nasirizadeh N, et al. An electrochemical nanobiosensor for plasma miRNA-155, based on graphene oxide and gold nanorod, for early detection of breast cancer. Biosensors and Bioelectronics. 2016;77:99-106.##Rahmani A, Leili M, Mehralipor J, et al. Evaluation the performance of electro per sulfate process by using copper-iron electrodes in removing of Aniline from Aqueous solution. Journal of Sabzevar University of Medical Sciences. 2019;26(2):225-32 [In Persian].##Kashi G, Hydarian N. Optimization Electrophotocatalytic Removal of Sulfanilamide From Aqueous Water by Taguchi Model. Issues. 2014;1(1).##Kalet SZ, Ismail SA, Ang WL, et al. Influence of ultrasound modes on sonoelectrochemical degradation of Congo red and palm oil mill effluent. Results in Chemistry. 2023;5:100880.##Tong H, Li H-L, Zhang X-G. Ultrasonic synthesis of highly dispersed Pt nanoparticles supported on MWCNTs and their electrocatalytic activity towards methanol oxidation. Carbon. 2007;45(12):2424-32.##Ojo BO, Arotiba OA, Mabuba N. Sonoelectrochemical degradation of ciprofloxacin in water on a Ti/BaTiO3 electrode. Journal of Environmental Chemical Engineering. 2022;10(2):107224.##Reghioua A, Barkat D, Jawad AH, et al. Parametric optimization by Box-Behnken design for synthesis of magnetic chitosan-benzil/ZnO/Fe3O4 nanocomposite and textile dye removal. Journal of Environmental Chemical Engineering. 2021;9(3):105166.##Rice EW, Bridgewater L, Association APH. Standard methods for the examination of water and wastewater: American public health association Washington, DC; 2012.##Mehralipour J, Jonidi Jafari A, Gholami M, et al. Investigation of photocatalytic-proxone process performance in the degradation of toluene and ethyl benzene from polluted air. Scientific Reports. 2023;13(1):4000.##Visco G, Campanella L, Nobili V. Organic carbons and TOC in waters: an overview of the international norm for its measurements. Microchemical Journal. 2005;79(1-2):185-91.##Gold AC, Thompson SP, Piehler MF. Nitrogen cycling processes within stormwater control measures: a review and call for research. Water research. 2019;149:578-87.##Ren Y-Z, Franke M, Anschuetz F, Ondruschka B, Ignaszak A, Braeutigam P. Sonoelectrochemical degradation of triclosan in water. Ultrasonics Sonochemistry. 2014;21(6):2020-5.##Heebner A, Abbassi B. Electrolysis catalyzed ozonation for advanced wastewater treatment. Journal of Water Process Engineering. 2022;46:102638.##Ai Z, Li J, Zhang L, Lee S. Rapid decolorization of azo dyes in aqueous solution by an ultrasound-assisted electrocatalytic oxidation process. Ultrasonics sonochemistry. 2010;17(2):370-5.##Xu Y, Wang C, Huang Y, Fu J. Recent advances in electrocatalysts for neutral and large-current-density water electrolysis. Nano Energy. 2021;80:105545.##Wu S, Hu YH. A comprehensive review on catalysts for electrocatalytic and photoelectrocatalytic degradation of antibiotics. Chemical Engineering Journal. 2021;409:127739.##Abdurahman MH, Abdullah AZ, Shoparwe NF. A comprehensive review on sonocatalytic, photocatalytic, and sonophotocatalytic processes for the degradation of antibiotics in water: Synergistic mechanism and degradation pathway. Chemical Engineering Journal. 2021;413:127412.##Chen S, Chen J, Xingyu, Xi G, et al. Sonoelectrochemical oxidation of aged landfill leachate with high-efficiency Ti/PANI/PDMS-Ce-PbO2 anode. Journal of Environmental Chemical Engineering. 2022;10(3):107499.##Frontistis Z. Sonoelectrochemical degradation of propyl paraben: An examination of the synergy in different water matrices. International Journal of Environmental Research and Public Health. 2020;17(8):2621.##Xu L, Wang X, Xu M-L, et al. Preparation of zinc tungstate nanomaterial and its sonocatalytic degradation of meloxicam as a novel sonocatalyst in aqueous solution. Ultrasonics Sonochemistry. 2020;61:104815.##Shende T, Andaluri G, Suri RP. Kinetic model for sonolytic degradation of non-volatile surfactants: Perfluoroalkyl substances. Ultrasonics Sonochemistry. 2019;51:359-68.##Sidnell T, Wood RJ, Hurst J, et al. Sonolysis of per-and poly fluoroalkyl substances (PFAS): A meta-analysis. Ultrasonics sonochemistry. 2022;87:105944.##Wang J, Jiang Y, Zhang Z, et al. Investigation on the sonocatalytic degradation of congo red catalyzed by nanometer rutile TiO2 powder and various influencing factors. Desalination. 2007;216(1-3):196-208.##Im J-K, Yoon J, Her N, et al. Sonocatalytic-TiO2 nanotube, Fenton, and CCl4 reactions for enhanced oxidation, and their applications to acetaminophen and naproxen degradation. Separation and Purification Technology. 2015;141:1-9.##AlJaberi FY, Ahmed SA, Makki HF, et al. Recent advances and applicable flexibility potential of electrochemical processes for wastewater treatment. Science of The Total Environment. 2023;867:161361.##Romero‐Soto I, Dia O, Leyva‐Soto LA, et al. Degradation of chloramphenicol in synthetic and aquaculture wastewater using electrooxidation. Journal of environmental quality. 2018;47(4):805-11.##Zhang Q, Huang W, Hong J-m, et al. Deciphering acetaminophen electrical catalytic degradation using single-form S doped graphene/Pt/TiO2. Chemical Engineering Journal. 2018;343:662-75.##Jiang H, Zhang K, Li W, et al. MoS2/NiS core-shell structures for improved electrocatalytic process of hydrogen evolution. Journal of Power Sources. 2020;472:228497.##Cui X, Zhang B, Zeng C, et al. Monolithic nanoporous NiFe alloy by dealloying laser processed NiFeAl as electrocatalyst toward oxygen evolution reaction. International Journal of Hydrogen Energy. 2018;43(32):15234-44.##Sun Q, Zhou M, Shen Y, et al. Hierarchical nanoporous Ni (Cu) alloy anchored on amorphous NiFeP as efficient bifunctional electrocatalysts for hydrogen evolution and hydrazine oxidation. Journal of catalysis. 2019;373:180-9.##Secula MS, Cagnon B, de Oliveira TF, et al. Removal of acid dye from aqueous solutions by electrocoagulation/GAC adsorption coupling: Kinetics and electrical operating costs. Journal of the Taiwan Institute of Chemical Engineers. 2012;43(5):767-75.##Tafoya JPV, Doszczeczko S, Titirici MM, et al. Enhancement of the electrocatalytic activity for the oxygen reduction reaction of boron-doped reduced graphene oxide via ultrasonic treatment. International Journal of Hydrogen Energy. 2022;47(8):5462-73.##Zhao H, Gao J, Zhao G, et al. Fabrication of novel SnO2-Sb/carbon aerogel electrode for ultrasonic electrochemical oxidation of perfluorooctanoate with high catalytic efficiency. Applied Catalysis B: Environmental. 2013;136-137:278-86.##Gągol M, Przyjazny A, Boczkaj G. Wastewater treatment by means of advanced oxidation processes based on cavitation-a review. Chemical Engineering Journal. 2018;338:599-627.##Fedorov K, Dinesh K, Sun X, et al. Synergistic effects of hybrid advanced oxidation processes (AOPs) based on hydrodynamic cavitation phenomenon - A review. Chemical Engineering Journal. 2022;432:134191.##Horáková M, Klementová Š, Kříž P, et al. The synergistic effect of advanced oxidation processes to eliminate resistant chemical compounds. Surface and Coatings Technology. 2014;241:154-8.##Velmurugan S, Palanisamy S, C-K Yang T, et al. Ultrasonic assisted functionalization of MWCNT and synergistic electrocatalytic effect of nano-hydroxyapatite incorporated MWCNT-chitosan scaffolds for sensing of nitrofurantoin. Ultrasonics Sonochemistry. 2020;62:104863.##Ang WL, McHugh PJ, Symes MD. Sonoelectrochemical processes for the degradation of persistent organic pollutants. Chemical Engineering Journal. 2022:136573.##Shestakova M, Vinatoru M, Mason TJ, et al. Sonoelectrochemical degradation of formic acid using Ti/Ta2O5-SnO2 electrodes. Journal of Molecular Liquids. 2016;223:388-94.##Patidar R, Srivastava VC. Ultrasound-assisted electrochemical treatment of cosmetic industry wastewater: Mechanistic and detoxification analysis. Journal of Hazardous Materials. 2022;422:126842.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

</ARTICLES>

</JOURNAL>
</XML>
