<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1403</YEAR>
<VOL>13</VOL>
<NO>2</NO>
<MOSALSAL>48</MOSALSAL>
<PAGE_NO>92</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>بررسی همبستگی بین آلودگی میکروپلاستیک و عناصر با پتانسیل سمیت در ماهی سفید دریای خزر (Rutilus kutum)</TitleF>
		<TitleE>Investigation of the Correlation between Microplastic Pollution and Potentially Toxic Elements in Caspian White Fish (Rutilus kutum)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>این پژوهش با هدف بررسی همبستگی آماری بین آلودگی میکروپلاستیک و عناصر با پتانسیل سمیت در جمعیت ماهی سفید (Rutilus kutum) در سه ایستگاه نمونه &#8204;برداری (کیاشهر، انزلی و آستارا) واقع در سواحل جنوب غربی &#160;دریای خزر انجام شد. نتایج حاصل از بررسی ۶۰ نمونه ماهی نشان داد که تمامی نمونه &#8204;ها آلوده به میکروپلاستیک بودند. بیشترین میانگین فراوانی میکروپلاستیک، &#160;35/50&#160;&#177; 53/75&#160; &#160;(قطعه به ازای هر ماهی) در ایستگاه انزلی مشاهده شد. نتایج تحلیل غلظت عناصر نشان داد که آهن با میانگین&#160;&#160;&#181;g/kg 5945/33&#160;&#177; 23111  در ایستگاه انزلی، بیشترین غلظت را داشت. در ایستگاه کیاشهر، همبستگی منفی معنی &#8204;داری بین فراوانی میکروپلاستیک &#8204;ها و عناصر کادمیوم و نیکل مشاهده شد.&#160;(rs&#62;-0/4،p&#60;0/05) در ایستگاه آستارا، همبستگی مثبت معنی &#8204;داری بین فراوانی میکروپلاستیک &#8204;ها و غلظت آرسنیک و نیکل&#160;(rs&#62;0/4،p&#60;0/05)مشاهده گردید. براساس مقایسه غلظت عناصر با استانداردهای FAO/WHO، تنها غلظت آرسنیک در ماهی&#8204; های ایستگاه &#8204;های مختلف، بالاتر از حد مجاز بود. این یافته ها نشان دهنده تعاملات پیچیده بین آلودگی میکروپلاستیک و غلظت عناصر در ماهی سفید دریای خزر است که نیازمند تحقیقات بیشتر برای ارزیابی تاثیرات زیست &#8204;محیطی و سلامت اکوسیستم دریای خزر است.

&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Abstract
This research was conducted to investigate the statistical correlation between microplastic contamination and potentially toxic elements in Kutum populations (Rutilus kutum) at three sampling stations: Kiashar, Anzali and Astara, located along the Southwestern coast of the Caspian Sea. The results from analysis of 60 fish samples indicated that all samples were contaminated with microplastics. The highest mean abundance of microplastic, 53.75&#177;35.50 (particles per fish), was observed at Anzali sampling station. The results of the elemental concentration analysis showed that Iron had the highest concentration, with a mean value of &#160;23111 &#177; 5945.33 &#160;&#181;g/kg at Anzali station. At Kiashar station, a significant negative correlation was observed between the abundance of microplastics and the concentrations of Cadmium and Nickel (rs˃-0.4, p˂0.05). At Astara station, a significant positive correlation was found between the abundance of microplastics and the concentrations of Arsenic and Nickel (rs˃0.4, p˂0.05). According to the comparison of elemental concentrations with FAO/WHO standards, only the concentration of Arsenic in fish from various stations exceeded the permissible limit. These findings indicate the complex interactions between microplastic contamination and elemental concentrations in Kutum (R. kutum) from the Caspian Sea, necessitating further research to evaluate the environmental impacts and the health of the Caspian Sea ecosystem.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>19</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/09/5
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/6/15
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/15
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/9/25
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فرشته</Name>
				<MidName></MidName>
				<Family>حاجی آقایی قاضی محله</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Haji Aghaei Ghaazi Mahalleh</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشکده منابع طبیعی، دانشگاه گیلان، صومعه سرا، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>fereshte.hj22@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جاوید</Name>
				<MidName></MidName>
				<Family>ایمانپور نمین</Family>
				<NameE>J.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Imanpour Namin</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشکده منابع طبیعی ، دانشگاه گیلان، صومعه سرا، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>javidiman@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Statistical correlation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Iron</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>Arsenic</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Nickel.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>همبستگی آماری</KeyText>
			</KEYWORD>

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

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

			<KEYWORD>
				<KeyText>آرسنیک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نیکل</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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Xuan, C., J. Wang, Y. Xie, Y. Ma, J. Zhang, H. Wei, A. Ibrahim and E. Abdou, 2022. Physiological response and oxidative stress of grass carp (Ctenopharyngodon idellus) under single and combined toxicity of polystyrene microplastics and cadmium. Ecotoxicology and Environmental Safety 245: 114080.##83.	Yaghobzadeh, Y., M. Hossein-Nezhad, G. Asadi- Shiran and M. Pourali. 2014. An investigation of lead concentration in Rutilus frisii kutum form Caspian Sea; case study of Bandar Anzali and Roodsar, Iran. Journal of Mazandaran University of Medical Sciences 23: 102-108. (In Persian).##84.	Yang, D., H. Shi, L. Li, J. Li, K. Jabeen and P. Kolandhasamy. 2015. Microplastic pollution in table salts from China. Environmental Science &#38; Technology 49: 13622–13627.##85.	Yazdani Foshtomi, M., S. Oryan, M. Taheri, K. Darvish Bastami and M. A. Zahed. 2019. Composition and abundance of microplastics in surface sediments and their interaction with sedimentary heavy metals, PAHs and TPH (Total Petroleum Hydrocarbons). Marine Pollution Bulletin 149: 110655.##86.	Zakeri, M., A. Najia, A. Akbarzadeh and A. Uddin. 2020. Microplastic ingestion in important commercial fish in the southern Caspian Sea. Marine Pollution Bulletin 160: 111598.##87.	Zhao, J., W. Ran, J. Teng, Y. Liu, H. Liu, X. Yin, R. Cao and Q. Wang. 2018. Microplastic pollution in sediments from the Bohai Sea and the yellow sea, China. Science of the Total Environment 640-641: 637-645.##88.	Zhou, Y., X. Liu and J. Wang. 2020. Ecotoxicological effects of microplastics and cadmium on the earthworm Eisenia foetida. Journal of Hazardous Materials 392: 122273.##89.	Zou, J., X. Liu, D. Zhang and X. Yuan. 2020. Adsorption of three bivalent metals by four chemical distinct microplastics. Chemosphere 248: 126064.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی وضعیت ذخایر و شاخص‌های نقاط مرجع شیلاتی ماهی کپور معمولی (Cyprinus carpio Linnaeus, 1758) در دریاچه پشت سد ارس استان آذربایجان غربی</TitleF>
		<TitleE>Stock Status and Fisheries Reference Points for Common Carp (Cyprinus carpio) in the Aras Dam Reservoir, the West Azerbaijan Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>چکیده
دریاچه پشت سد ارس بزرگ&#8204;ترین منبع آبی شمال غرب کشور به لحاظ بهره&#8204;برداری از انواع آبزیان می&#8204;باشد، اما اطلاعات مربوط به وضعیت ذخایر آبزیان آن بسیار محدود می&#8204;باشد. هدف از این مطالعه، تعیین وضعیت ذخایر ماهی کپور معمولی(Cyprinus carpio) در دریاچه پشت سد ارس با استفاده از جدیدترین نسخه مدل صید-حداکثر محصول پایدار (++CMSY) &#160;بود. برای این منظور، با استفاده از داده&#8204;های صید سال&#8204;های 1392 الی 1401 و بکارگیری مدل++ CMSY، سقف برداشت و میزان ذخیره جمعیت گونه کپور معمولی در دریاچه سد ارس تخمین زده شد. نتایج بیانگر وضعیت نامناسب این گونه در دریاچه پشت سد ارس &#160;و بالا بودن فشار صید بر ذخایر آن است. بررسی رابطه طول و وزن کپور معمولی بیانگر الگوی رشد همگون بود. بطورکلی، تداوم این روند و عدم تعدیل بهره&#8204;برداری چه بصورت مجاز و چه غیرمجاز از ذخایر گونه، منجر به کاهش و نهایتاً تخلیه ذخیره خواهد شد. این مطالعه، لزوم مدیریت صید و صیادی به ویژه صید غیرمجاز، توجه به سقف برداشت سالانه مجاز، بکارگیری سیاست&#8204;های مدیریتی، برنامه بازسازی ذخایر و حفاظت از مناطق نوزادگاهی گونه کپور معمولی دریاچه پشت سد ارس را به مدیران اجرایی استان توصیه می&#8204;کند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Abstract
Aras Dam reservoir is the largest water source in the northwest of Iran in terms of exploitation of various aquatic species, but the information of its aquatic stocks is very limited. The purpose of this study was to determine the stock &#160;status of common carp (Cyprinus carpio) in the Aras Dam reservoir using the latest version of catch-maximum sustainable yield (CMSY++) model. For this purpose, by using the CMSY++ model and the catch data from October 2013 to March 2022, and harvest limit and stock level of the common carp in the Aras Dam reservoir were estimated. The results indicate the poor condition of this species and the high fishing pressure on its stock. The length-weight relationship showed that growth pattern in common carp was homogeneous. In &#160;general, the continuation of this trend and the failure to adjust the exploitation of this species stock, either legally or &#160;illegally, will lead to the reduction and depletion of its stock.. This study, recommends to the decision makers for appropriate mangement of fishing especially illegal fishing, to pay attention to the allowed annual harvest limits, apply management policies and protection of &#160;the nursery grounds of common carp in the Aras Dam reservoir.


&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>21</FPAGE>
			<TPAGE>34</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/09/52024/11/23
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/9/3
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/152024/12/21
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/10/1
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>حقی وایقان</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Haghi Vayghan</FamilyE>
				<Organizations>
				<Organization>گروه اکولوژی و مدیریت ذخایر آبزیان، پژوهشکده آرتمیا و آبزی پروری، دانشگاه ارومیه، ارومیه، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>a.haghi@urmia.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهرناز</Name>
				<MidName></MidName>
				<Family>قنبرزاده</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghanbarzadeh</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی منابع طبیعی و محیط زیست، دانشکده کشاورزی، دانشگاه شیراز، شیراز، فارس، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mehrna.ghanbarzadeh@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Stock management</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>CMSY++</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Aras Dam reservoir</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Common Carp</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Length-weight relationship.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدیریت ذخایر</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدل CMSY++</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>دریاچه پشت سد ارس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کپور معمولی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رابطه طول و وزن</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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The worldwide crisis in fisheries: economic models and human behavior. Cambridge University Press.##7-	Cone, R. S. 1989. The need to reconsider the use of condition indices in fishery science. Transactions of the American Fisheries Society 118(5), 510-514.##8-	Doyen, L., C. Béné, M. Bertignac, F. Blanchard, A. A. Cissé, C. Dichmont, S. Gourguet, O. Guyader, P. Y. Hardy and S. Jennings. 2017. Ecoviability for ecosystem‐based fisheries management. Fish and Fisheries 18(6), 1056-1072.##9-	FAO. 2020. World fisheries and aquaculture. Food and Agriculture Organization. 1-244.##10-	FAO. 2024. The state of world fisheries and aquaculture 2024 blue transformation in action. The United Nations.##11-	Fazli, H., A. A. Janbaz and K. Khedmati. 2020a. Risk of stock extinction in two species of kilkas (Clupeonella engrauliformis and C. grimmi) from the Caspian Sea. Iranian Journal of Ichthyology 7(1): 92-100.##12-	Fazli, H., M. Tavakoli, M. R. Khoshghalb, M. Moghim and T. Valinasab. 2020b. Population dynamics and the risk of stock extinction of Persian sturgeon (Borodin) in the Caspian Sea. Fisheries &#38; Aquatic Life 28(2), 62-72.##13-	Fazli, H., F. Kaymaram, G. R. Daryanabard, S. A. Hoseini, G. A. Bandani, M. Larijani and M. Yahyaei. 2023. Population biology and stock status of common carp (Cyprinus carpio Linnaeus, 1758) in the Caspian Sea. Regional Studies in Marine Science 68, 103272.##14-	Foley, M. M., B. S. Halpern, F. Micheli, M. H. Armsby, M. R. Caldwell, C. M. Crain, E. Prahler, N. Rohr, D. Sivas, M. W. Beck, M. H. Carr, L. B. Crowder, J. Emmett Duffy, S. D. Hacker, K. L. McLeod, S. R. Palumbi, C. H. Peterson, H. M. Regan, M. H. Ruckelshaus, P. A. Sandifer and R. S. Steneck. 2010. Guiding ecological principles for marine spatial planning. Marine Policy 34(5): 955-966.##15-	Fritsch, S., F. Guenther and M. F. Guenther. 2019. Package ‘neuralnet’. Training of Neural Networks 2: 30-38.##16-	Froese, R. 2006. Cube law, condition factor and weight–length relationships: history, meta‐analysis and recommendations. Journal of Applied Ichthyology 22(4): 241-253.##17-	Froese, R., N. Demirel, G. Coro, K. M. Kleisner and H. Winker. 2017. Estimating fisheries reference points from catch and resilience. Fish and Fisheries 18(3): 506-526.##18-	Froese, R., A. C. Tsikliras and K. I. Stergiou. 2011. Editorial note on weight–length relations of fishes. Acta Ichthyologica et Piscatoria 41(4): 261-263.##19-	Froese, R., H. Winker, G. Coro, M. L. Palomares, A. C. Tsikliras, D. Dimarchopoulou, K. Touloumis, N. Demirel, G. Vianna and G. Scarcella. 2023.  New developments in the analysis of catch time series as the basis for fish stock assessments: The CMSY++ method. Acta Ichthyologica et Piscatoria 53: 173-189.##20-	Haghi Vayghan, A., and N. Agh. 2022. Stock assessment of Aras Crayfish (Astacus leptodactylus Eschscholtz, 1823) for sustainable fishing management. Journal of Fisheries 75(4): 507-520. (In Persian)##21-	Haghi Vayghan, A., R. Ghorbani, Y. Peighambari, M. A. Lee, D. M. Kaplan and B. A. Block. 2018. Association between Skipjack (Katsuwonus pelamis) distribution caught by Iranian purse seiners and environmental variables in the Indian Ocean. Journal of Applied Ichthyological Research 6(1): 1-20. (In Persian)##22-	Haghi Vayghan, A., R. Ghorbani, S. Y. Peyghambari, M. A. Lee, D. M. Kaplan and B. A. Block. 2017. Relationship between yellowfin tuna (Thunnus albacares) distribution caught by Iranian purse seiners and environmental variables in the Indian Ocean. Iranian Scientific Fisheries Journal 26(1): 67-82. (In Persian)##23-	Haghi Vayghan, A., R. Zarkami, R. Sadeghi and H. Fazli. 2016. Modeling habitat preferences of Caspian kutum, Rutilus frisii kutum (Kamensky, 1901) (Actinopterygii, Cypriniformes) in the Caspian Sea. Hydrobiologia 766(1): 103-119.##24-	Hill, S. L., J. Hinke, S. Bertrand, L. Fritz, R. W. Furness, J. N. Ianelli, M. Murphy, R. Oliveros‐Ramos, L. Pichegru and R. Sharp. 2020. Reference points for predators will progress ecosystem‐based management of fisheries. Fish and Fisheries 21 (2): 368-378.##25-	Hossain, M.Y., S. Sayed, M. Mosaddequr Rahman, M. Ali, M. Hossen, A. Elgorban, Z. Ahmed and J. Ohtomi. 2015. Length‐weight relationships of nine fish species from the Tetulia River, southern Bangladesh. Journal of Applied Ichthyology 31(5): 967-969. (In Persian)##26-	Ji, Y., Q. Liu, B. Liao, Q. Zhang and Y. N. Han. 2019. Estimating biological reference points for Largehead hairtail (Trichiurus lepturus) fishery in the Yellow Sea and Bohai Sea. Acta Oceanologica Sinica 38(10): 20-26.##27-	Kimura, D. K., and J. V. Tagart. 1982. Stock reduction analysis, another solution to the catch equations. Canadian Journal of Fisheries and Aquatic Sciences 39(11): 1467-1472.##28-	Martell, S., and R. Froese. 2013. A simple method for estimating MSY from catch and resilience. Fish and Fisheries 14(4): 504-514.##29-	Mateus, L. D. F., and G. Estupiñán. 2002. Fish stock assessment of piraputanga Brycon microlepis in the Cuiabá River basin, Pantanal of Mato Grosso, Brazil. Brazilian Journal of Biology 62: 165-170.##30-	Mohebbi, F. 2021. Aras River and Dam Reservoir Pollutions: human activities or climate change. Ecology and Water Resources 5(1): 60-66.##31-	Moutopoulos, D., and K. Stergiou. 2002. Length–weight and length–length relationships of fish species from the Aegean Sea (Greece). Journal of Applied Ichthyology 18(3): 200-203.##32-	Nikolsky, G. 1976. The interrelation between variability of characters, effectiveness of energy utilization, and karyotype structure in fishes. Evolution 30(1):180-185.##33-	Ojelade, O. C., I. T. Omoniyi, W. O. Abdul, F. I. Adeosun, A. A. Idowu and I. Abdulraheem. 2019. Reproductive Biology, Trophodynamics and Stock Structure of Ribbonfish (Trichiurus lepturus Linnaeus, 1758) in Tropical Marine Waters of the Bight of Benin. 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A study of the dynamics of the fishery for yellowfin tuna in the eastern tropical Pacific Ocean. Inter-American Tropical Tuna Commission Bulletin 2: 243-285.##40-	Schnute, J. T., and L. J. Richards. 2002. Surplus production models PP. 104-126. In: Handbook of Fish Biology and Fisheries. Blackwell Publishing, Malden, MA, USA.##41-	Schweder, T., and N. L. Hjort. 1996. Bayesian synthesis or likelihood synthesis-what does borel's paradox say? Preprint series. Statistical Research Report 1-14.##42-	Verhulst, P. F. 1838. Notice sur la loi que la population suit dans son accroissement. Correspondence Mathematique et Physique 10: 113-129.##43-	Walters, C. J., S. J. Martell and J. Korman. 2006. A stochastic approach to stock reduction analysis. Canadian Journal of Fisheries and Aquatic Sciences 63(1): 212-223.##44-	Winker, H., F. Carvalho and M. Kapur. 2018. JABBA: just another Bayesian biomass assessment. Fisheries Research 204: 275-288.##45-	Yelghi, S., Z. Mazaheri Kohanestani and S. G. Mokarami. 2014. An investigation of some biological features of Cyprinus carpio (Linneaus, 1758) in Gorgan Rud estuary. Journal of Applied Ichthyological Research 1(4): 81-94. (In Persian)##46-	Zhang, K., J. Zhang, Y. Xu, M. Sun, Z. Chen and M. Yuan. 2018. Application of a catch-based method for stock assessment of three important fisheries in the East China Sea. Acta Oceanologica Sinica 37(2): 102-109.##47-	Zhou, S., A. E. Punt, A. D. M. Smith, Y. Ye, M. Haddon, C. M. Dichmont and D. C. Smith. 2017. An optimized catch-only assessment method for data poor fisheries. ICES Journal of Marine Science 75(3): 964-976.## ##</REF>
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		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>پایش وضعیت موجود بوم‌سازگان رودخانه زاینده رود با استفاده از شاخص‌های زیستی و کیفیت آب</TitleF>
		<TitleE>Monitoring Zayandehroud River Ecosystem Health using Biological and Water Quality Indices</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>چکیده
رودخانه زاینده&#8204;رود منبع حیاتی آب در مرکز ایران است. اما این رودخانه به دلیل دستکاری&#8204;های انسانی به یکی از آسیب&#8204;پذیرترین اکوسیستم&#8204;ها تبدیل شده است. در این مطالعه بخشی از رودخانه زاینده رود که دارای جریان دائمی است (سد تنظیمی تا پل کله) با هدف ارزیابی کیفیت آب و سلامت بوم سازگان رودخانه بررسی شد. از آب و درشت بی مهرگان کف&#8204;زی در 11 ایستگاه در تابستان 1401 نمونه برداری شد. سپس شاخص کیفیت منابع آب سطحی ایران (IRWQISC)، شاخص&#8204;های غنا و تنوع و شاخص&#8204;های زیستی (BMWP، ASPT) محاسبه شد. نتایج نشان می&#8204;دهد؛ شاخص IRWQISC در اکثر ایستگاه&#8204;ها وضعیت متوسط دارد و تنها در 3 ایستگاه کیفیت آب در وضعیت نسبتا خوب قرار گرفته است. در حالی که شاخص BMWP، وضعیت بد و شاخص ASPT، آلودگی شدید و متوسط، شاخص تنوع &#160;شانون وضعیت آلودگی شدید و متوسط را نشان داد. شاخص IRWQISC نتواسته است&#8204; قطع جریان آب در پایین دست سد انحرافی چم آسمان و اثرات آن بر کاهش کیفیت آب و سلامت بوم&#8204;سازگان رودخانه را به طور دقیق منعکس کند. در حالی که با کاهش شدید شاخص غنا و شاخص&#8204;های زیستی در ایستگاه پل کله، عدم تعادل بوم&#8204;سازگان رودخانه&#8204; مشخص شد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Abstract
Zayandehroud is the water source for life in Central Iran, but it has become has turned into one of the most vulnerable ecosystem due to human disturbances. In this study, water quality and ecosystem health of Zayandehroud was evaluated in a segment of the river with permanent flow, from the Zayandehrud Regulating Dam to Pol-Kalleh. Water and benthic macroinvertebrate samples were collected from 11 stations during the summer of 2022. The Iranian Water Quality Index for Surface Water (IRWQISC), along with richness and diversity indices, as well as biological indices (BMWP and ASPT), were calculated. The findings revealed that the IRWQISC index categorizes water quality as moderate in most stations, with relatively good quality observed in only three stations. In contrast, the BMWP index denoted poor conditions, the ASPT index reflected severe to moderate pollution levels, and the Shannon diversity index also indicates severe to moderate pollution. The IRWQISC index was unable to accurately capture the effects of water flow interruption downstream of the Cham-Aseman diversion dam and its impact on the deterioration of water quality and overall river ecosystem health. However, the substantial decline in the richness index and biological indices at the Pol-Kalleh station highlights a significant ecological imbalance in the river ecosystem.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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		</PAGES>

		<RECEIVE_DATE>
			2024/09/52024/11/232024/12/3
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/9/13
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/152024/12/212025/01/20
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/11/1
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فخریه</Name>
				<MidName></MidName>
				<Family>محسنی</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohseni</FamilyE>
				<Organizations>
				<Organization>محیط زیست دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>fakhri.mohseni@na.iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>نعمتی ورنوسفادرانی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Nemati Varnosfaderany</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>nemati@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علیرضا</Name>
				<MidName></MidName>
				<Family>سفیانیان</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Soffianian</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سیما</Name>
				<MidName></MidName>
				<Family>فاخران</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Fakheran</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email></Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Monitoring</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Benthic Macroinvertebrates</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Biological Index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Water Quality</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ecosystem Health.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پایش زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>درشت بی‌مهرگان کف‌زی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کیفیت آب</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سلامت بوم‌سازگان.</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Aghajanloo, K., E. Hajizadeh and S. Ariaeezadeh. 2022. Evaluation of Karun river water quality based on IRWQI and WAWQI indicators in Molasani and Ahvaz stations. Iranian Journal of Soil and Water Research 53(2): 367-380. (In Persian).##2.	Alivand Darani, Z., and A. Chamani. 2020. Water quality assessment of Zayandeh-rood River based on diversity and abundance of macrobenthos in 2017. Experimental Animal Biology 8(4): 97-107. (In Persian).##3.	Armitage, P. D., D .Moss, J. F. Wright and M. T. Furse. 1983. The performance of a new biological water quality score system based on macroinvertebrates over a wide range of unpolluted running-water sites. Water Research 17(3): 333-347.##4.	Aslhashemi, A., and H. Taghipour. 2010. Water quality index. The Application of Chemistry in Environment 1(4): 1-5. (In Persian).##5.	Aththanayake, A. M. N. S., N. D. L. Nikawela, B. K. A. Bellanthudawa and S. Wijetunga. 2024. Integrated assessment of Kirala Kele wetland health: Bridging the gap between water quality parameters and biotic components. Water Supply 24(3): 738-759.##6.	Brack, W., V. Dulio, M. Ågerstrand, I. Allan, R. Altenburger, M. Brinkmann, D. Bunke, R. M. Burgess, I. Cousins, B. I. Escher and F. J. Hernández. 2017. Towards the review of the european union water framework directive: recommendations for more efficient assessment and management of chemical contamination in European surface water resources. Science of the Total Environment 576: 720-737.##7.	Buck, M., N. E. A. Woodley, D. M. Borkent, T. Wood, J. R. Pape, V. Vockeroth, V.  Michelsen and S. A. Marshall. 2009. Key to Diptera families-adults. Manual of Central American Diptera 1: 95–156.##8.	Chessman, B. C. 2003. New sensitivity grades for Australian river macroinvertebrates. Marine and Freshwater Research 54: 95-103.##9.	Department of Environment. 2012. Quality index of the country's water resources and their classification.  Water and soil office. Human Environment Deputy of Environmental Protection Organization.##10.	Department of Natural Resources, Isfahan University of Technology. 2017. Environmental flow requirement of Zayandehrud River and Gavkhooni International Wetland for sustainable ecological functions. Isfahan provincial directory of environmental protection. Project No. 93/6816.##11.	Department of Natural Resources, Isfahan University of Technology. 2019. Biodiversity monitoring studies of macrobenthos and macrophytes of Gavkhooni Basin in order to be used in the comprehensive management plan of the watershed of Gavkhooni International Wetland.  Isfahan provincial directory of environmental protection. Project No. 96/6817.##12.	Ebrahimi Dastgerdi, H., E. Ebrahimi and Fakheran, S. 2017. Impacts of Zayandehroud dam on the macro-benthic invertebrate and water quality of Zayandehroud river using BMWP and ASPT biological indices. Iranian Journal of Applied Ecology 6(2): 55-67. (In Persian).##13.	Erseus, C., M. J. Wetzel and L. Gustavsson. 2008. ICZN rules—a farewell to Tubificidae (Annelida, Clitellata). Zootaxa 1744(1): 66-68.##14.	Fan, X., H. Yu, D. S. Tiando, Y. Rong, W. Luo, C. Eme, S. Ou, J. Li and Z. Liang. 2021. Impacts of human activities on ecosystem service value in arid and semi-arid ecological regions of China. International Journal of Environmental Research and Public Health 18(21): 11121.##15.	Fathi, P., E. E. Dorche, O. B. Kashkooli, J. Stribling and A. Bruder. 2022. Development of the Karun macroinvertebrate tolerance index (KMTI) for semi-arid mountainous streams in Iran. Environmental Monitoring and Assessment 194(6): 421.##16.	Fathi, P., E. E. Dorche, M. Zare Shahraki, J. Stribling, O. Beyraghdar Kashkooli, A. Esmaeili Ofogh and A. Bruder. 2022. Revised Iranian water quality index (RIWQI): a tool for the assessment and management of water quality in Iran. Environmental Monitoring and Assessment 194(7): 504.##17.	Feio, M. J., R. M. Hughes, M. Callisto, S. J. Nichols, O. N. Odume, B. R. Quintella, M. Kuemmerlen, F. C. Aguiar, S. F. Almeida, P. Alonso-EguíaLis and F. O. Arimoro. 2021. The biological assessment and rehabilitation of the world’s rivers: An overview. Water 13(3): 371.##18.	Fernández, N., A. Ramírez and F. Solano. 2004. Physico-chemical water quality indices—a comparative review. Bistua: Revista de la Facultad de Ciencias Básicas 2(1): 19–30.##19.	Gholizadeh, M., and O. Heydari. 2020. Evaluation of Gorganrood river water quality based on surface water quality indicators in the Gonbad Kavous. Iranian Journal of Health and Environment 13(1): 33–48. (In Persian).##20.	Hering, D., R. K. Johnson, S. Kramm, S. Schmutz, K. Szoszkiewicz and P. F. Verdonschot. 2006. Assessment of European streams with diatoms, macrophytes, macroinvertebrates, and fish: A comparative metric‐based analysis of organism response to stress. Freshwater Biology 51(9): 1757–1785.##21.	Kavand, H., S. Ziaee and M. Mardani Najafabadi. 2023. The impact of water conservation policies on the reallocation of agricultural water-land resources. Frontiers in Water 5: 1138869.##22.	Li, M., S. Li, H. Liu and J. Zhang. 2023. Balancing water ecosystem services: Assessing water yield and purification in Shanxi. Water 15(18): 3261.##23.	Ligon, F. K., W. E. Dietrich and W. J. Trush. 1995. Downstream ecological effects of dams. Bio Science 45(3): 183-192.##24.	Luo, Y., D. L. Ficklin, X. Liu and M. Zhang. 2013. Assessment of climate change impacts on hydrology and water quality with a watershed modeling approach. Science of the Total Environment 450: 72-82.##25.	Magallon Ortega, G., C. Escalera Gallardo, E. López-López, J. E. Sedeño-Díaz, M. Lopez Hernandez, M. Arroyo-Damián and R. Moncayo-Estrada. 2021. Water quality analysis in a subtropical river with an adapted biomonitoring working party (BMWP) index. Diversity 13(11): 606.##26.	Nasiri, M., A. Ghojoghi and H. T. Podeh. 2023. Investigation of Zayandeh River water quality based on macrobenthos as biological indicators. International Journal of Aquatic Biology 11(3) 213-221.##27.	Niknam, E., A. Chamani and M. Nourouzi. 2020. The water quality of Zayandeh-rood river with macrobenthos biodiversity indexes in fall 2017 to spring 2018. Applied Biology 32(4): 164-175. (In Persian).##28.	Nilsson, C., C. A. Reidy, M. Dynesius and C. Revenga. 2005. Fragmentation and flow regulation of the world's large river systems. Science 308(5720): 405-408.##29.	Ofogh, A. R. E., E. E. Dorche Birk and S. A Bruder. 2023. Effect of seasonal variability on the development and application of a novel Multimetric Index based on benthic macroinvertebrate communities–A case study from streams in the Karun river basin (Iran). Ecological Indicators 146:109843.##30.	Pescador, M. L., A. K. Rasmussen and S. C. Harris. 2004. Identification manual for the caddisfly (Trichoptera) larvae of Florida. Division of Water Resource Management, Florida Department of Environmental Protection.##31.	Pirali Zefrehei, A., and E. Ebrahimi. 2017. Introduction of several biological indices for the assessment of river water quality. Journal of Water and Sustainable Development 3(2): 35-42. (In Persian).##32.	Poff, N. L., and J. K. Zimmerman. 2010. Ecological responses to altered flow regimes: A literature review to inform the science and management of environmental flows. Freshwater Biology 55(1): 194-205.##33.	Rezaei, F., H. R. Safavi and A. Ahmadi. 2013. Groundwater vulnerability assessment using fuzzy logic: A case study in the Zayandehrood aquifers, Iran. Environmental Management 51: 267-277.##34.	Scholes, R. J. 2020. The future of semi-arid regions: A weak fabric unravels. Climate 8(3): 43.##35.	Shannon, C. E. 1948. A mathematical theory of communication. The Bell System Technical Journal 27(3): 379-423.##36.	Singh, N., B. K. Choudhary, S. Singh and R. Kumar. 2022. Monitoring and assessment of anthropogenic impacts on water quality by estimating the BMWP and ASPT indices for a headwater stream in Doon Valley, India. Sustainable Water Resources Management 8(4): 108.##37.	Smith, D. G. 1990. A better water quality indexing system for rivers and streams. Water Research 24(10): 1237-1244.##38.	Soltani, S., F. Mokhtari, R. Zare and S. Raeesi. 2020. Investigation of changes in water quality parameters in Zayandehrood Dam basin. Journal of Natural Environment 72(4): 445-458. (In Persian).##39.	Sutadian, A. D., N. Muttil, A. G. Yilmaz and B. J. C. Perera. 2016. Development of river water quality indices—a review. Environmental Monitoring and Assessment 188: 1-29.##40.	Utilleul, P., J. D. Stockwell, D. Frigon and P. Legendre. 2000. The Mantel test versus Pearson's correlation analysis: Assessment of the differences for biological and environmental studies. Journal of Agricultural, Biological, and Environmental Statistics 5: 131-150.##41.	Varnosfaderany, M. N., E. Ebrahimi, N. Mirghaffary and A. Soffianian. 2010. Biological assessment of the Zayandeh Rud River, Iran, using benthic macroinvertebrates. Limnologica-Ecology and Management of Inland Waters 40(3): 226-232.##42.	Varnosfaderany, M. N., N. Mirghaffary, E. Ebrahimi and A. Soffianian. 2009. Water quality assessment in an arid region using a water quality index. Water Science and Technology 60(9): 2319-2327.##43.	Wan Abdul Ghani, W. M. H., A. Abas Kutty, M. A. Mahazar, S. A. Al-Shami and S. Ab Hamid. 2018. Performance of biotic indices in comparison to chemical-based Water Quality Index (WQI) in evaluating the water quality of urban rivers. Environmental Monitoring and Assessment 190: 1-14.##44.	Zamani-Ahmadmahmoodi, R., S. Aminian, S. Bayati and A. Chamani. 2023. Evaluation of water quality changes in Zayandehroud River using IRWQISC quality index. Journal of Environmental Health Engineering 10(4): 398-411. (In Persian).## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>پایش اثرات تغییر کاربری و پوشش اراضی بر کیفیت زیستگاه‌های حوضه آبخیز هراز</TitleF>
		<TitleE>Monitoring the effects of land use and land cover changes on habitat quality in the Haraz watershed</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>کیفیت زیستگاه نوعی خدمات اکوسیستمی حمایتی است که تحت تأثیر تغییرات کاربری اراضی شکننده و آسیب پذیر می&#8204;شود. هدف این مطالعه ارزیابی کیفیت زیستگاه&#8204;های حوضه آبخیز هراز در استان مازندران بر مبنای تغییرات کاربری اراضی بود. با تهیه و آماده&#8204;سازی داده&#8204;های موردنیاز، مدل اینوست (InVEST) برای ارزیابی کیفیت زیستگاه&#8204;های منطقه مطالعاتی مدنظر قرار گرفت. تصاویر کاربری اراضی سه دوره 2000، 2010 و 2020 &#160;با استفاده از تصاویر ماهواره&#8204;های لندست 7 و 8 در محیط ادریسی سلوا آماده گردید. نتایج نشان داد که زیستگاه&#8204;های واقع در بخش مرکزی حوضه در سال&#8204;های مورد نظر دارای بالاترین کیفیت بودند در حالی که مناطق شمالی حوضه کمترین کیفیت را داشتند. میزان تغییرات کیفیت زیستگاه&#8204;ها در بازه&#8204;های زمانی 2010-2000، 2010-2020 و 2020-2000 حاکی از آن بود که نقاط داغ کیفیت زیستگاه&#8204;ها در مناطق مرکزی و نقاط سرد در بخش&#8204;های شمالی وجود دارند. از سال 2000 تا 2020 نقاط سرد کیفیت زیستگاه&#8204;ها افزایش داشته اند در حالی که نقاط داغ کاهش یافته&#8204;اند. به طور کلی از سال 2000 تا 2020 کیفیت زیستگاه&#8204;ها در 180163 هکتار از اراضی منطقه کاهشی و در 24096 هکتار افزایشی بوده است. بر این اساس، ضروری است در راستای توسعه و تبدیل کاربری&#8204;ها در منطقه مطالعاتی استراتژی&#8204;های مناسب به منظور حفظ کیفیت زیستگاه&#8204;های طبیعی آن اتخاذ شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Habitat quality is a type of supporting ecosystem service that becomes fragile and vulnerable under the influence of land use changes. The aim of this study was to assess the quality of habitats in the Haraz watershed in Mazandaran province based on land use changes. The InVEST model was used to assess the quality of habitats in the study area. Land use images of three periods 2000, 2010 and 2020 were prepared using Landsat 7 and 8 satellite images in the Idrisi Selva environment. The results showed that the habitats located in the central part of the basin had the highest quality in the years considered, while the northern areas of the basin had the lowest quality. The rate of changes in habitat quality in the time periods 2000-2010, 2010-2020 and 2000-2020 indicated that habitat quality the hotspots are in the central regions and coldspots are in the northern parts. From 2000 to 2020, the coldspots of habitat quality have increased, while the hotspots have decreased. In general, from 2000 to 2020, habitat quality has decreased in 180,163 hectares and increased in 24,096 hectares of the region. Accordingly, it is necessary to adopt appropriate strategies in order to maintain the quality of its natural habitats in the development and conversion of land uses in the study area.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>49</FPAGE>
			<TPAGE>63</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/09/52024/11/232024/12/32024/09/25
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/7/4
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/152024/12/212025/01/202025/02/5
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/11/17
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سحر</Name>
				<MidName></MidName>
				<Family>بازرگان</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>bazargan</FamilyE>
				<Organizations>
				<Organization>گروه علوم محیط زیست، دانشکده علوم، دانشگاه زنجان، زنجان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Bazargan@znu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فاطمه</Name>
				<MidName></MidName>
				<Family>رجائی</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rajaei</FamilyE>
				<Organizations>
				<Organization>گروه علوم محیط زیست، دانشکده علوم، دانشگاه زنجان، زنجان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Rajaei_Fatemeh@znu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فرهان</Name>
				<MidName></MidName>
				<Family>احمدی میرقائد</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ahmadi Mirqaed</FamilyE>
				<Organizations>
				<Organization>گروه علوم محیط زیست، دانشکده علوم دریایی و محیطی، دانشگاه مازندران، بابلسر، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>f.ahmadi.m@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مصطفی</Name>
				<MidName></MidName>
				<Family>قلی پور</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Gholipour</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی، دانشگاه علوم کشاورزی و منابع طبیعی گرگان، گرگان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mostafagholipour@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>InVEST</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Haraz watershed</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Hot spots analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ecosystem services</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Habitat quality</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اینوست</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>حوضه آبخیز هراز</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحلیل نقاط داغ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خدمات اکوسیستم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کیفیت زیستگاه ها</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1-	Ahmadi Mirghaed, F., and A. Souri. 2023. The effect of land use changes on water production in the Taraz watershed, Khuzestan province, southwest Iran. Geography and Environmental Hazards 2(2): 29-46.##2-	Ahmadi Mirghaed, F. A., and B. Souri. 2021. Relationships between habitat quality and ecological properties across Ziarat Basin in northern Iran. Environment, Development and Sustainability 1:1-16. ##3-	Aneseyee, A. B., E. Elias, T. Soromessa and G. Feyisa. 2020. Land use/land cover change effect on soil erosion and sediment delivery in the Winike watershed, Omo Gibe Basin, Ethiopia. Science of the Total Environment, 728: 138776.‌##4-	Arkhi, S. A., A. Mahmoudian and S. Emaduddin. 2021. Forecasting the risk of forest destruction using geographic information system and logistic regression model (case study: Sardasht city). Geography and Environmental Hazards 40: 92-69. (In Persian)##5-	Broquet, M. F., P. Cabral.  Joao D. 2024. Habitat quality on the edge of anthropogenic pressures: predicting the impact of land use changes in the Brazilian Upper Paraguay River Basin. Journal of Cleaner Production,142546.‌##6-	 Das, A., and T. Bas. 2020. Assessment of peri-urban wetland ecological degradation through importance-performance analysis (IPA): A study on Chatra Wetland, India Ecological Indicators 114:  106274.##7-	Eastman, J.R., Van Fossen, M.E. and Solarzano, L.A. (2005) Transition Potential Modeling for Land Cover Change. pp. 357-386. In: Maguire, D.J., Goodchild, M.F. and Batty, M. (Eds.), GIS, Spatial Analysis and Modeling, Esri Press. ##8-	 Foley, J., R. DeFries and D. Gregory. 2005. Global consequences of land use. Science 309: 570-574.##9-	Gholampour, K., J. Mahmoudi, K. Ahmadi and M Barati 2012. Study of social and economic factors influencing on rangelands degradation in Eshtehard, Karaj. Natural Ecosystemsof Iran, 3 (1): 75-84. (In Persian)##10-	Gong, J., Y. Xie, E. Cao, Q. Huang and H. Li. 2019. 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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>تحلیل تأثیر ناهمگونی سیمای سرزمین شهری بر دمای سطح زمین در شهر اصفهان</TitleF>
		<TitleE>Analyzing the Effect of Urban Landscape Heterogeneity on Land Surface Temperature in Isfahan City</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>با گسترش و رشد فراینده سطوح نفوذ ناپذیر، چالش های زیست محیطی متعددی در سطوح شهری به وجود آمده است. تغییرات الگوی دمایی محیط و ایجاد جزایر حرارتی در این مناطق یکی از مهم ترین این چالش هاست. تغییر در ساختار و الگوی کاربری اراضی به نوبه خود بر ساختار سیمای سرزمین تأثیر می گذارد. این مطالعه به بررسی تغییرات ساختار سیمای سرزمین و پهنه های حرارتی طی دوره زمانی 2022-1992 در شهر اصفهان پرداخته است. برای این منظور نقشه های پهنه بندی دمای سطح زمین تهیه و متریک های سیمای سرزمین برای تجزیه و تحلیل رابطه بین تغییر الگوهای کاربری زمین و مناطق دمای سطح زمین محاسبه شدند. نتایج این مطالعه نشان داد که در مناطق با دمای بالا (جزایر حرارتی) اراضی بایر و فاقد پوشش گیاهی غالب هستند. همچنین بررسی متریک های سیمای سرزمین نشان داد هر چه پیوستگی بین کاربری ها و ساختار سیمای سرزمین بیشتر باشد، لزوما سطح زمین دماهای پایین تری را تجربه نمی کند. عامل مهم و تعیین کننده در دما نوع کاربری موجود در منطقه است. بنابراین می توان بیان کرد که دمای سطح زمین تحت تأثیر ترکیب کاربری زمین است. با توجه به اهمیت تعدیل دما در مناطق شهری، نحوه پراکنش و توزیع فضاهای سبز بر اساس اصول سیمای سرزمین، نقش بارزی در مدیریت حرارتی شهری دارد.&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The rapid expansion of impervious surfaces in urban areas has caused significant environmental challenges, including shifts in temperature patterns and the formation of urban heat islands. Changes in land use patterns and structures profoundly influence the composition, configuration, and function of landscapes. This study analyzed changes in landscape structure and thermal zones in Isfahan city from 1992 to 2022. To achieve this, land surface temperature maps were generated, and landscape metrics were calculated to explore the relationship between land use changes and land surface temperature zones. The results revealed that bare lands with little to no vegetation dominate high-temperature zones, contributing significantly to the formation of urban heat islands. Furthermore, landscape metrics indicated that land use type significantly influences local temperature. However, the analysis of landscape metrics indicated that higher continuity between land uses and landscape structures does not necessarily result in lower temperatures. The key factor influencing temperature is the type of land use in the area. Therefore, it can be concluded that land surface temperature is influenced by combinations of land use. Given the importance of temperature adjustment in urban areas, the distribution and allocation of green spaces based on landscape principles play a critical role in urban thermal management.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>65</FPAGE>
			<TPAGE>78</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/09/52024/11/232024/12/32024/09/252024/12/16
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/9/26
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/152024/12/212025/01/202025/02/52025/02/16
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/11/28
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مهدیه</Name>
				<MidName></MidName>
				<Family>ابوالحسنی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mahdiyeh</FamilyE>
				<Organizations>
				<Organization>علوم و مهندسی محیط زیست، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>m1372.abolhasani@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>لطفی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Lotfi</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>lotfi@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Landscape metrics</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Cold islands</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Heat islands</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Land surface temperature</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>متریک های سیمای سرزمین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جزایر سرد حرارتی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جزایر گرم حرارتی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>دمای سطح زمین</KeyText>
			</KEYWORD>

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

		<REFRENCES>
			<REFRENCE>
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	</ARTICLE>


	<ARTICLE> 
		<TitleF>تاثیر قارچ مایکوریزا بر ماده مؤثره موسیلاژ و برخی تنظیم کننده های اسمزی گیاه گاوزبان (.Borago officinails L) تحت تنش آبی</TitleF>
		<TitleE>Effect of Mycorrhizal Fungi on Mucilage Active Ingredient and Osmotic Regulators of Borage (Borago officinails L.) under Water Stress</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تنش آبی یکی از مهمترین عوامل تاثیرگذار بر عملکرد گیاهان است. &#160;با توجه به تأثیر بالقوه قارچ مایکوریزا بر تعدیل اثر تنش آبی بر عملکرد &#160;گیاه گاوزبان ، آزمایشی به صورت کرت&#8204;های خرد شده در قالب طرح بلوک&#8204;های کامل تصادفی ، اجرا گردید. تنش آب به عنوان عامل اصلی در سطوح آبیاری پس از 30، 60، 90، 120 و 150 میلی&#8204;متر تبخیر آب از تشتک تبخیر کلاس A و قارچ مایکوریزا به عنوان عامل فرعی در سطوح عدم کاربرد، کاربرد گونه Glomus mosseae و کاربرد گونه G. intraradices در نظر گرفته &#8204;شد. برای موسیلاژ&#160; گل ، برهمکنش آبیاری و قارچ معنی&#173; دار بود. در سطوح آبیاری پس از 120 و 150 میلی&#173;متر تبخیر کاهش درصد موسیلاژ گل مشاهده گردید، اما کاربرد قارچ در این سطوح شرایط را تغییر داد و منجر به افزایش موسیلاژ شد. در سطوح آبیاری پس از 90، 120 و 150 میلی&#173;متر تبخیر آب از تشتک تبخیر، کاهش پرولین و قند محلول در سطوح آبیاری پس از 60، 90، 120 و 150 میلی&#173;متر تبخیر در شرایط حضور قارچ مایکوریزا نسبت به عدم کاربرد قارچ مشاهده شد. بر اساس نتایج ، تیمار آبیاری پس از 90 میلی&#173;متر تبخیر و کاربرد قارچ&#173; G. mosseae توصیه می&#173; شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Water stress is one of the most important factors affecting plant performance. Considering the potential effect of mycorrhizal fungi on modulating the effect of water stress on the performance of Borage , an experiment was conducted as split-plot in randomized complete block design. Water stress as the main factor in irrigation levels after 30, 60, 90, 120 and 150 mm water evaporation from evaporation pan class A and mycorrhiza fungi as sub-agent in levels of non-application, application of Glomus mosseae &#160;and G. intraradices species were considered. For flower mucilage, the interaction of irrigation and mycorrhizal fungus was significant, and at the irrigation level of 120 and 150 mm, water evaporation increased the water stress and caused a decrease in flower mucilage. At the irrigation levels after 90, 120 and 150 mm of water evaporation, , the reduction of proline and soluble sugar of borage was observed after 60, 90, 120 and 150 mm of water evaporation in the presence of mycorrhizal fungus compared to the absence of fungus application. Based on the results, irrigation treatment is recommended after 90 mm of water evaporation and the application of mycorrhizal fungus G. mosseae.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>79</FPAGE>
			<TPAGE>92</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/09/52024/11/232024/12/32024/09/252024/12/162024/12/1
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/9/11
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2024/12/152024/12/212025/01/202025/02/52025/02/162025/03/2
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1403/12/12
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>رحیمی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rahimi</FamilyE>
				<Organizations>
				<Organization>بخش تحقیقات جنگلها، مراتع و آبخیزداری، مرکز تحقیقات و آموزش کشاورزی و منابع طبیعی استان کهگیلویه و بویراحمد، سازمان تحقیقات، آموزش و ترویج کشاورزی، یاسوج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>rahimi.ali1362@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>شاهرخ</Name>
				<MidName></MidName>
				<Family>جهانبین</Family>
				<NameE>Sh.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jahanbin</FamilyE>
				<Organizations>
				<Organization>گروه زراعت و اصلاح نباتات دانشکده کشاورزی دانشگاه یاسوج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>jabbari@znu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>امین</Name>
				<MidName></MidName>
				<Family>صالحی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Salehi</FamilyE>
				<Organizations>
				<Organization>گروه زراعت و اصلاح نباتات دانشکده کشاورزی دانشگاه یاسوج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>aminsalehi@yu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>هوشنگ</Name>
				<MidName></MidName>
				<Family>فرجی</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Faraji</FamilyE>
				<Organizations>
				<Organization>گروه زراعت و اصلاح نباتات دانشکده کشاورزی دانشگاه یاسوج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Hooshangfarajee@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Borage</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Proline</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Water stress</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Soluble sugar</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Mycorrhiza</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Mucilage.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گاوزبان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پرولین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تنش آب</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>قند محلول</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مایکوریزا</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>موسیلاژ.</KeyText>
			</KEYWORD>
		</KEYWORDS>

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			<REFRENCE>
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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

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