<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1399</YEAR>
<VOL>7</VOL>
<NO>4</NO>
<MOSALSAL>29</MOSALSAL>
<PAGE_NO>509</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>بررسی کارایی کیتوزان نانومغناطیسی شده در حذف نیترات و فسفات از محلول‌های آبی</TitleF>
		<TitleE>Evaluation of the efficiency of nanomagnetic chitosan in the removal of nitrate and phosphate from aqueous solutions</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف:&#160; حضور نیترات و فسفات در غلظتهای بالای حد مجاز در منابع آب سطحی و زیرزمینی منجر به ایجاد بیماری و مشکل در منابع آب سطحی می گردند. هدف این مطالعه، بررسی کارایی جاذب نانوکامپوزیت کیتوزان مغناطیسی-متالیک در حذف نیترات و فسفات از محلولهای آبی می باشد.
روش کار: جاذب توسط روش هم ترسیبی سنتز گردید. غلظتهای مختلف نیترات (mg/L 300-50)&#160; و فسفات (mg/L 400-100) تهیه شده و مقدار حذف آنها توسط غلظتهای مختلف جاذب سنتز شده (g/L 5-1) بررسی شد. پارامترهای مختلف نظیر دما (C&#176; 40-20)، pH (8-5)، زمان تماس (90-0 دقیقه) و حضور یونهای مداخله گر (کلرور، فسفات، سختی mM 5/1) بررسی شد. برای تعیین مشخصات جاذب سنتز شده از آزمایشات SEM، XRD، FTIR و XRF استفاده شد.
&#160;یافته ها:&#160; جاذب نانوکامپوزیت کیتوزان مغناطیسی-متالیک قادر به حذف موثر نیترات و فسفات از محلولهای آبی می باشد. راندمان حذف نیترات و فسفات در شرایط 5=pH، غلظت نیترات (mg/L 100)، غلظت فسفات (mg/L 200)، زمان ماند 60 دقیقه و غلظت جاذب g/L 3/0 به ترتیب برابر 87.2% و 74.9% بود. فرآیند جذب هر دو آلاینده از مدل فروندلیخ و سینتیک شبه درجه دوم تبعیت نموده که در دماهای بالا، گرمازا بود. یونهای مداخله گر باعث کاهش راندمان حذف آلاینده ها تا 73.1% برای نیترات و 65.9% برای فسفات بود.
نتیجه گیری: از آنجایی که حضور آنیونهای مزاحم نیترات و فسفات، به عنوان آلاینده های متداول و شاخص منابع آبی مطرح می باشند، استفاده از جاذب نانوکامپوزیت کیتوزان مغناطیسی-متالیک در حذف این آلاینده ها بسیار موثر می باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background &#38; Objective: The presence of nitrate and phosphate in concentrations above the allowable level in surface and groundwater resources leads to disease and problems. The aim of this study was to investigate the adsorption efficiency of magnetic-metallic chitosan nanocomposite in the adsorption of nitrate and phosphate from aqueous solutions.
Materials and methods: The adsorbent was synthesized by co-precipitation method. Different concentrations of nitrate (50-300 mg/L) and phosphate (100-400 mg/L) were prepared and their removal was evaluated by different concentrations of synthesized adsorbent (0.1-0.5 g/L). Various parameters such as temperature (20-40 &#176; C), pH (5-8), contact time (0-90 minutes) and the presence of interfering ions (chloride, phosphate, hardness 1.5 mM) were investigated. SEM, XRD, FTIR and XRF tests were used to determine the synthesized adsorbent characteristics.
Results: Magnetic-metallic chitosan nanocomposite adsorbent is able to effectively remove nitrate and phosphate from aqueous solutions. Nitrate and phosphate removal efficiencies under conditions of &#160;pH=5, nitrate concentration (100 mg/L), phosphate concentration (200 mg/L), 60 min contact time and 0.3 g/L adsorbent concentration were 87.2% and 74.9%, respectively. The adsorption process of both pollutants followed the langmuir model and pseudo second kinetic order. Interfering ions reduced the removal efficiency of contaminants by 73.1% for nitrate and 65.9% for phosphate.
Conclusion: Since the presence of nitrate and phosphate anions, as common contaminants and indicators of water resources, the use of magnetic-metallic chitosan nanocomposite adsorbent is very effective in the removal of these contaminants.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>373</FPAGE>
			<TPAGE>383</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/2
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/7/10
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/3/18
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>نوری سپهر</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Noorisepehr</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط ، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران 2 مرکز تحقیقات بهداشت، ایمنی و محیط (RCHSE)، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>عماد</Name>
				<MidName></MidName>
				<Family>دهقانی فرد</Family>
				<NameE>Emad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dehghanifard</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط ، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران 2 مرکز تحقیقات بهداشت، ایمنی و محیط (RCHSE)، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بابک</Name>
				<MidName></MidName>
				<Family>کاکاوندی</Family>
				<NameE>Babak</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Kakavandi</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط ، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران 2 مرکز تحقیقات بهداشت، ایمنی و محیط (RCHSE)، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>: Chitosan</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Magnetic iron oxide</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Nitrate</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Phosphate</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Adsorption</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کیتوزان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اکسید آهن مغناطیسی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نیترات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فسفات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جذب سطحی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Katal R, Baei MS, Rahmati HT, Esfandian H. Kinetic, isotherm and thermodynamic study of nitrate adsorption from aqueous solution using modified rice husk. J Ind Eng Chem 2012; 18:295-302.##2.	WHO. Guidelines for Drinking-Water Quality. 4th Edition, World Health Organization, 2011.##3.	Yuan X, Bai C, Xia W, Xie B, An J. Phosphate adsorption characteristics of wasted low-grade iron ore with phosphorus used as natural adsorbent for aqueous solution. Desalin Water Treat 2014: 1-11.##4.	Emmanuelawati I, Yang J, Zhang J, Zhang H, Zhou L, Yu C. Low-cost and large-scale synthesis of functional porous materials for phosphate removal with high performance. Nanoscale 2013;5:6173-80.##5.	Blachnio M, Budnyak TM, Derylo-Marczewska A, Marczewski AW, Tertykh VA. Chitosan–silica hybrid composites for removal of sulfonated azo dyes from aqueous solutions. Langmuir 2018;34:2258-73. ##6.	Chang YC, Chen DH. Preparation and adsorption properties of monodisperse chitosan-bound Fe&#60; sub&#62; 3&#60;/sub&#62; O&#60; sub&#62; 4&#60;/sub&#62; magnetic nanoparticles for removal of Cu (II) ions. J Colloid Interf Sci 2005;283:446-51.##7.	Karaca E, Şatır M, Kazan S, Açıkgöz M, Öztürk E, Gürdağ G, Ulutaş D. Synthesis, characterization and magnetic properties of Fe3O4 doped chitosan polymer. J Magnet Magnet Mater 2015;373:53-9.##8.	Jiang H, Chen P, Luo S, Tu X, Cao Q, Shu M. Synthesis of novel nanocomposite Fe3O4/ZrO2/chitosan and its application for removal of nitrate and phosphate. Appl Surf Sci 2013;284:942-9.##9.	Sowmya A, Meenakshi S. Effective removal of nitrate and phosphate anions from aqueous solutions using functionalised chitosan beads. Desalin Water Treat 2014;52:2583-93.##10.	Aswin Kumar I, Viswanathan N. Development and reuse of amine-grafted chitosan hybrid beads in the retention of nitrate and phosphate. J Chem Eng Data 2018;63:147-58.##11.	Mirzaei M, Behzad Q, Hadi M, Jahangir AS. Removal of calcium, magnesium, chlorine and bicarbonate ions from saline by modified mineral adsorbent. 6th National Conference on Environmental Engineering; Faculty of Environment, Tehran University, Tehran, 2012 [In Persian].##12.	Khodadadi M, Saghi MH, Azadi NA, Sadeghi S. Adsorption of Chromium VI from Aqueous Solutions onto Nanoparticle Sorbent: Chitozan-Fe-Zr. J Mazandaran Univ Med Sci 2016;26(141):70-82 [In Persian].##13.	Banu HT, Meenakshi S. One pot synthesis of chitosan grafted quaternized resin for the removal of nitrate and phosphate from aqueous solution. Int J Biol Macromolecul 2017;104:1517-27.##14.	Bozorgpour F, Ramandi HF, Jafari P, Samadi S, Yazd SS, Aliabadi M. Removal of nitrate and phosphate using chitosan/Al2O3/Fe3O4 composite nanofibrous adsorbent: comparison with chitosan/Al2O3/Fe3O4 beads. Int J Biol Macromolecul 2016;93-557-65.##15.	Karthikeyan P, Banu HAT, Meenakshi S. Synthesis and characterization of metal loaded chitosan-alginate biopolymeric hybrid beads for the efficient removal of phosphate and nitrate ions from aqueous solution. Int J Biol Macromolecul 2019;130:407-18.##16.	Pouretedal H, Sadegh N. Effective removal of Amoxicillin, Cephalexin, Tetracycline and Penicillin G from aqueous solutions using activated carbon nanoparticles prepared from vine wood. J Water Proc Eng 2014;1:64-73.##17.	Mohammadi E, Daraei H, Ghanbari R, Athar SD, Zandsalimi Y, Ziaee A, Maleki A, Yetilmezsoy K. Synthesis of carboxylated chitosan modified with ferromagnetic nanoparticles for adsorptive removal of fluoride, nitrate, and phosphate anions from aqueous solutions. J Molecular Liq 2019;273:116-24.##18.	Dutta M, Dutta N, Bhattacharya K. Aqueous phase adsorption of certain beta-lactam antibiotics onto polymeric resins and activated carbon. Sep Purif Technol 1999;16(3):213-24.##19.	Ghodrat M, Asrari E. Comparative study of the performance of chitosan and chitosan adsorbents modified with Fe3O4 to eliminate erythromycin from aqueous solutions. Iran J Health Env 2018;10:471-82.##20.	Rafiei HR, Shirvani M. Sorption of Lead (Pb) from Aqueous Solutions by Sepiolite and Bentonite Modified with Chitosan Biopolymers: Isotherms and Kinetics. Water Wastewater J 2016; 27(3):75-87 [In Persian].## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی کارآیی فرآیند فتوکاتالیستی پرتوی فرابنفش و نانو ذرات TiO2 مغناطیسی با ساختار پوسته/هسته در حذف آنتی‌بیوتیک سفیکسیم از محلول‌های آبی</TitleF>
		<TitleE>Apllication of photocatalitic process using Fe3O4/ TiO2 nanocomposite coreshell on the removal of Cefixim antibiotic from aqueous solutions</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: آنتی&#8204;بیوتیک&#8204;ها جزو آلاینده&#8204;های زیست&#8204;محیطی دارای اثرات پایدار هستند. هدف از این پژوهش تعیین راندمان حذف آنتی&#8204;بیوتیک سفیکسیم از محلول&#8204;های آبی توسط فرآیند فتوکاتالیستی پرتوی فرابنفش و نانو ذرات TiO2 مغناطیسی با ساختار پوسته/هسته است.
روش کار: این مطالعه از نوع مطالعات تجربی&#8211;آزمایشگاهی محسوب می&#8204;شود. متغیرهای موردنظر شامل pH (9-5)، غلظت آلایندهmg/L 10-2، غلظت فتوکاتالیست (g/L 5-5/0) بررسی شدند. فاضلاب سنتتیک برای هر مرحله از آزمایش به حجم یک لیتر بود. کلیه آزمایش&#8204;ها در رآکتور استیل ضدزنگ با جریان برگشتی انجام شد. زمان نمونه&#8204;گیری برای کلیه&#8204;ی متغیر یکسان بود. برای تعیین راندمان حذف آنتی&#8204;بیوتیک سفیکسیم از دستگاه HPLC استفاده گردید. فتوکاتالیست سنتز شده با استفاده از آنالیزهای SEM، XRD، VSM مورد ارزیابی قرار گرفت.
&#160;یافته ها: نتایج آنالیز مشخصات فیزیکی نشان داد که نانو ساختار مغناطیسی هسته/پوسته TiO2 دارای اندازه متوسط nm 10 بوده است. فرآیند فتو کاتالیستی پرتوی فرابنفش و نانو ذرات Tio2 مغناطیسی با ساختار پوسته/هسته قادر به حذف 100% آلاینده سفیکسیم (غلظت mg/L 2 در مدت 25 دقیقه در 6=pH و با غلظت کاتالیست g/L 4) صورت گرفت. بررسی مدل&#8204;های سنیتیکی نشان داد که روند حذف فتوکاتالیستی سفیکسیم از مدل درجه اول پیروی می&#8204;کند.
نتیجه گیری: نتایج این پژوهش نشان داده است که فرآیند فتو کاتالیستی پرتوی فرابنفش و نانو ذرات TiO2 مغناطیسی با ساختار پوسته/هسته به&#8204;طور بسیار مؤثر می&#8204;تواند در حذف کامل سفیکسیم از محیط&#8204;های آبی به کار رود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background &#38; Objective: Antibiotics are considered among the pollutants in water environments with stable effects. This study aimed to investigate the efficiency of photocatalytic process using core&#8211;shell TiO2 under ultraviolet radiation for the removal of Cefixime antibiotic from aqueous solutions.
Materials and methods: This study was conducted in an experimental-laboratory scale. The effect of factors such as pH (5, 6, 7, 8 and 9), initial concentrations of Cefixime (2-10 mg/L) and concentrations of catalyst (0.5-5 g/L) was surveyed. Sample volume for every step of the experiments was 1000 ml. A batch stainless steel 3L photo catalytic reactor was designed. The synthesized catalyst was characterized by SEM ، XRD and VSM Methods.
Results: Physical characteristics of the Fe3O4/SiO2/TiO2 revealed that the catalyst particles had the average size of 10 nm. The photocatalytic degradation of Cefixime with UV+ Fe3O4/SiO2/TiO2 in the optimal condition was 100% (pH =6, retention time= 25 min, Cefixime concenteration= 2 mg/L catalyst dosage= 4 g/L). Synthetic models showed that the process of photocatalytic removal of Cefixime followed the first-order model.
Conclusion: The results of this study suggested that UV+ Fe3O4/SiO2/TiO2 process is very effective method for the complete removal of Cefixime antibiotic from aqueous solutions.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>384</FPAGE>
			<TPAGE>400</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/25
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/6/4
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/23
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/6/2
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فرانک</Name>
				<MidName></MidName>
				<Family>الماسی</Family>
				<NameE>Faranak</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Almasi</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>عماد</Name>
				<MidName></MidName>
				<Family>دهقانی فرد</Family>
				<NameE>Emad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dehghanifard</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران 2 مرکز تحقیقات بهداشت، ایمنی و محیط ((RCHSE، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>ابراهیم</Name>
				<MidName></MidName>
				<Family>محمدی کلهری</Family>
				<NameE>Ebrahim</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi Kalhori</FamilyE>
				<Organizations>
				<Organization>1 گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی البرز، کرج، ایران 2 مرکز تحقیقات بهداشت، ایمنی و محیط ((RCHSE، دانشگاه علوم پزشکی البرز، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Advanced oxidation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Photocatalytic processes</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Cefixime</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Magnetic TiO2 nanoparticles core/shell.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اکسیداسیون پیشرفته</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فرآیند فتوکاتالیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سفیکسیم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نانو ذرات TiO2 مغناطیسی با ساختار پوسته/هسته</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Yazdanbakhsh AR, Sheikhmohammadi A, Sardar M. Investigation the Efficiency of Combined Coagulation and Advanced Oxidation by Fenton Process in the Removal of Clarithromycin Antibiotic COD. J Water Wastewater 2010;23(2):8 [In Persisn]. ##2.	Metcalf E, Eddy M. Wastewater engineering: treatment and Resource recovery. Mic Graw-Hill, USA. 2014:1530-3.##3.	Safari G, Hoseini M, Kamali H, Moradirad R, Mahvi A. Photocatalytic Degradation of Tetracycline Antibiotic from Aqueous Solutions Using UV/TiO2 and UV/H2O2/TiO2. J Health 2014;5(3):203-13[In Persisn].##4.	Baquero F, Martínez J-L, Cantón R. Antibiotics and antibiotic resistance in water environments. Curr Opin Biotechnol 2008;19(3):260-5.##5.	Adam EH, Saeed AE, Barakat IE. Study of degradation of cefixime trihydrate under stress conditions using stability indicating reverse phase-high performance liquid chromatography method. Der Pharma Chem. 2011;3:197-207.##6.	Rahmani A, Mehralipour J, Shabanloo A, Majidi S. 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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>کاربست مدل‌های SWEEP و AERMOD در شبیه‌سازی ریسک انتشار 10 PMاز دپو مواد اولیه و پسماندهای صنایع کاشی سرامیک، خاک چینی و شیشه شهرستان اردکان یزد در سال 1397</TitleF>
		<TitleE>Application of SWEEP and AERMOD Models to Simulate PM10 Emission Risk from Primary Materials and Waste Depos of Tile and Ceramic, Khak-e-Chini and Glass Industries of Ardakan, Yazd, Iran in 2018</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>مقدمه: کاربرد مدل&#173;های کیفیت هوا در سیستم ارزیابی ریسک سلامت به عنوان ابزاری موثر در ارزیابی مواجهه جمعیت انسانی با عوامل زیان آور محیطی تعریف شده است. این تحقیق با هدف ارزیابی ریسک سلامت مواجهه تنفسی با 10PM انتشاریافته از دپو مواد اولیه و پسماندهای تعدادی از صنایع کانی&#8204;های غیرفلزی به روش مدل&#8204;سازی انجام شد.
روش بررسی: در این مطالعه توصیفی ابتدا برای تخمین میزان نشر 10PM از دپوهای صنایع کاشی سرامیک، خاک چینی و شیشه اطلاعات موردنیاز مدل SWEEP با بازدیدهای میدانی و اندازه&#173;گیری&#8204;های آزمایشگاهی تهیه شد. سپس با ورود اطلاعات هواشناسی به AERMET، مدل رقومی ارتفاع به AERMAP، نرخ انتشار و ابعاد هندسی منابع آلاینده به AERMOD مقادیر مواجهه با 10PM &#160;در جمعیت تحت تاثیر شبیه&#173;سازی شد. ترکیب شیمیایی دپو&#8204;ها با استفاده از ICP-MS تعیین گردید. متعاقبا با استفاده از روابط پیشنهادی EPA ریسک سرطان&#173;زایی و غیرسرطان&#173;زایی مواجهه با 10 PM تخمین زده شد. 
یافته&#8204;ها: بر اساس نتایج شبیه&#173;سازی مدل SWEEP بیشترین میزان نشر 10PM برای دپو کارخانه کاشی و سرامیک تخمین زده شد. بیشترین ماکسیمم&#173;های غلظت یک، هشت و 24 ساعته شبیه&#173;سازی شده 10 PM به ترتیب برابر با 8840، 1967 و g/m3&#181; 1272 است. بیشترین میانگین مواجهه تنفسی یک (53/52)، هشت (64/11)، 24 (g/m3&#181; 85/5) ساعته با 10PM برای کارکنان کارخانه فرآوری شن و ماسه تخمین زده شد. بیشترین درصد ترکیب شیمیایی دپوها، سیلیس بود. بر این اساس، مقادیر ریسک&#173; سرطان&#173;زایی (ILCR) مواجهه با 10PM کوچکتر از 4-10 و ریسک غیرسرطانزایی (HQ) کوچکتر از یک پیش&#173;بینی شد.
نتیجه گیری: اگرچه مقادیر عددی ریسک در محدوده مجاز پیش&#173;بینی شد اما می&#173;توان با ایجاد سنگفرش بر روی دپو صنایع تا حدودی میزان انتشار 10PM را کاهش داد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>&#160;
Background: Application of air quality models in Health Risk Assessment system has been defined as an effective tool in assess the human population exposure to environmental harmful factors. The present study was conducted to aim of health risk assessment of respiratory exposure to PM10 Emitted from Depos of primary materials and waste a number of Non-metallic minerals industries by Modeling method.
Methods: In this descriptive study, first to Field visits and laboratory measurements was obtained the information needed for SWEEP model to estimate PM10 emission rate from depos of Tile and Ceramic, Khak-e-chini and glass industries. Then, with the introduction of meteorological information to AERMET, the digital elevation model to AERMAP, the emission rate and the geometric dimensions of the pollutant sources to AERMOD, simulated the values of exposure to PM10 in the affected population. The chemical composition of the depos was determined using ICP-MS. Subsequently, using the EPA suggested relationships was estimated the risk of carcinogenic and non-carcinogenic exposure to PM10.
Results: According to the simulation results of SWEEP model, the highest PM10 emission was estimated for the Tile and Ceramic depo. The highest concentration maximum of 1, 8, and 24 h of PM10 simulated were 8840, 1967, and 1272 &#181;g/m3, respectively. The highest average respiratory exposure of 1 (52.53), 8 (11.64), 24 (5.85 &#181;g/m3) hour to PM10 was estimated for Sand and Gravel processing plant staff. The highest percentage of chemical compounds in depos was for silica. Accordingly, the carcinogenicity risk (ILCR) of exposure to PM10 was predicted less than 10-4 and non- carcinogenicity risk (HQ) less than one.
Conclusion: Although numerical values of risk were predicted in the permissible limit, but to creating Surface rock on the depo industries can reduce the emission of PM10.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>401</FPAGE>
			<TPAGE>426</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/5
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/2/16
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/16
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/5/26
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سعید</Name>
				<MidName></MidName>
				<Family>شجاعی برجوئی</Family>
				<NameE>Saeed</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shojaee Barjoee</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی و کویرشناسی، دانشگاه یزد، یزد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>حمیدرضا</Name>
				<MidName></MidName>
				<Family>عظیم زاده</Family>
				<NameE>HamidReza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Azimzadeh</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی و کویرشناسی، دانشگاه یزد، یزد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>اصغر</Name>
				<MidName></MidName>
				<Family>مصلح آرانی</Family>
				<NameE>Asghar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mosleh Arani</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی و کویرشناسی، دانشگاه یزد، یزد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>PM10</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>AERMOD</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>SWEEP</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Health Risk Assessment</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Respiratory exposure</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>PM10</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>AERMOD</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>SWEEP</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ارزیابی ریسک سلامت</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مواجهه تنفسی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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US Environmental Protection Agency, Guidelines for Carcinogen Risk Assessment. US EPA, Washington, DC http://www epa gov/cancerguidelines 2005.##30.	USEPA. Exposure factors handbook: 2011 edition. USEPA Office of Research and Development Washington.; 2011.##31.	Bureau of Technical Services-Air Quality Evaluation Section. Toxicity Values for Inhalation Exposure. New Jersey Department of Environmental Protection 2011: NJDEP/DAQ/AQEv ToxAll2011.xls 1/30/2.##32.	Sadeghi RMH. Analysis of wind erosion and determination of sand movement direction in Khezrabad region. Watershed Engin  Manage 2018;10(1): 95-107 [In Persian] ##33.	Farzanehpey F, Torabi A, Bakhshinia S, Mesbahzadeh T. The Severity of Wind Erosion Assessment in Ala Region of Semnan Using IRIFR. E. A Model. J Desert Eco Engin 2016;5(10): 99-107 [In Persian] ##34.	Kazemi M, Feiznia S, Khosravi H, Mesbah H. Investigating of Susceptibility of Maharloo Lake Sediments to Wind Erosion and Determination of Dust Movement Direction. Desert Manage 2019;6(12): 49-60  [In Persian] ##35.	Ono DM, Hardebeck E, Schade T. Owens Valley PM10 planning area demonstration of attainment state implementation plan: project alternatives analysis summary. The District 1997.##36.	Afrasyabi S, Tazeh M, Taghizadeh Mehrjardi R, Kalantari S. Performance of two measurement methods of pin meter and laser disto meter in the measurement of microtopography Created by desert pavement. J Desert Eco Engin 2019;8(22): 1-14.##37.	Iranmanesh M, Gharahi N, Pajoohesh M. The Effect of Vegetation Pattern, Biochar and Powdery Walnut Shell on Wind Erosion, Using Wind Tunnel. Desert Manage 2019;7(13): 135-48 [In Persian] ##38.	Feng G, Sharratt B. Evaluation of the SWEEP model during high winds on the Columbia Plateau. Earth Surf Proc Land 2009;34(11): 1461-8.##39.	Mahmoodabadi M, Dehghani F, Azimzadeh H. Effect of soil particle size distribution on wind erosion rate. J Soil Manage Sustain Produc 2011;1(1): 81-97 [In Persian] ##40.	Mahmoodabadi M, Mirzaee M, Naghavi H. Aggregate Size Distribution Indices Influenced by Different Types/Managements of Plant Residues under Field Conditions. J Environ Ero Res 2016;6(3): 52-70.##41.	shahverdi s, nikoo s, mashhadi n, et al. Study of landforms sedimentation based on changes in land use (Case Study: Damghan). J Desert Eco Engin 2016;5(12): 37-50 [In Persian] ##42.	Fadavi A, Abari MF, Nadoushan MA. Evaluation of AERMOD for distribution modeling of particulate matters (Case study: Ardestan Cement Factory). Int J Pharm Res Allied Sci 2016;5(4): 262-70.##43.	Jayadipraja E, Daud A, Assegaf A, Maming M. The application of the AERMOD model in the environmental health to identify the dispersion area of total suspended particulate from cement industry stacks. J Res Med Sci 2016;4(6): 2044-9.##44.	Mokhtar MM, Hassim MH, Taib RM. Health risk assessment of emissions from a coal-fired power plant using AERMOD modelling. Process Saf Environ 2014;92(5): 476-85.##45.	Chaleshtori LA, Nejadkoorki F, Ashrafi K. Performance of AERMOD Under Different Building Forms and Dimensions. Environ Sci 2015;13(1): 15-24 [In Persian] ##46.	Zou B, Zhan FB, Wilson JG, Zeng Y. Performance of AERMOD at different time scales. Simul Model Pract Theory 2010;18(5): 612-23 [In Persian] ##47.	Noorpoor A, Kazemi Shahabi N. Dispersion modeling of air pollutants from the Ilam cement factory stack. J Civil Environ Engin 2014;44(1): 37-44  [In Persian] ##48.	Shamsipour A, Ashrafi E, Alikhah AM, Ashrafi K. Modeling the distribution of suspended particles in the south of Tehran by the model of AERMOD (A Case Study of Tehran cement factory). Environ Sci 2016;41(4): 799-814  [In Persian] ##49.	Fard MR, Rashidi Y, Amiri M. Modeling the emission and calculation of the risk of steelmaking contaminants using the AERMOD model. J Health Field 2018;6(3): 49-59 [In Persian]## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>کارآیی ترکیبات کلات‌کننده با نرخ تجزیه‌پذیری زیستی متفاوت در بهبود عملکرد گیاه‌پالایی خاک‌ آلوده به کادمیوم توسط گونه‌های زینتی تاج‌خروس (Amaranthus caudatus) و گل جعفری (Tagetes patula)</TitleF>
		<TitleE>Evaluation of Chelating Agents with Different Biodegradability Rates on the Enhanced Phytoremediation Efficiency of Ornamental Species (Amaranthus caudatus and Tagetes patula) in Cadmium Contaminated Soils</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: امروزه از آن&#8204;جا که روند فزاینده آلودگی محیط&#173;زیست و بویژه خاک سلامت زیستمندان را تهدید می&#8204;کند، انواع روش&#8204;های پالایش خاک از جمله گیاه&#173;پالایی برای پالایش آلاینده&#8204;های آلی، غیرآلی و هسته&#8204;ای از محل&#8204;های آلوده مورد توجه قرار گرفته&#8204;اند. از این&#8204;رو، این پژوهش با هدف ارزیابی کارآیی عوامل کلات&#173;کننده زیست تجزیه&#173;پذیر در بهبود عملکرد گیاه&#173;پالایی خاک&#173; آلوده به کادمیوم توسط گونه&#173;های زینتی تاج&#173;خروس و گل جعفری در سال 1397 انجام شد.
مواد و روش&#173;ها: در این پژوهش توصیفی، پس از آلوده کردن خاک با 50 و 100 میلی&#8204;گرم در کیلوگرم کلرید کادمیوم و تیمار آن با محلول&#8204;های 50/2، 00/2 و 50/2 میلی&#8204;مول در کیلوگرم EDTA، اسید سالیسیلیک و اسید سیتریک بعنوان عامل کلات&#173;کننده، نسبت به کشت و آبیاری گیاهچه&#8204; گیاهان در گلدان&#8204;های حاوی خاک آلوده&#8204; طی 60 روز اقدام شد. پس از برداشت و هضم اسیدی نمونه&#8204;های خاک تحت کشت، ریشه و شاخساره گیاهان از تیمارهای شاهد و آزمایشی، محتوی کادمیوم در آن&#8204;ها توسط دستگاه طیف&#8204;سنج نشری پلاسمای جفت&#8204;شده القایی تعیین شد.
یافته &#173;ها: بیشینه میانگین غلظت کادمیوم در نمونه&#173;های خاک زیر کشت، ریشه و شاخساره تاج&#173;خروس با 87/1، 50/4 و 89/1 به&#173;ترتیب مربوط به تیمارهای اسید سالیسیلیک، EDTA و اسید سالیسیلیک و در گل جعفری نیز با 86/1، 18/1 و 10/3 به&#173;ترتیب مربوط به تیمارهای فاقد کلات، اسید سیتریک و اسید سالیسیلیک بوده است. از طرفی بر اساس مقادیر فاکتورهای انتقال و انباشت زیستی نتیجه گرفته شد که گونه&#173;های تاج&#173;خروس و گل جعفری به&#8204;ترتیب از قابلیت تثبیت و استخراج گیاهی برخوردار بودند.
نتیجه&#173; گیری: اسیدهای آلی همچون اسید سالیسیلیک و اسید سیتریک از طریق ساز&#173;و&#173;کارهایی مانند اثرات شبه هورمونی، آزادسازی و انحلال فسفات، افزایش تحرک کادمیوم و برخی فعالیت&#173;های آنزیمی، دگرگونی میکرو&#173;ساختاری و کاهش ظرفیت نگه&#173;داری فلزات توسط ذرات رس، نقش مهمی در الکتروکینتیک پالایش خاک دارند. لذا، با توجه به اثر مطلوب اسیدهای آلی بعنوان عوامل کلات&#173;کننده در ارتقا&#173;ی کارایی گیاه&#173;پالایی گونه&#173; های فرا انباشتگر، استفاده از آن&#173;ها در فرآبند آلودگی&#8204;زدایی خاک توصیه می&#173;شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background &#38; Objective: Nowadays, since increasing environmental pollution particularly soil contamination can cause adverse health effects, kind of methods such as phytoremediation techniques are commonly used to remediate organic, inorganic and nuclear pollutants from contaminated sites. Therefore, this study was conducted to assess of chelating agents with different biodegradability rates on the enhanced phytoremediation efficiency of Amaranthus caudatus and Tagetes patula as ornamental species in cadmium contaminated soils in 2018.
Materials &#38; Methods: In pot experiments, the soil specimens were moderately artificially contaminated by cadmium chloride (50 and 100 mg/kg). &#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160; Then 2.5 mmol/kg of EDTA, 2.0 mmol/kg of salicylic acid (SA) and 2.5 mmol/kg of citric acid (CA) solution were added to the contaminated soils to study the influence of these chelating agents on phytoremediation efficiency by studied ornamental plants. Finally, after acid digestion of cultivated soil, roots and stems of A. caudatus and T. patula, the Cd content was determined using ICP-OES.
Results: The results showed that after 60 days of pots irrigation, the maximum mean content of Cd (mg/kg) in cultivated soil, root and stem samples of A. caudatus with 1.87, 4.50 and 1.89 were found in the SA, EDTA and SA treatments, respectively. Moreover, the maximum mean content of Cd in cultivated soil, root and stem samples of T. patula with 1.86, 1.18 and 3.10 were found in the control, CA and SA treatments, respectively. Also, the values of translocation and bioconcentration factors indicate that A. patula can be considered to be potential plant species for phytostabilization and phytoextraction of cadmium, respectively.
Conclusion: The results reported in this study show that the organic acids such as SA and CA have considerable role in soil refining electrokinetic or enhance of soil electrokinetic bioremediation through mechanisms resembling hormonelike effects, phosphate &#160;release and dissolution, enhancing of cadmium mobility and some enzymatic activities, microstructural variations and retention capacity decreasing of clay particles. Therefore, due to the desirable effects of organic acids as chelate agents to enhancing phytoremediation efficiency of hyperaccumulator species use of these compounds in the cleanup of contaminated soil is recommended.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>427</FPAGE>
			<TPAGE>442</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/52020/05/6
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/2/17
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/162020/08/15
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/5/25
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>نسترن</Name>
				<MidName></MidName>
				<Family>عاقلان</Family>
				<NameE>Nastaran</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Aghelan</FamilyE>
				<Organizations>
				<Organization>دانشجوی دکترای تخصصی محیط‌زیست، دانشکده علوم پایه، واحد همدان، دانشگاه آزاد اسلامی، همدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سهیل</Name>
				<MidName></MidName>
				<Family>سبحان اردکانی</Family>
				<NameE>Soheil</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sobhanardakani</FamilyE>
				<Organizations>
				<Organization>دکترای تخصصی علوم محیط‌زیست، دانشیار گروه محیط‌زیست، دانشکده علوم پایه، واحد همدان، دانشگاه آزاد اسلامی، همدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهرداد</Name>
				<MidName></MidName>
				<Family>چراغی</Family>
				<NameE>Mehrdad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Cheraghi</FamilyE>
				<Organizations>
				<Organization>دکترای تخصصی علوم محیط‌زیست، دانشیار گروه محیط‌زیست، دانشکده علوم پایه، واحد همدان، دانشگاه آزاد اسلامی، همدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بهاره</Name>
				<MidName></MidName>
				<Family>لرستانی</Family>
				<NameE>Bahareh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Lorestani</FamilyE>
				<Organizations>
				<Organization>دکترای تخصصی علوم محیط‌زیست، دانشیار گروه محیط‌زیست، دانشکده علوم پایه، واحد همدان، دانشگاه آزاد اسلامی، همدان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>هاجر</Name>
				<MidName></MidName>
				<Family>مریخ پور</Family>
				<NameE>Hajar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Merrikhpour</FamilyE>
				<Organizations>
				<Organization>دکترای تخصصی علوم خاک، استادیار گروه کشاورزی، دانشگاه سیدجمال الدین اسدآبادی، اسدآباد، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Amaranthus caudatus</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Tagetes patula</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Cadmium</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Environmental remediation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Chelating agents</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تاج‌خروس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گل جعفری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کادمیوم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اصلاح محیط‌زیست</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عوامل کلات‌کننده</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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[Investigation of physiological response and phytoremediation ability of Echinacea purpurea in cadmium contaminated soil]. Iran J Hortic Sci Technol 2018; 19(2): 127-42 (In Persian).##25. Sinhal VK, Srivastava A, Singh VP. EDTA and citric acid mediated phytoextraction of Zn, Cu, Pb and Cd through marigold (Tagetes erecta). J Environ Biol 2010; 31(3): 255-59.##26. Liu JN, Zhou QX, Wang S, et al. Cadmium tolerance and accumulation of Althaea rosea Cav. and its potential as a hyperaccumulator under chemical enhancement. Environ Monit Assess 2009; 149: 419-27.##27. Towolawi AT, Arowolo TA, Bada BS, et al. Phytoextraction assessment of green Amaranth (Amaranthus viridis Linn.) Grown on soil amended with sewage sludge. Ife J Sci 2017; 19(1): 133-40.##28. United States Department of Agriculture (USDA). Field Book for Describing and Sampling Soils, version 3.0. National soil survey center, Natural Resources Conservation Service, 2012, 300 p.##29. Carter MR, Gregorich EG. Soil sampling and methods of analysis, (2nd ed), CRC Press Boca Raton; 2008: FL, 1204p.##30. Ebrahimi M. Effect of EDTA treatment method on leaching of Pb and Cr by Phragmites australis (Cav.) Trin. Ex Steudel (common reed). Caspian J Env Sci 2015a; 13(2):153-66.##31. Sobhanardakani S, Heydari A, Khorasani NA, et al. Preparation of new biofungicides using antagonistic bacteria and mineral compounds for controlling cotton seedling damping-off disease. J Plant Prot Res 2009; 49(1): 49-55.##32. Bardiya Bhurat K, Sharma S, Mishra Y, et al. Tagetes erecta (marigold), a phytoremediant for Niand Pb contaminated area: a hydroponic analysis and factors involved. Rendiconti Lincei 2017; 28(4): 673-78.##33. Liu JN, Zhou QX, Sun T, et al. Identification and chemical enhancement of two ornamental plants for phytoremediation. Bull Environ Contam Toxicol 2008; 80: 260-65.##34. Bareen F, Rafiq Kh, Shafiq M, et al. Uptake and leaching of Cu, Cd, and Cr after EDTA application in sand columns using Sorghum and Pearl Millet. Pol J Environ Stud 2019; 28(4): 2065-77.##35. Sobhanardakani S, Jamshidi K. Assessment of metals (Co, Ni and Zn) content in the sediments of Mighan Wetland using geo-accumulation index. Iran J Toxicol 2015; 9(30): 1386-90.##36. Davodpour R, Sobhanardakani S, Cheraghi M, et al. Honeybees (Apis mellifera L.) as a potential bioindicator for detection of toxic and essential elements in the environment (Case study: Markazi Province, Iran). Arch Environ Contam Toxicol 2019; 77(3): 344-58.##37. Di Bonito M, Breward N, Crout NMJ, et al. Overview of selected soil pore water extraction methods for the determination of potentially toxic elements in contaminated soils: Operational and technical aspects. Environ Geochem 2008; 213-49.##38. Hosseini NS, Sobhanardakani S, Cheraghi M, et al. Heavy metal concentrations in roadside plants (Achillea wilhelmsii and Cardaria draba) and soils along some highways in Hamedan, west of Iran. Environ Sci Pollut Res 2020; 27(12): 13301-14.##39. 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]. Iran J Health Environ 2019; 12(1): 87-100 (In Persian).##40. Almaroai YA, Usman ARA, Ahmad M, et al. Effect of synthetic chelators and low-molecular-weight, organic acids on chromium, copper and arsenic uptake and translocation in Maize (Zea mays L.). Soil Sci 2012; 177:655-63.##41. Ebrahimi M. Effect of EDTA and DTPA on phytoremediation of Pb-Zn contaminated soils by Eucalyptus camaldulensis Dehnh and effect on treatment time. Desert 2015b; 19(1): 65-73.##42. Ouhadi VR, Yong RN, Bayesteh H, et al. Influence of potential determining ions on the microstructural performance and contaminant adsorption of a homoionic illitic clay. Water Air Soil Pollut 2007; 181: 77-93.##43. Zhang, X, Yang H, Cui Z. Evaluation and analysis of soil migration and distribution characteristics of heavy metals in iron tailings. J Clean Prod 2018; 172: 475-80.##44. Rungruang N, Babel S. Cadmium removal potential from contaminated soil by Tagetes erecta L. and Panicum maximum: influence of soil pH. Soil Sediment Contam 2016; 25:133-50.##45. Goodarzi AR, Mirmomen M. [The effect of time and pore fluid characteristics on electrokinetic performance in removing heavy metals from soil]. Modares Civil Eng J 2016; 8(3): 229-41 (In Persian).##46. Neugschwandtner RW, Tlustos P, Komarek M, et al. Chemically enhanced phytoextraction of risk elements from a contaminated agricultural soil using Zea mays and Triticum aestivum: performance and metalmobilization over a three year period. Int J Phytoremediat 2012; 14(8): 754-71.##47. Chitraprabha K, Sathyavathi S. Phytoextraction of chromium from electroplating effluent by Tagetes erecta (L.). Sustain Environ Res 2018; 28: 128-34.##48. Kaur C, Selvakumar G, Ganeshamurthy AN. Organic Acids in the Rhizosphere: Their Role in Phosphate Dissolution. Springer, 2016; pp 165-77.##49. Barrow NJ, Debnath A, Sen A. Mechanisms by which citric acid increases phosphate availability. Plant Soil 2017; 423(1-2): 1-12.##50. Kaur R, Yadav P, Sharma A, et al. Castasterone and citric acid treatment restores photosynthetic attributes in Brassica juncea L. under Cd(II) toxicity. Ecotoxicol Environ Safe 2017; 145: 466-75.##51. Khan AR, Ullah I, Waqas M, et al. Host plant growth promotion and cadmium detoxification in Solanum nigrum, mediated by endophytic fungi. Ecotoxicol Environ Safe 2017; (136): 180-88.##52. Mendoza-Hernandez JC, Perea-Velez YS, Arriola-Morales J, et al. Assessing the effects of heavy metals in ACC deaminase and IAA production on plant growth-promoting bacteria. Microbiol Res 2016; 188-189: 53-61.##53. Liu YT, Chen ZS, Hong CY. Cadmium- Induced physiological response and antioxidant enzyme changes in novel cadmium accumulator Tagetes patula. J Hazard Mater 2011; 189: 724-31.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی وضعیت مدیریت پسماندهای بیمارستانی در ایران:
مطالعه موردی شهر کرمانشاه در سالهای 95-1394</TitleF>
		<TitleE>Investigation of the Hospital Waste Management in Iran: a Case Study of the Kermanshah Province During 2015-16 Years</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: مدیریت پسماندهای بیمارستانی توجهات زیادی را جلب کرده زیرا مدیریت نامناسب و ناکافی آن سبب خطراتی برای سلامتی انسان و همچنین محیط زیست می شود. در این راستا هدف از این مطالعه بررسی مدیریت پسماند&#8204;های بیمارستانی شهر کرمانشاه بر اساس چک لیست بهداشت محیط بیمارستانی وزارت بهداشت درمان و آموزش پزشکی می باشد. 
روش کار: این مطالعه (کمی- کیفی) در دو بازه زمانی در دو سال متوالی از طریق تکمیل چک لیست معتبر مدیریت پسماند وزارت بهداشت، درمان و آموزش پزشکی که شامل تمامی مراحل مدیریت پسماندهای بیمارستانی است انجام شد. میزان پسماند تولیدی هر بیمارستان هم هفته&#173;ای یکبار در فصل پاییز در بازه مطالعه اندازه گیری شد. 
یافته&#8204;ها: نتایج این مطالعه نشان داد که میانگین کل درصد مطلوبیت مدیریت پسماند با استاندارد&#8204;های بهداشتی در بیمارستان&#8204;های کرمانشاه در سال&#8204;های 1394 و 1395 به ترتیب 5/15 &#177; 38/70 و 8/14 &#177; 3/74 بود. میانگین مطلوبیت مدیریت پسماند در بیمارستان&#8204;های دولتی، نظامی، خصوصی و تأمین اجتماعی در دو سال مورد مطالعه به ترتیب از 61 به 14/65 درصد، 75 به 79 درصد، 87 به 90 درصد و 5/84 به 86 درصد ارتقاء یافته است. میانگین کل پسماند تولیدی روزانه به ازای هر تخت، 06/4 کیلوگرم به &#8204;دست آمد، به طوری&#173; که برای بیمارستان&#8204;های دولتی، نظامی، تأمین اجتماعی و خصوصی به ترتیب 69/4، 26/3، 7/2 و 62/1 کیلوگرم در روز به ازای تخت فعال بود. نتایج نشان داد که بین مقدار تولید پسماند بیمارستانی و تعداد تخت&#173;های فعال رابطه معنی&#8204;داری (95% دامنه اطمینان) وجود دارد. 
نتیجه&#8204;گیری: از نتایج حاصل از این مطالعه، امتیاز مدیریت پسماند بیمارستان&#173;های کرمانشاه در حدود متوسط ارزیابی می شود. بنابراین نیاز به تلاش، نظارت و کنترل بیشتری برای رسیدن به وضعیت مطلوب مدیریت پسماند بیمارستانی&#160; می&#173;باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Background &#38; objectives: The management of healthcare wastes is receiving greater attention because of the risks to both human health and the environment caused by inadequate waste management practices. In that context, the objective of this study was to investigate the hospital solid waste management in Kermanshah city, Kermanshah province, Iran based on Ministry of Health and Medical Education checklist which is related to environmental health of hospitals.
Methods: This study (qualitative-quantitative) was performed in two interval time in two consecutive years through a valid checklist of waste management process of Iranian Ministry of Health which include all steps of medical waste management. The quantity of hospital waste produced was measured during one week in autumn session during study interval.&#160;
Results: The results of this study showed that the total averages of desirability in waste management compared to health standards in Kermanshah city hospitals were 70.38 &#177; 15.5 and 74.3 &#177; 14.8 in 2015 and 2016, respectively. The average desirability of waste management in governmental, military, private and social hospitals improved from 61 to 65.14, 75 to 79, 87 to 90 and 84.5 to 86%, respectively in two years of study interval. The average (weighted mean) of total hospital wastes generation rate (in Kermanshah city) was 4.06 kg/bed-day and for governmental, military, private and social hospitals were 4.69, 3.26, 2.7 and 1.62 kg/bed-day, respectively. The results indicated that there was a significant correlation (p &#60; 0.05) between hospital active bed and medical wastes production.
Conclusion: From the results of this study, the score of waste management practices in Kermanshah hospitals are evaluated as moderate. Therefore, more efforts, monitoring and control should be implied to achieve the desired state of hospital waste management</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>443</FPAGE>
			<TPAGE>454</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/52020/05/62019/10/12
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/7/20
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/162020/08/152020/06/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/3/12
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>شهلا</Name>
				<MidName></MidName>
				<Family>رخشان</Family>
				<NameE>Shahla</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rakhshan</FamilyE>
				<Organizations>
				<Organization>دانش آموخته کارشناسی ارشد مهندسی بهداشت محیط، مرکز تحقیقات عوامل محیطی موثر بر سلامت، دانشگاه علوم پزشکی کرمانشاه، کرمانشاه، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نساء</Name>
				<MidName></MidName>
				<Family>فرمانی</Family>
				<NameE>Nesa</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Farmani</FamilyE>
				<Organizations>
				<Organization>کمیته تحقیقات دانشجویی، دانشجوی کارشناسی مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی کرمانشاه، کرمانشاه، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>انور</Name>
				<MidName></MidName>
				<Family>اسدی</Family>
				<NameE>Anvar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Asadi</FamilyE>
				<Organizations>
				<Organization>استادیار گروه مهندسی بهداشت محیط، مرکز تحقیقات عوامل محیطی موثر بر سلامت، پژوهشکده سلامت، دانشگاه علوم پزشکی کرمانشاه، کرمانشاه، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Hospital waste</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Waste management</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Medical waste</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Generation rate</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Kermanshah</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Iran</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>مدیریت پسماند</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زباله‌های پزشکی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نرخ تولید</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کرمانشاه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ایران</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Ferreira V, Teixeira MR. Healthcare waste management practices and risk perceptions: Findings from hospitals in the Algarve region, Portugal. Waste Manage. 2010;30(12):2657-63.##2. Birpınar ME, Bilgili MS, Erdoğan T. Medical waste management in Turkey: A case study of Istanbul. Waste Manage. 2009;29(1):445-8.##3. Tchobanoglous G, Hilary T, Samuel V. Integrated solid waste managementengineering principles and management issues. McGraw-Hill Companies,Incorporated. 1993.##4. Michael L, Phillip B, Jeffrey E. Hazardous waste management. Waveland Pr Inc; Reissue edition. 2010.##5. Sawalem M, Selic E, Herbell JD. Hospital waste management in Libya: A case study. Waste Manage (Oxford) 2009;29(4):1370-5.##6. Verma LK, Mani S, Sinha N, Rana S. Biomedical waste management in nursing homes and smaller hospitals in Delhi. Waste Manage.2008;28(12):2723-34.##7. Abd El-Salam MM. Hospital waste management in El-Beheira Governorate, Egypt. J Environ Manage 2010;91(3):618-29.##8. Bazrafshan E, Kord Mostafapoor F. Survey of medical waste characterization and management in Iran: a case study of Sistan and Baluchestan Province. Waste Manag. Res. 2011;29(4):442-50.##9. WHO. Management of solid health-care waste at primary health-care centres: A decision-making guide. ##10. Prüss-Üstün A, Giroult E, Rushbrook P, Organization WH. Safe management of wastes from health-care activities. World Health Organization. 1999. ##11. Marinković N, Vitale K, Holcer NJ, et al. Management of hazardous medical waste in Croatia. Waste Manage. 2008;28(6):1049-56.##12. Al-Khatib IA, Al-Qaroot YS, Ali-Shtayeh MS. Management of healthcare waste in circumstances of limited resources: a case study in the hospitals of Nablus city, Palestine. Waste Manag Res 2009;27(4):305-12.##13. Dehghani M, Azam K, Changani F, Fard ED. Assessment of medical waste management in educational hospitals of Tehran university medical sciences. Iran. J. Environ. Health. Sci. Eng. 2008;5(2):131-6.##14. Nourmoradi H, Haghighat Ga, Doustei M, et al. Investigation of the environmental health status of hospitals of Medical University of Ilam in 2016. Journal of Jiroft University of Medical Sciences 2018;5(1):274-85.  [in Persian[##15. Salimi M, Arab M, Akbari F, et al. A survey on the status of environmental health management in Qom province hospitals. Journal of School of Public Health and Institute of Public Health Research 2007;5(3):59-66.  [in Persian[##16. Mehdipour Rabori M, Khalooei A, Nakhaei Amroudi N, Nourmoradi H. Compliance with Environmental Health Standards in Educational Hospitals of Kerman University of Medical Sciences in 2009. Journal of Health 2014;5(2):159-69.  [in Persian[##17. Tudor T, Noonan C, Jenkin L. Healthcare waste management: a case study from the National Health Service in Cornwall, United Kingdom. Waste Manage. (Oxford) 2005;25(6):606-15##18. Jonidi Jafari A, Golbaz S, Sajjadi H. The study of environmental hygiene indexes status in Karaj :Hospitals:2011. Hospital (Rio J) 2013;11(4):9-18. [in Persian[##19. Diaz LF, Eggerth LL, Enkhtsetseg S, Savage GM. Characteristics of healthcare wastes. Waste Manage. (Oxford) 2008;28(7):1219-26.##20. Farzadkia M, Akbari H, Gholami H, Darabi A. Management of Hospital Waste: A Case Study in Tehran, Iran. Health Scope 2018;7(2):e61412.##21. Qdais HA, Rabi A, Abdulla F. Characteristics of the medical waste generated at the Jordanian hospitals. Clean Technol Environ Policy 2007;9(2):147-52.##22. Taghipour H, Mosaferi M. Characterization of medical waste from hospitals in Tabriz, Iran. Sci Total Environ 2009;407(5):1527-35.##23. Askarian M, Vakili M, Kabir G. Results of a hospital waste survey in private hospitals in Fars province, Iran. Waste Manage. (Oxford) 2004;24(4):347-52.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مدل‌سازی و بهینه‌سازی فرایند انعقاد-لخته‌سازی شیرابه لندفیل 
با استفاده از روش سطح پاسخ</TitleF>
		<TitleE>Modelling and Optimization of Coagulation–Flocculation Process of Landfill Leachate by Response Surface Methodology</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: امروزه با توجه به روش&#173;های متداول لندفیل کردن، دغدغه&#173;های محیط&#173;زیستی شیرابه&#173;های تولیدی به یک مشکل جهانی تبدیل شده است. فرایند فیزیکی-شیمیایی یک راه&#8204;&#173;حل بالقوه و مقرون به&#8204;&#173;صرفه برای تصفیه شیرابه لندفیل به&#173;&#173;شمار می&#8204;رود. به&#173;دلیل وقت&#173;گیر بودن آزمایشات جارتست برای دستیابی به غلظت مناسب مواد منعقدکننده، هدف این پژوهش، بررسی تصفیه&#8204;پذیری شیرابه لندفیل زباله مشهد با استفاده از روش سطح پاسخ به&#173;عنوان جایگزین روش&#173;های معمولی در فرایند انعقاد-لخته&#173;سازی بوده است. 
مواد و روش&#173;ها: آزمایشات در جارتست 6 خانه با حجم موثر mL 500 انجام شد. توانایی کلرید آهن 6 آبه در پاسخ به چهار پارامتر COD، TSS، کدورت و قلیائیت مورد بررسی قرار گرفت. برای ارزیابی مدل و بهینه&#173;سازی غلظت منعقدکننده و pH با توجه به بالاترین راندمان حذف، طرح مرکب مرکزی و روش سطح پاسخ استفاده شد. آنالیزهای فیزیکی و شیمیایی بر مبنای روش&#8204;های استاندارد آب و فاضلاب آمریکا انجام گردید.
یافته&#173;ها: نتایج نشان داد که برای سه پاسخ (COD، TSS و قلیائیت) مدل درجه دوم و کدورت نیز مدل درجه دوم کاهش یافته تحت شرایط بهینه برای غلظت g/L 23/10 در pH 85/8 حاصل شده است. آزمایشات تطبیق تحت شرایط بهینه منجر به حذف COD، TSS، کدورت و قلیائیت به ترتیب برابر 79/66%، 61/88%، 53/97% و 89/67% شد. بررسی&#173;های آماری (جدول ANOVA، مقادیر R2 و P-value) نشان داد که مدل&#173;ها برای ارائه داده&#173;های تجربی مناسب و در تمامی مدل&#173;ها، مقدار R2 بیشتر از 99/0 بود. مقادیر P-value نیز نشان داد که اثرات درجه دوم و درجه دوم کاهش یافته در غلظت کلرید آهن و pH انعقاد معنی&#173;دار بوده است. همسویی و تطابق نتایج تجربی نیز نزدیک به پیش&#173;بینی حاصل از مدل&#173;ها بود.
نتیجه&#173;گیری: با توجه به نتایج حاصل از این پژوهش با روش سطح پاسخ، از فرآیند انعقاد-لخته&#173;سازی می&#173;توان به&#173;عنوان فرایندی موثر برای حذف ترکیبات بازدارنده شیرابه به کار گرفت.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>&#160;
Background and Objective: Nowadays, due to the conventional methods of landfilling, the environmental concerns about generated leachate are becoming a global problem. Physical-chemical process is considered a potential and cost-effective solution for the treatment of municipal landfill leachate. Since jar-test are time-consuming experiments for obtaining the appropriate concentration of coagulants, the aim of this research was the treatment of landfill leachate using response surface methodology as a substitute for conventional methods in coagulation&#8211;flocculation process.
Materials and Methods: Experiments were performed in a six-cell jar-test with effective volume of 500 mL. The ability of Ferric chloride hexahydrate to response to four parameters including COD, TSS, alkalinity and turbidity was investigated. To evaluate the model and optimization of coagulant concentration and pH, central composite design and response surface methodology were used due to the highest removal efficiency. Physical and chemical analyses were performed based on standard methods for the examination of water and wastewater.
Results: The results showed that the quadratic model was achived for the three responses (COD, TSS and alkalinity) and the Reduced Quadratic model was obtained for Turbidity under the optimum conditions for the concentration of 10.23g/L at pH 8.85. Verification experiments, under optimum conditions in removal of COD, TSS, turbidity and alkalinity resulted 66.79%, 88.61%, 97.53% and 67.89%, respectively. Statistical studies (ANOVA table, the amounts of R2 and P-value) showed that the models were suitable for providing experimental data and in all models, the R2 value was greater than 0.99. P-value values also showed that the effects of quadratic model and reduced quadratic model were significant in ferric choloride dosage and coagulation pH. These experimental results were consistent with those predicted by the model. 
Conclusion: According to the obtained results by response surface methodology, coagulation&#8211;flocculation process can be used as the effective process to remove leachate inhibitors.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>455</FPAGE>
			<TPAGE>476</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/52020/05/62019/10/122020/02/7
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/11/18
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/162020/08/152020/06/12020/06/24
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/4/4
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>خجسته‌پور</Family>
				<NameE>Mehdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Khojastehpour</FamilyE>
				<Organizations>
				<Organization>استاد، گروه مهندسی بیوسیستم، دانشکده کشاورزی، دانشگاه فردوسی، مشهد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سعید</Name>
				<MidName></MidName>
				<Family>قنبری آزاد پاشاکی</Family>
				<NameE>Saeed</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghanbari Azad Pashaki</FamilyE>
				<Organizations>
				<Organization>دانشجوی دکتری تخصصی گروه مهندسی بیوسیستم، دانشکده کشاورزی، دانشگاه فردوسی مشهد، مشهد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمدعلی</Name>
				<MidName></MidName>
				<Family>ابراهیمی نیک</Family>
				<NameE>Mohammadali</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ebrahimi-nik</FamilyE>
				<Organizations>
				<Organization>استادیار، گروه مهندسی ‌بیوسیستم، دانشکده کشاورزی، دانشگاه فردوسی مشهد، مشهد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>عباس</Name>
				<MidName></MidName>
				<Family>روحانی</Family>
				<NameE>Abbas</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rohani</FamilyE>
				<Organizations>
				<Organization>دانشیار، گروه مهندسی ‌بیوسیستم، دانشکده کشاورزی، دانشگاه فردوسی مشهد، مشهد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>: Leachate treatment</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ferric chloride</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Response surface methodology</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Coagulation–flocculation.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تصفیه شیرابه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کلرید آهن</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>روش سطح پاسخ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>انعقاد-لخته‌سازی</KeyText>
			</KEYWORD>
		</KEYWORDS>

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	</ARTICLE>


	<ARTICLE> 
		<TitleF>تثبیت مخمر ساکارومایسس سرویزیه بر روی بستر آلژینات 
به منظور حذف ایبوپروفن از محلول های آبی</TitleF>
		<TitleE>Immobilization of Saccharomyces Cerevisiae on Alginate Substrate to Biodegradation of Ibuprofen from Aqueous Solutions</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و هدف: ایبوپروفن یکی از پرمصرف ترین داروهای ضد التهابی غیر استروئیدی است که از طریق کارخانجات سازنده و دفع پساب بیمارستانی و حتی فاضلاب خانگی به منابع آبی وارد می&#173;شود. هدف از این مطالعه، حذف ایبوپروفن در فرآیند تجزیه زیستی به وسیله مخمر ساکارومیسس سرویزیه تثبیت شده بر روی بستر آلژینات از محلول&#8204;های آبی می باشد. 
مواد و روش ها: این پژوهش، یک مطالعه تجربی- آزمایشگاهی می باشد. در این مطالعه تاثیر پارامترهای غلظت مخمر (g/100ml) 3/0- 1/0، غلظت اولیه ایبوپروفن (mg/l) 350-50، زمان تماس 30-1 ساعت&#160; و pH اولیه محلول &#160;(4-7) بر فرآیند تجزیه زیستی ایبوپروفن با مخمرساکارومایسس تثبیت شده بر روی بستر آلژینات مورد بررسی قرار گرفت آزمایشها با استفاده از روش سطح پاسخ&#160; در نرم افزار Design Expert 7 با استفاده از روش Behnken Box- طراحی و بهینه &#173;سازی گردید. 
یافته ها: یافته&#173;های این مطالعه نشان داد حداکثر حذف ایبوپروفن توسط مخمر تثبیت شده بر روی آلژینات 5 /93 درصد در 5/5pH= &#160;، غلظت مخمر g/100ml)) 2/0، زمان 30 ساعت و غلظت اولیه mg/L 50&#160; ایبوپروفن است. 
نتیجه گیری: برمبنای نتایج این مطالعه می توان بیان نمود که مخمر ساکارومایسس سرویزیه تثبت شده توانایی تجزیه بیولوژیکی ایبوپروفن را با کمترین هزینه و راندمان بالا دارا است و می&#173;توان از این روش مقرون به صرفه جهت تصفیه فاضلاب&#173;های دارویی استفاده نمود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>&#160;
Background: Ibuprofen is one of the most widely used non-steroidal anti-inflammatory drugs that enter the water resources through manufacturing plants and disposal of hospital effluents and even domestic wastewater. The aim of this study was to removal of ibuprofen using biodegradation process by Saccharomyces Cerevisiae yeast fixed on alginate substrate from aqueous solutions.
Method: This research was an experimental-laboratory study. The effect of parameters including yeast concentration (0.1-0.3 g/100ml), Initial concentration of ibuprofen (50-350 mg/l), contact time (1-30 hours),&#160; initial pH (4-7) on the biodegradation of ibuprofen with stabilized yeast on alginate substrate was investigated. Experiments were designed and optimized using response surface methodology in Design Expert 7 software.
Results: The findings of this study showed that the maximum removal of ibuprofen by fixed yeast on alginate at pH = 5.5, yeast concentration 0.2 (g /100ml), time 30 hours, and initial concentration of ibuprofen=50 mg/L was 93.5%.
Conclusion: Based on the results of this study, it can be concluded that the fixed Saccharomyces cerevisiae is capable to biodegradation of ibuprofen at low cost and high efficiency and this cost-effective method can be used for the treatment of pharmaceutical wastewater.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>477</FPAGE>
			<TPAGE>494</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/52020/05/62019/10/122020/02/72020/02/1
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/11/12
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/162020/08/152020/06/12020/06/242020/08/16
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/5/26
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>کبری</Name>
				<MidName></MidName>
				<Family>طهماسبی</Family>
				<NameE>Kobra</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Tahmasebi</FamilyE>
				<Organizations>
				<Organization>دانشجوی کارشناسی ارشد مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>روشنک</Name>
				<MidName></MidName>
				<Family>رضایی کلانتری</Family>
				<NameE>Roshanak</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rezaei Kalantary</FamilyE>
				<Organizations>
				<Organization>۲ گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی ایران، تهران، ایران ۳ مرکز تحقیقات تکنولوژی بهداشت محیط، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>اسرافیلی</Family>
				<NameE>Ali</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Esrafili</FamilyE>
				<Organizations>
				<Organization>۲ گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی ایران، تهران، ایران ۳ مرکز تحقیقات تکنولوژی بهداشت محیط، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سجاد</Name>
				<MidName></MidName>
				<Family>مظلومی</Family>
				<NameE>Sajad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mazloomi</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی ایلام، ایلام، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Alginate</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Aqueous solutions</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Biodegradation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ibuprofen</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Yeast Saccharomyces cerevisiae</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ایبوپروفن</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تجزیه بیولوژیکی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مخمر ساکارومایسس سرویزیه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آلژینات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>محلول‌های آبی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Kaur A, Umar A, Kansal SK. Heterogeneous photocatalytic studies of analgesic and non-steroidal anti-inflammatory drugs. APPL CATAL A-GEN 2016;510: 134-55.##2.	NARVAEZ V JF, JIMENEZ C C. Pharmaceutical products in the environment: sources, effects and risks. Vitae 2012;19(1): 93-108.##3.	Mestre A, Pires J, Nogueira J, Carvalho A. Activated carbons for the adsorption of ibuprofen. Carbon 2007;45(10): 1979-88.##4.	Heckmann L-H, Callaghan A, Hooper HL, et al. Chronic toxicity of ibuprofen to Daphnia magna: effects on life history traits and population dynamics. J Toxicol Lett 2007;172(3): 137-45.##5.	Subramanya NT. Biodegradation of bisphenol a and ibuprofen by ammonia oxidizing bacteria: Texas A&#38;M University; 2007.##6.	Boynton CS, Dick CF, Mayor GH. NSAIDs: an overview. J. Clin. Pharmacol. 1988;28(6): 512-17.##7.	Renner R. Drug mixtures prove harmful. ACS Publications; 2002.##8.	Xia D, Lo IM. Synthesis of magnetically separable Bi2O4/Fe3O4 hybrid nanocomposites with enhanced photocatalytic removal of ibuprofen under visible light irradiation. J Water Res 2016;100: 393-404.##9.	Ferreira AM, Coutinho JA, Fernandes AM, Freire MG. Complete removal of textile dyes from aqueous media using ionic-liquid-based aqueous two-phase systems. Sep.J Purif. Technol. 2014;128: 58-66.##10.	Mittal H, Maity A, Ray SS. Synthesis of co-polymer-grafted gum karaya and silica hybrid organic–inorganic hydrogel nanocomposite for the highly effective removal of methylene blue. Chem Eng J 2015;279: 166-79.##11.	RAHAEI S, Razavi S, EMAM JZ. The ability of Saccharomyces cerevisiae strain in aflatoxin reduction in pistachio nuts.  2010.##12.	YARKE SN, Ghaemi N, Nouhi A. Optimizing conditions of lead removal by saccharomyces cerevisiae in laboratory condition.  2011.##13.	Teixeira MC, Duque P, Sá-Correia I. Environmental genomics: mechanistic insights into toxicity of and resistance to the herbicide 2, 4-D. Trends Biotechnol. 2007;25(8): 363-70.##14.	Yang S, Hai FI, Nghiem LD, et al. Removal of bisphenol A and diclofenac by a novel fungal membrane bioreactor operated under non-sterile conditions. Int. Biodeterior. Biodegradation 2013;85: 483-90.##15.	Naghdi M, Taheran M, Brar SK, et al. Removal of pharmaceutical compounds in water and wastewater using fungal oxidoreductase enzymes. Environ Pollut 2018;234: 190-213.##16.	Erşan M. Removal of tetracycline using new biocomposites from aqueous solutions. Desalination Water Treat. 2016;57(21): 9982-92.##17.	Chang E-E, Wan J-C, Kim H, et al. Adsorption of selected pharmaceutical compounds onto activated carbon in dilute aqueous solutions exemplified by acetaminophen, diclofenac, and sulfamethoxazole. Sci. World J. 2015;2015.##18.	Hattrem MN, Dille MJ, Seternes T, et al. The relative bioavailability of ibuprofen after administration with a novel soft chewable drug formulation. CLIN PHARM DRUG DEV 2018;7(2): 168-76.##19.	Xing Z, Zhang Q, Shi X, Lin Y. Saccharomyces cerevisiae immobilized in alginate for continuous fermentation. J Clean Energy Technol 2016;4.##20.	Inal M, Yiğitoğlu M. Production of bioethanol by immobilized Saccharomyces cerevisiae onto modified sodium alginate gel. J CHEM TECHNOL BIOT. 2011;86(12): 1548-54.##21.	Denney R, Vogel AI, Mendham J. Vogel's textbook of quantitative chemical analysis/revised by J Mendham...[et al.]. Harlow, Essex, England: Longman Scientific &#38; Technical; New York: Prentice Hall; 2000.##22.	Behnamfard A, Salarirad MM. Equilibrium and kinetic studies on free cyanide adsorption from aqueous solution by activated carbon. J. Hazard. Mater. 2009;170(1): 127-33.##23.	Saratale R, Saratale G, Chang J-S, Govindwar SP. Decolorization and biodegradation of textile dye Navy blue HER by Trichosporon beigelii NCIM-3326. J Hazard Mater 2009;166(2-3): 1421-28.##24.	Kalme S, Parshetti G, Jadhav S, Govindwar SP. Biodegradation of benzidine based dye Direct Blue-6 by Pseudomonas desmolyticum NCIM 2112. Bioresour Technol 2007;98(7): 1405-10.##25.	Amirnia S, Ray MB, Margaritis A. Heavy metals removal from aqueous solutions using Saccharomyces cerevisiae in a novel continuous bioreactor–biosorption system. Chem. Eng. Trans. 2015;264: 863-72.##26.	Sadeghi A, Dolatabadi M, Asadzadeh S, JAMALI BF. Ability of the yeast saccharomyces cerevisiae for biological removal of ciprofloxacin antibiotic in aqueous solution.  2015.##27.	Nguyen ML, Juang R-S. Modification of crosslinked chitosan beads with histidine and Saccharomyces cerevisiae for enhanced Ni (II) biosorption. J TAIWAN INST CHEM E 2015;56: 96-102.##28.	Sadeghi A, Dehghan A, Asadzadeh S, Dolatabadi M. Removal of nitrate from aqueous solutions using Saccharomyces cerevisiae biosorbent: adsorption isotherms and kinetics. J North Khorasan Univ Med Sci 2014;6(2): 441-49.##29.	Nourmoradi H, Moghadam KF, Jafari A, Kamarehie B. Removal of acetaminophen and ibuprofen from aqueous solutions by activated carbon derived from Quercus Brantii (Oak) acorn as a low-cost biosorbent. J. Environ. Chem. Eng. 2018;6(6): 6807-15.##30.	Plakas KV, Karabelas AJ. Removal of pesticides from water by NF and RO membranes—A review. Desalination 2012;287: 255-65.##31.	Sadeghi A, Bazardehi MAK, Raffe S, Zarif B. Biotransformation of carmoisine and reactive black 5 dyes using saccharomyces cerevisiae. Health 2014;6(10): 859.##32.	Narendranath NV, Power R. Relationship between pH and medium dissolved solids in terms of growth and metabolism of Lactobacilli and Saccharomyces cerevisiae during ethanol production. Appl. Environ. Microbiol. 2005;71(5): 2239-43.##33.	Samarghandi M, Asgari G, Shokoohi R, et al. Efficiency of Saccharomyces Cerevisiae in Ceftriaxone Removal from Aquatic Environments: Kinetic, Isotherm of Absorption and Thermodynamics Study. J Health 2019;10(3): 270-86.##34.	Mahmoud M. Decolorization of certain reactive dye from aqueous solution using Baker’s yeast (Saccharomyces cerevisiae) strain. HBRC J 2014.##35.	Afshar P, Motamedzadegan A, Ahmady M, et al. Review on aflatoxins biodegradation strategies based on fungi. Clinical Excellence 2017;7(1): 36-48.36.##36.	Oliveira CAF, Bovo F, Corassin CH, et al. Recent trends in microbiological decontamination of aflatoxins in foodstuffs. Aflatoxins-recent advances and future prospects 2013.##37.	Vatandoostarani S, Lotfabad TB, Heidarinasab A, Yaghmaei S. Degradation of azo dye methyl red by Saccharomyces cerevisiae ATCC 9763. Int Biodeterior Biodegrad 2017;125: 62-72.##38.	Jadhav J, Parshetti G, Kalme S, Govindwar SP. Decolourization of azo dye methyl red by Saccharomyces cerevisiae MTCC 463. Chemosphere 2007;68(2): 394-400.##39.	Çabuk A, Ilhan S, Filik C, ÇALIŞKAN F. Pb^{2+} Biosorption by Pretreated Fungal Biomass. TURK J BIOL 2005;29(1): 23-28.##40.	Ehrampoush MH, Sadeghi A, Ghaneian MT, Bonyadi Z. Optimization of diazinon biodegradation from aqueous solutions by Saccharomyces cerevisiae using response surface methodology. AMB Express 2017;7(1): 68.##41.	Collado N, Buttiglieri G, Ferrando-Climent L, et al. Removal of ibuprofen and its transformation products: experimental and simulation studies. Sci Total Environ 2012;433: 296-301.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی کارایی نانوکامپوزیت مگنتیت/ بیوسیلیکا / آلژینات سدیم (MBSA) در حذف فلز جیوه از محیط‌های آبی: مطالعات سینتیک، ایزوترم و ترمودینامیک</TitleF>
		<TitleE>An Investigation on the Efficiency of Magnetite/Biosilicate/Sodium Alginate (MBSA) for the 
Removal of Hg(II) from Aquatic Environments: 
Kinetics, Isotherms and Thermodynamic Studies</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>زمینه و اهداف: یکی از مهم&#8204;ترین مشکلاتی که جهان امروز با آن مواجه شده است، مشکلات زیست محیطی آلودگی توسط فلزات سنگین می&#8204;باشد. جیوه به&#8204;عنوان یکی از فلزات سمی، به دلیل پایداری و انباشت زیستی آن در زنجیره غذایی و همچنین اثرات نامطلوب بهداشتی مانند نارسایی کلیه و آسیب دستگاه گوارش توجه زیادی را به خود جلب کرده است. هدف از این تحقیق حذف جیوه از محیطهای آبی &#160;با نانوکامپوزیت مگنتیت/ بیوسیلیکا / آلژینات سدیم می&#8204;باشد.
مواد و روش&#8204;ها: در مطالعه حاضر نانوکامپوزیت مگنتیت/ بیوسیلیکا / آلژینات سدیم به روش هم رسوبی سنتز گردید و سپس ساختار و مورفولوژی آن با استفاده از آنالیز&#8204;هایSEM ، XRD &#160;و VSM بررسی شد. پارامترهای جذبی نظیر pH، زمان تماس، مقدار جاذب، دما و غلظت اولیه یون جیوه مورد بررسی قرار گرفت.
یافته&#8204;ها: pH برابر با 5، میزان جاذب 0/2 گرم در لیتر در زمان تماس 80 دقیقه و دمای 45 درجه سلسیوس به عنوان شرایط بهینه به دست آمد، با افزایش غلظت جیوه راندمان حذف کاهش می&#8204;یابد. بررسی جذب جیوه توسط جاذب&#8204; سنتز شده از ایزوترم لانگمویر (9998/0= R2) و سینتیک شبه درجه 2 (9997/0= R2)پیروی می&#8204;کند. مطالعه ترمودینامک نیز بیانگر انجام یک واکنش گرماگیر و خود بخودی می&#8204;باشد.
نتیجه&#8204;گیری: در مجموع می&#8204;توان اذعان داشت جاذب سنتز شده به دلیل راندمان مناسب در حذف جیوه و جداسازی آسان و سریع به وسیله آهنربا، می&#8204;تواند به عنوان جاذبی کار آمد در حذف جیوه از محیط آبی باشد.
&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Backgrounds and objectives: Today &#39;s World is faced with the environmental problems associated with heavy metal contamination as one of the main issues of concern. Mercury, known as one of the most toxic heavy metals, has gained a lot of attention due to its sustainability and bioaccumulation in the food chain as well as having detrimental health problems such as kidney failure and gastrointestinal damages. This study is centered on the removal of Hg (II) ions from aqueous solutions using a magnetite/biosilica/sodium alginate nanocomposite as an efficient adsorbent.
Materials and methods: Within this study, the magnetite/biosilica/sodium alginate nanocomposite was successfully synthesized via a co-precipitation method. The structure and morphology of the prepared adsorbent were confirmed by SEM, XRD and VSM analyses. The parameters affecting the adsorption process such as pH, contact time, adsorbent amount, temperature and initial concentration of Hg (II) ions were all evaluated.
Findings: The optimum conditions obtained were as follows: pH 5, adsorbent dosage 0.2 g/L, contact time 80 min, temperature 45 &#176;C. The results revealed that the removal efficiency dropped by increasing Hg(II) concentration. The adsorption of Hg (II) obeyed the Langmuir isotherm (R2 0.9998) and pseudo-second kinetic model (R2 0.9997). Additionally, the thermodynamic studies demonstrated that the adsorption process is of endothermic and spontaneous nature.
Conclusions: All in all, the synthesized adsorbent was applied for the removal of Hg (II) ions from the aquatic environment. Ease of separation from the aqueous solution due to its magnetic properties as well as high level of Hg (II) recovery are amongst the unique feature of the adsorbent.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>495</FPAGE>
			<TPAGE>509</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2019/10/22020/08/252020/05/52020/05/62019/10/122020/02/72020/02/12019/11/10
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/8/19
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/06/72020/08/232020/08/162020/08/152020/06/12020/06/242020/08/162020/03/3
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1398/12/13
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مهناز</Name>
				<MidName></MidName>
				<Family>قنبریان</Family>
				<NameE>Mahnaz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghambarian</FamilyE>
				<Organizations>
				<Organization>۱ استادیار گروه پژوهشی صنایع شیمیایی، پژوهشکده توسعه صنایع شیمیایی جهاد دانشگاهی، البرز، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مجتبی</Name>
				<MidName></MidName>
				<Family>یگانه بادی</Family>
				<NameE>Mojtaba</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Yegane Badi</FamilyE>
				<Organizations>
				<Organization>۲ دانشجوی دکترای مهندسی بهداشت محیط، دانشکده بهداشت محیط، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>اسرافیلی</Family>
				<NameE>Ali</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Esrafili</FamilyE>
				<Organizations>
				<Organization>دانشیار گروه مهندسی بهداشت محیط، دانشکده بهداشت، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>بهبهانی</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Behbahani</FamilyE>
				<Organizations>
				<Organization>۴ استادیار، دانشکده مهندسی شیمی، دانشگاه صنعتی شهدای هویزه، دشت آزادگان، سوسنگرد،ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>حسینی</Family>
				<NameE>Mahdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hoseini</FamilyE>
				<Organizations>
				<Organization>دانشجوی دکترای مهندسی بهداشت محیط، دانشکده بهداشت محیط، دانشگاه علوم پزشکی ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>حمیدرضا</Name>
				<MidName></MidName>
				<Family>صبحی</Family>
				<NameE>Hamid Reza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sobhi</FamilyE>
				<Organizations>
				<Organization>۵ استادیار، گروه شیمی، دانشگاه پیام نور، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Adsorption</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>MBSA nanoparticle</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Mercury</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Isotherms</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Kinetics</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Thermodynamics</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جذب سطحی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نانوذره MBSA</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جیوه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ایزوترم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سینتیک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ترمودینامیک</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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Application of Amino and Thiolated Multi-walled Carbon Nanotubes for Removal of Mercury from Aqueous Solutions. Modares Civil Eng J 2015;15(4): 97-104.##49. Hosseini M, Esrafili A, Gholami M. New magnetic/Biosilica/Sodium Alginate Composites for removal of Pb (II) ions from aqueous solutions: kinetic and isotherm studies. J Adv in Environ Health Res 2018;6(3): 160-72.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

</ARTICLES>

</JOURNAL>
</XML>
