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<XML>
<JOURNAL>
<YEAR>1404</YEAR>
<VOL>34</VOL>
<NO>4</NO>
<MOSALSAL>150</MOSALSAL>
<PAGE_NO>81</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ اثر تریپتوفان جیره در تراکم‌های مختلف پرورش بچه تاسماهی سیبری (Acipenser baerii) بر عملکرد رشد، بقا و برخی شاخص‌های خونی</TitleF>
		<TitleE>Effect of dietary tryptophan on growth performance, survival and hematological indices of juvenile Siberian sturgeon (Acipenser baerii) at different stocking densities</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف از این مطالعه، بررسی تاثیر سطوح مختلف تریپتوفان جیره بر عملکرد رشد و برخی از شاخص&#8204;های خونی بچه تاسماهی سیبری (Acipenser baerii) در تراکم&#8204;های مختلف پرورش بود. بدین منظور، بچه تاسماهیان سیبری با میانگین وزن 10/0&#177;24/10 گرم در دو تراکم پایین (LD؛ 3/1 کیلوگرم در مترمربع) و بالا (HD؛ 6/2 کیلوگرم در مترمربع) با جیره&#8204;های غذایی حاوی تریپتوفان با سطوح صفر (شاهد)، 2/0، 4/0 و 6/0 درصد پروتئین جیره به مدت 12 هفته غذادهی شدند. نتایج تجزیه&#8204;وتحلیل عملکرد رشد در پایان دوره آزمایش نشان داد که تریپتوفان، تراکم&#8204; و برهم&#8204;کنش آنها بر وزن نهایی، درصد افزایش وزن، نرخ رشد ویژه و میانگین رشد روزانه اثر معنی&#8204;دار داشتند (05/0p&#8804;)، به&#8204;طوری&#8204;که تریپتوفان در سطح 4/0 درصد تیمار کم&#8204;تراکم، دارای بهترین عملکرد بود. همچنین تراکم و برهم&#8204;کنش تراکم و تریپتوفان بر نرخ مصرف غذا، تاثیر معنی&#8204;دار داشتند (05/0p&#8804;)، به&#8204;طوری&#8204;که میزان آن در تریپتوفان 6/0 درصد تراکم بالا در بیشترین سطح بود. تریپتوفان بر ضریب چاقی (CF)، ضریب تبدیل غذایی (FCR) و نرخ کارآیی پروتئین (PER)، فقط در تراکم پایین، اختلاف معنی&#8204;دار نشان داد (05/0p&#8804;). بیشترین مقدار CF در تریپتوفان 2/0 درصد و بیشترین مقادیر FCR و PER در تریپتوفان 4/0 و 6/0 درصد تیمارهای کم&#8204;تراکم مشاهده شد، درحالی&#8204;که در تراکم بالا، تفاوت معنی&#8204;دار مشاهده نشد. تریپتوفان، تراکم و برهم&#8204;کنش آنها بر بازماندگی، اثر معنی&#8204;دار نداشت (05/0p&#8804;). در شاخص&#8204;های هماتولوژیک، تریپتوفان، تراکم و برهم&#8204;کنش آنها بر تعداد گلبول&#8204;های قرمز خون، اختلاف معنی&#8204;دار نشان داد (05/0P&#8804;) که در تیمار کم&#8204;تراکم با تریپتوفان 4/0 درصد، در بیشترین سطح قرار داشت. در تعداد گلبول&#8204;های سفید (WBC)، هموگلوبین (HB) و هماتوکریت (HCT)، در تیمارهای هر دو &#8204;تراکم، اختلاف معنی&#8204;دار دیده شد (05/0p&#8804;)، به&#8204;طوری&#8204;که بالاترین مقادیر WBC و HB در تریپتوفان 4/0 درصد تیمارهای هر دو &#8204;تراکم پایین و بالا دیده شد. بیشترین HCT، در تراکم پایین با تریپتوفان 4/0 درصد مشاهده شد. تریپتوفان بر HCT در HD، تاثیر معنی&#8204;دار نداشت. نتایج مطالعه حاضر نشان داد که بهترین عملکرد رشد تاسماهی سیبری در تیمارهای کم&#8204;تراکم تغذیه شده با جیره&#8206;های حاوی 4/0 درصد تریپتوفان نسبت به سایر تیمارها دیده شد، اگرچه جیره&#8204;های حاوی تریپتوفان در عملکرد رشد تیمارهای پرتراکم، اختلاف معنی&#8204;دار نداشت. استفاده از جیره&#8206;های حاوی 4/0 درصد تریپتوفان، در شاخص&#8204;های هماتولوژیک (مقادیر WBC و HB) هر دو تراکم پایین و بالا اختلاف معنی&#8204;دار داشت. بنابراین، کاربرد جیره&#8204;های حاوی تریپتوفان توانست در بهبود پرورش تاسماهی سیبری در شرایط تراکم بالا موثر باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
According to world&#39;s growing population, one of the most important problems is food security. On the other hand, aquaculture is considered one of the important industries for providing protein and food resources worldwide, which has always faced numerous challenges (Pauly and Zeller, 2017). Given the issue of food security, the primary goal of aquaculturists is to achieve higher production. However, one of the most significant problems in aquaculture is the lack of water resources (Falahatkar and Rahdari, 2017). The lack of water resources has led fish producers to use increased stocking density as a solution to improve production. The increase in density can cause stress. One of the ways to achieve much production is to improve formulated diets to enhance the growth and health of fish. Researchers have added tryptophan to the diets of cultured fish to improve growth performance because it has been shown that this amino acid can improve growth performance as a very important economic indicator (Hosseini et al., 2020; Jhon et al., 2024; Zhang et al., 2024). Therefore, the present study was conducted with the hypothesis that growth, survival, and hematological indices in high-density cultured juvenile Siberian sturgeon (Acipenser baerii) would improve with the supplementation of dietary tryptophan.
Methodology 
The study was conducted with 12,000 juvenile Siberian sturgeons with an average weight of 10.24&#177;0.10 g in 8 experimental treatments with three replicates in 24 tanks as follows: Treatments 1 and 2 (fish fed with no dietary tryptophan at densities of 1.3 (LD; low density) and 2.6 kg/m&#178; (HD; high density), respectively), Treatments 3 and 4 (fish fed with diets containing 0.2% tryptophan in the protein at densities of 1.3 and 2.6 kg/m&#178;, respectively), Treatments 5 and 6 (fish fed with diets containing 0.4% tryptophan in the protein at densities of 1.3 and 2.6 kg/m&#178;, respectively), Treatments 7 and 8 (fish fed with diets containing 0.6% tryptophan in the protein at densities of 1.3 and 2.6 kg/m&#178;, respectively). The juvenile sturgeons were fed at 3% of their body weight for 12 weeks. At the end of the rearing period, the fish were weighed and growth indices were measured. Blood samples were taken for hematological analysis. To assess the effects of stocking density and tryptophan levels on growth performance, survival, and hematological indices, a Two-way ANOVA test was used, followed by Tukey&#39;s test for comparisons at the P&#8804;0.05 significance level.
Results
The analysis of growth performance at the end of the experimental period showed that different tryptophan levels, stocking densities, and their interaction had significant effects on WG, BWI, SGR, and DGR (p&#8804;0.05). In all mentioned factors, tryptophan in LD with diets containing tryptophan showed significant differences compared to control and HD. The highest levels of these parameters were observed at 0.4% tryptophan in LD. Results showed no significant differences between treatments fed with different diets containing tryptophan in feed intake, but stocking densities and their interaction had significant effects (p&#8804;0.05). The interaction effect of different tryptophan levels and stocking densities on PER, CF, and FCR showed significant effects of different tryptophan levels and stocking densities on these growth indices, with no significant interaction effect (p&#8804;0.05). While the impact of diets containing tryptophan in LD showed significant differences, this difference was not observed in HD. The interaction effect of tryptophan and stocking density on SR was not significant, and survival rates were 100% in all treatments (p&#8804;0.05). In hematological indices, different tryptophan levels, stocking densities, and their interaction had significant effects on RBC (p&#8804;0.05), with the best performance in LD fed with 0.4% tryptophan. Tryptophan and stocking density had significant effects on WBC, HB, and HCT, with no significant interaction effects (p&#8804;0.05). WBC and HB levels in both density treatments showed significant differences, with the highest WBC in LD with 0.2% tryptophan and HD with 0.6% tryptophan. The highest HB levels were observed at 0.4% tryptophan in both densities treatments. The highest HCT levels was observed at 0.4% tryptophan in LD, while no significant differences were observed in HCT at different tryptophan levels in HD.
Discussion and conclusion
The results of this study showed the positive impact of using tryptophan on growth performance and increased production in LD. Threre was no significant effect on growth indices in HD. The negative effects of density and stress on growth performance divert the body&#39;s micronutrient reserves from their primary function, using for stress response instead of growth, leading to reduced growth (Dabrowski et al., 1996). Additionally, regarding the positive effect of 0.4% tryptophan on hematological indices in juvenile Siberian sturgeon culture, results showed that in LD, using this diet positively affected all hematological indices, promoting the health of Siberian sturgeon. In HD, although tryptophan had no significant impact on RBC and HCT, it positively affected WBC and HB, improving the health of Siberian sturgeon. It appears that improving hematological indices with diets containing tryptophan in HD increases fish tolerance to stress in HD. In general, it can be concluded that providing the necessary amount of tryptophan in the diet is essential for the growth, development and health of Siberian sturgeon at HD by improving hematological indices. Therefore, it is recommended to use 0.4% tryptophan to increase production and improve health conditions in Siberian sturgeon, especially under high density conditions. 
Conflict of interest
The corresponding author, on substitute of all authors of this article, announces that in publishing this article, publication ethics, including plagiarism, research misbehavior, data cheating, or both submission and publication, have been completely avoided, and there are no commercial benefits, and the authors have not received any payment for presenting their work. Therefore, the originality of the content of this article is declared. This work has not been previously published elsewhere and has not been submitted to another journal at the same time. Hereby, it grants permission to the publisher to publish the article and its contents, including text, tables, figures, etc.
Acknowledgments
We would like to express our gratitude to the Beluga Caviar Fish Farm, International Sturgeon Research Institute and the Faculty of Natural Resources, University of Guilan.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>17</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/02/11
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/11/23
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/08/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/5/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>معصومه</Name>
				<MidName></MidName>
				<Family>نقیبی</Family>
				<NameE>Masoumeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Naghibi</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشکده منابع طبیعی، دانشگاه گیلان، صومعه‌سرا، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>m.naghibi83@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>میرمسعود</Name>
				<MidName></MidName>
				<Family>سجادی</Family>
				<NameE>Mirmasoud</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sajjadi</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشکده منابع طبیعی، دانشگاه گیلان، صومعه‌سرا، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mmsajjadi@hotmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمود</Name>
				<MidName></MidName>
				<Family>محسنی</Family>
				<NameE>Mahmoud</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohseni</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین‌المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mahmoudmohseni73@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بهرام</Name>
				<MidName></MidName>
				<Family>فلاحتکار</Family>
				<NameE>Bahram</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Falahatkar</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشکده منابع طبیعی، دانشگاه گیلان، صومعه‌سرا، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>falahatkar@guilan.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Sturgeon</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Nutritions</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Amino acid</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Stress</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماهیان خاویاری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مواد مغذی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اسید آمینه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استرس</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Allameh, S.K. Akhoundi, A. and Mohammadi, M., 2022. Effect of stock density on growth performance of rainbow trout fingerling. Advanced Aquaculture Sciences Journal, 5: 59-65. (In Persian)##Azeredo, A. Machado, M. Martos-Sitcha, J.A. Martínez-Rodríguez, G. Moura1, J. Peres, H. Oliva-Teles, A. Afonso1, A. Mancera, J.M. and Costas, B., 2019. Dietary tryptophan induces opposite health-related responses in the Senegalese sole (Solea senegalensis) reared at low or high Stocking densities with implications in disease resistance. Frontiers in Physiology, 10: 1-15. DOI: 10.3389/fphys.2019.00508##Barros, M.M. Lim, C. and Klesius, P.H., 2002. Effect of iron supplementation to cottonseed and chronic photoperiod manipulation. Aquaculture, 252: 566-572. DOI: 10.1300/J028v10n01_07##Billard, R. and Lecointre, G., 2001. Biology and conservation of sturgeon and paddlefish. Reviews in Fish Biology and Fisheries, 10: 355-392. DOI: 10.1023/A:1012231526151 ##Biswas, P. Rawat, P. Patel, A.B. and Jena, A.K., 2018. Dietary supplementation of L-tryptophan: Effect on growth and survival of Pabda, Ompok bimaculatus (Bloch) fry. Journal of Applied Aquaculture, 31: 322-336. DOI: 10.1080/10454438.2018.1545721##Cabanillas-Gámez, M. Bardullas, U. Galaviz, M.A. Rodriguez, S. Rodriguez, V.M. and López, L.M., 2019. Tryptophan supplementation helps totoaba (Totoaba macdonaldi) juveniles to regain homeostasis in high-density culture conditions. Fish Physiology and Biochemistry, 46: 597-611. DOI: 10.1007/s10695-019-00734-2##Cabanillas-Gámez, M. López, L.M. Bardullas, U. Espinoza-Villegas, R.E. True, C.D. and Galaviz, M.A., 2022. Effect of dietary tryptophan on blood and plasma parameters of striped bass Morone saxatilis, exposed to acute stressors. Latin American Journal of Aquatic Research, 50: 529-540. DOI: 10.3856/vol50-issue4-fulltext-2929##Chen, Y. and Guillemin, G.J., 2009. Kynurenine pathway metabolites in humans: disease and healthy states. International Journal of Tryptophan Research, 2: 1-19. DOI: 10.4137/ijtr.s2097##Cheng, C.H. Guo, Z.X. Ye, C.X. and Wang, A.L., 2018. Effect of dietary astaxanthin on the growth performance, nonspecific immunity, and antioxidant capacity of pufferfish (Takifugu obscurus) under high temperature stress. Fish Physiology and Biochemistry, 44: 209-218. DOI: 10.1007/s10695-017-0425-5. Epub 2017 Sep 21##Conceicao, L.E. Aragao, C. Dias, J. Costas, B. Terova, G. Martins, C. and Tort, L., 2012. Dietary nitrogen and fish welfare. Fish Physiology and Biochemistry, 38: 119-141. DOI:10.1007/s10695-011-9592-y ##Dabrowski, K. Matusiewics, M. Matusiewics, K. Hoppe, P. and Ebeling, J., 1996. Bioavailability of vitamin C from two ascorbyl monophosphate esters in rainbow trout, Oncorhynchus mykiss (Walbaum). Aquaculture Nutrition, 2: 3-10. DOI: 10.1111/j.1365-2095.1996.tb00002.x##Diogenes, A.F. Teixeira, C. Almeida, E. Skrzynska, A. Costas, B. Oliva-Teles, A. and Peres, H., 2019. Effects of dietary tryptophan and chronic stress in gilthead seabream (Sparus aurata) juveniles fed corn distillers dried grains with solubles (DDGS) based diets. Acuaculture, 498: 396-404. DOI: 10.1016/j.aquaculture.2018.08.079##Docan, A. Cristea, V. Grecu, I. and Dediu, L., 2010. Haematological response of the European catfish, Silurus glanis reared at different densities in “flow-through” production system. Archiva Zootechnica, 13: 63-70. ##Drabkin, D.R., 1945. Crystallographic and optical properties of human hemoglobin. A proposal for the standardization of hemoglobin. American Journal of the Medical Sciences, 209: 268-270. ##Ellis, T. North, B. Scott, A.P. Bromage, N.R. and Porter, M., 2002. The relationships between stocking density and welfare in farmed rainbow trout. Journal of Fish Biology, 61: 493-531. DOI: 10.1111/j.1095-8649.2002.tb00893.x##Falahatkar, B., 2014. Aquatic nutrition and formolation. Institute of applied Scientific Education of Agricultural Ministry. 334P. (In Persian)##Falahatkar, B. Eslamloo, K. and Yokoyama, S., 2014. Suppression of stress responses in Siberian sturgeon, Acipenser baerii, juveniles by the dietary administration of bovine lactoferrin. Journal of the World Aquaculture Society, 45: 699-708. DOI: 10.1111/jwas.12153. ##Falahatkar, B. and Rahdari, A., 2017. Aquaculture in dried and semidried areas. Sarva (Agricultural and Natural Resources Education Research (TAK)) Press. 300P. (In Persian)##Falahatkar, B., 2018. Nutritional Requirements of the Siberian Sturgeon: An Updated Synthesis. Agricultural and Food Sciences, 11: 207-228. DOI:10.1007/978-3-319-61664-3_11##Fattahi, S. and Hosseini, S.A., 2013. The effect of dietary tryptophan on growth performance and carcass proximate composition of Rutilus rutilus caspicus juveniles. Journal of Animal Environment. 5: 103-109. (In Persian)##Fattahi, S. Hosseini, S.A. Sudagar, M. Mazandarani, M. and Khani, F., 2015. Growth, feeding factors and the effect of salinity stress on the survival rate on roach (Rutilus rutilus caspicus) juveniles fed with different levels of betaine and tryptophan. Fisheries Science and Technology, 4: 65-78. DOI: 20.1001.1.23225513.1394.4.2.10.0. (In Persian)##Gaylord, T.G. and Barrows, F.T., 2009. Multiple amino acid supplementations to reduce dietary protein in plant-based rainbow trout, Oncorhynchus mykiss, feeds. Aquaculture, 287: 180-184. DOI: 10.1016/j.aquaculture.2008.10.037##Geraylou, Z. Souffreau, C. Rurangwa, U. D’Hondt, S. Callewaert, L. Courtin, C.M. Delcour, J.A. Buyse, J. and Ollevier, F., 2012. Effects of arabinoxylan-oligosaccharides (AXOS) on juvenile Siberian sturgeon (Acipenser baerii) performance, immune responses and gastrointestinal microbial community. Fish and Shellfish Immunology, 33: 718-724. DOI: 10.1016/j.fsi.2012.06.010##Ghafle Marammazi, J. Yaghoubi, M. and Safari, O., 2016. Effects of using crystalline amino acids in diets of sobaity sea bream (Sparidentex hasta) on whole body proximate, amino acids composition, growth and feeding performance. Iranian Scientific Fisheries Journal, 25: 217-229. DOI: 10.22092/ISFJ.2017.110271. (In Persian) ##Gholipoor, F. Allameh, S.K. Mohammadi, M. and Nasr Esfahani, M., 2006. Effect of stocking densities on grow and Food conversion ratio of rainbow trout (Oncorhynchus mykiss). Research and Reconstruction, 7: 23-27. (In Persian)##Gonzalez-silvera, D. Herrera, M. Giraldez, I. and Esteban, M.A., 2018. Effects of the dietary tryptophan and aspartate on the immune response of Meagre (Argyrosomus regius) after stress. Fishes, 3: 1-13. DOI: 10.3390/fishes3010006##Halford, J.C. Boyland, E.J. Lawton, C.L. Blundell, J.E. and Harrold, J.A., 2011. Serotonergic anti-obesity agents: past experience and future prospects. National Library of Medicine, Drugs, 71: 2247-2255. DOI: 10.2165/11596680-000000000-00000##Harpaz, S., 2005. L-Carnitine and its attributed functions in fish culture and nutrition, A review. Aquaculture. 249: 3-21. DOI: 10.1016/j.aquaculture.2005.04.007##Hosseini, S.M., 2010. The effect of tryptophan and lysine on food intake growth, survival, and carcass proximate composition of beluga (Huso huso) juveniles. Dissertation. Gorgan University of Agricultural Sciences and Natural Resources.70P. (In Persian) ##Hosseini, S.M. Perez-Jimenez, A. Costas, B. Azeredo, R. and Gesto, M., 2019. Physiological roles of tryptophan in teleosts: current knowledge and perspectives for future studies. Reviews in Aquaculture, 11: 3-24. DOI: 10.1111/raq.12223##Hosseini, S.M. Mirghaed, A.T. Ghelichpour, M. Pagheh, E. Iri, Y. and Kor, A., 2020. Effects of dietary tryptophan supplementation and stocking density on growth performance and stress responses in rainbow trout (Oncorhynchus mykiss). Aquaculture, 519: 1-26. DOI: 10.1016/j.aquaculture.2019.734908##Hseu, J.R. Lu, F.I. Su, H.M. Wang, L.S. Tsai, C.L. and Hwang, P.P., 2003. Effect of exogenous tryptophan on cannibalism, survival and growth in juvenile grouper, (Epinephelus coioides). Aquaculture, 218: 251-263. DOI: 10.1016/S0044-8486(02)00503-3##Hung, S.S.O. Lazard, J. Mariojouls, C. and Moreau, Y., 2003. Comparison of starch utilization in fingerlings of two Asian catfishes from the Mekong River (Pangasius bocourti, Sauvage, 1880, Pangasius hypophthalmus, Sauvage, 1878). Aquaculture Nutrition, 9: 215-222. DOI: 10.1046/j.1365-2095.2003.00244.x##Jabbari, E. Akarami, R. and Chitsaz, H., 2016. Effect of betaine as a feed at tractant on growth, survival, body composition and response to environmental stress in kutum (Rutilus frisii kutum) fingerling. Iranian Scientific Fisheries Journal, 26: 83-92. DOI: 10.22092/ISFJ.2017.110332. (In Persian)##Jhon, B. Erika, A.D.C. Yuri, R. and Amauri, G., 2024. Tryptophan supplementation reduces body weight but does not reduce anxiety-like behavior in zebrafish. Discover the World's Research, 4: 1-13. DOI: 10.21203/rs.3.rs-4151627/v1##Jiang, W.D. Wen, H.L. Liu, Y. and Jiang, J., 2016. Enhanced muscle nutrient content and flesh quality, resulting from tryptophan, is associated with anti-oxidative damage referred to the Nrf2 and TOR signalling factors in young grass carp (Ctenopharyngodon idella): Avoid tryptophan deficiency or excess. Food Chemistry, 199: 210-219. DOI: 10.1016/j.foodchem.2015.12.003##Jodun, W. Millard, M. and Mohler, J., 2011. The effect of rearing density on growth, survival, and feed conversion of juvenile Atlantic sturgeon. North American Journal of Aquaculture, 64: 10-15. DOI: 10.1577/1548-8454(2002)064&#60;0010:TEORDO&#62;2.0.CO;2##Kalbassi, M.R. Abdollahzadeh, E.A. and Salari-Joo, H., 2013. A review on aquaculture development in Ecopershia. 159-178. DOI: 20.1001.1.23222700.2013.1.2.4.6##Katooky, S. Jafaryan, H.A. Gholipour, H. and Ebrahimi, P., 2023. Effects of stocking density on growth parameters and some biochemical factors of blood serum in rainbow trout larvae (Oncorhynchus mykiss Walbaum, 1792). Journal of Applied Ichthyological Research, 11: 10-17. (In Persian)##Koksal, G. Rad, F. and Kindir, M., 2000. Growth performance and feed conversion efficiency of Siberian sturgeon juveniles (Acipenser baerii) reared in concrete raceways. Turkish Journal of Veterinary and Animal Sciences, 24: 435-442. ##Lepage, O. Tottmar, and O. Winberg, S., 2002. Elevated dietary intake of L-tryptophan counteracts the stress-induced elevation of plasma cortisol in (Oncoryhnchus mykiss, Walbaum). Journal of Experimental Biology, 205: 3679-3687. DOI: 10.1242/jeb.205.23.3679##Machado, M. Azeredo, R. Domingues, A. Fernandez-Boo, S. Dias, J. Conceicao, L.E.C. and Costas, B., 2019. Dietary tryptophan deficiency and its supplementation compromises inflammatory mechanisms and disease resistance in a teleost fish. Scientific Reports, 9: 76-89. DOI: 10.1038/s41598-019-44205-3##Mohseni, M. Hamidoghli, A. and Bai, S.C., 2021. Organic and inorganic dietary zinc in beluga sturgeon (Huso huso): Effects on growth, hematology, tissue concenrtation and oxidative capacity. Aquaculture, 539, pp 672-736. DOI: 10.1016/j.aquaculture.2021.736672##Nathalie¸ L.F. and Bernard, S., 2007. Biological roles of tryptophan and its metabolism: potential implication for pig feeding. Livestock Science, 112: 23-32. DOI: 10.1016/j.livsci.2007.07.002##Nghia, V.D. Huu, L.T. An, L.T.T. and Huy, N.V., 2022. Effects of dietary tryptophan on cannibalism, survival and growth of Wallago attu (Bloch and Schneider, 1801) juveniles. Hue University Journal of Science: Natural Science, 131 67-75. DOI: 10.26459/hueunijns.v131i1D.6516##North, B.P. Turnbull, J.F. Ellis, T. Porter, M.J. Migaud, H. Bron, J. and Bromage, N.R., 2006. The impact of stocking density on the welfare rainbow trout (Oncorhynchus mykiss). Aquaculture, 255: 466-479. DOI: 10.1016/j.aquaculture.2006.01.004##Papoutsoglou, S.E. Karakatsouli, N. and Chiras, G., 2005. Dietary L-tryptophan and tank colour effects on growth performance of rainbow trout (Oncorhynchus mykiss) juveniles reared in a recirculating water system. Aquacultural Engineering, 32: 277-284. DOI: 10.1016/j.aquaeng.2004.04.004##Pastuszewska, B. Tomaszewka, D.Z. Buraczewska, L. Swiech, E. and Taciak, M., 2007. Effect of supplementating pig diet with tryptophan and acidifier on protein digestion and deposition¸ and on brain serotonin concentration in young pig. Animal Feed Science and Technology, 132: 49-65. DOI: 10.1016/j.anifeedsci.2006.02.006##Pauly, D. and Zeller, D., 2017. Comments on FAOs state of world fisheries and aquaculture. Marine Policy, 77: 176-181. DOI: 10.1016/j.marpol.2017.01.006##Peters, J.C., 1991. Tryptophan nutrition and metabolism: an overview. Advances in Experimental Medicine and Biology, 249: 345-358. DOI: 10.1007/978-1-4684-5952-4_32##Rafatnezhad, S. Falahatkar, B. and Tolouei Gliani, M.H., 2008. Effects of stocking density on haematological parameters, growth and fin erosion of great sturgeon (Huso huso) juveniles. Aquaculture Research, 39: 1506-1513. DOI: 10.1111/j.1365-2109.2008.02020.x##Rafatnezhad, S. and Falahatkar, B., 2011. Evaluation of stocking density on water quality parameters in rearing of beluga (Huso huso). Iranian Scientific Fisheries Journal, 20: 165-170. DOI: 10.22.92/ISFJ.2017.109985 (In Persian)##Ramsay, J.M. Feist, G.W. Varga, Z.M. Westerfield, M. Kent, M.L. and Schreck, C.B., 2006. Whole-body cortisol is an indicator of crowding stress in adult zebrafish, Danio rerio. Aquaculture, 258: 565-574. DOI: 10.1016/j.aquaculture.2006.04.020. ##Řehulka, J., 2000. Influence of astaxanthin on growth rate condition, and some blood indices of rainbow trout (Oncorhynchus mykiss). Aquaculture, 190: 27-47. DOI: 10.1016/S0044-8486(00)00383-5##Sajjadi, M., 2017. Aquafeed formulation. University of Guilan Press. 287P. (In Persian)##Sayed Hassani, M. Alipour, A. Yousefi Jourdehi, A. and Yeganeh, H., 2018. The effect of stocking Density on growth and stress indices of fingerlings and juvenile Acipenser baerii reared in fiberglass tanks. Journal of Animal Physiology and Development, 11: 27-40. (In Persian)##Shamsaie, M. Foroudi, F. Shekarabi, S.P. Arabi, F. and Mohammadi, N., 2019. Effect of different levels of synthetic tryptophan on growth performance and carcass amino acids profile of rainbow trout (Oncorhynchus mykiss) fry. Journal of Renewable Natural Resources Research, 10: 10-53. (In Persian)##Tejpal, C.S. Pal, A.K. Sahu, N.P. Kumar, J.A. Muthappa, N.A. Vidya, S. and Rajan, M.G., 2009. Dietary supplementation of L-tryptophan mitigates crowding stress and augments the growth in Cirrhinus mrigala fingerlings. Aquaculture, 293: 277-279. DOI: 10.1016/j.aquaculture.2008.09.014##Valipour, A.R.  Gorohi, D. Sayad Bourani, M. and Hasanpour, A., 2023. Investigating of density effect on the growth and survival of Caspian Kutum, Rutilus frisii (Kamensky, 1901) pre-fattening in freshwater concrete ponds. Aquatic Animals Nutrition, 9: 81-95. DOI: 10.22124/janb.2023.25882.1224. (In Persian)##Vijayan, M.M. Ballantyne, J.S. and Leatherland, J.F., 1990. High stocking density alters the energy metabolism of brook charr (Salvelinus fontinalis). Aquaculture, 88: 371-381. DOI: 10.1016/0044-8486(90)90162-G##Weil, L.S. Barry, T.P. and Malison, J.A., 2001. Fast growth in rainbow trout is correlated with a rapid decrease in post-stress cortisol concentrations. Aquaculture, 193: 373-380. DOI: 10.1016/S0044-8486(00)00482-8##Williot, P. Malison, L. Gessner, J. Arlatdi, G. Bronzi, P. and Gulyas, T., 2001. Sturgeon farming in Western Europe: recent developments and perspectives. Aquatic Living Resources, 14: 367-374. DOI: 10.1016/S0990-7440(01)01136-6##Williot, P. Arlati, G. Chebanov, M. Gulyas, T. Kasimov, R. Kirschbaum, F. Patriche, N. Pavlovskaya, L.P. Poliakova, L. Pourkazemi, M. Kim, Y, Zhuang, P. and Zholdasova, I., 2002. Status and management of Eurasian sturgeon: an overview. International Review of Hydrobiology, 87: 483-506. DOI: 10.1002/1522-2632(200211)87:5/6&#60;483::AID-IROH483&#62;3.0.CO;2-K##Yasmin, F. Sutradhar, S. Roy, A. Sarkar, R. and Mukherjee, S., 2023. Impacts of protein-, L-tryptophan-, carbohydrate-, oil-rich diets on growth performance, levels of melatonin, oxidative stress, antioxidative agents, and vital digestive enzymes in the gut of juvenile carp (Catla catla). Journal of Endocrinology and Reproduction, 27: 261-278. DOI: 10.21203/rs.3.rs-2707236/v1##Zhang, X. Chang, E. Fu, Y. Liu, X. Xu, J. Wu, Y. Wang, A. Dong, X. and Miao, S., 2023. Tryptophan can alleviate the inhibition in growth and immunity of tilapia (GIFT Oreochromis spp.) induced by high dietary soybean meal level. Aquaculture Reports, 31: 1-10. DOI: 10.1016/j.aqrep.2023.101646##Zhang, Z. Zhang, M. Hong, J. Guo, C. Jiang, X. Dong, P. Huang, X. Yang, Z. Guo, G. Li, X. Zhao, D. Li, G. Li, M. Yu, G. and Liu, B., 2024. Tryptophan attenuates soybean meal-induced intestinal oxidative stress, mitophagy hyperactivation, and apoptosis inhibition in hybrid yellow catfish (Pelteobagrus fulvidraco ♀ × Pelteobagrus vachelli ♂), to improve intestinal health. Animal Science and Technology, 596: 1-52. DOI: 10.2139/ssrn.4823332## Zhu, H. Gong, G. Wang, J. Wu, X. Xue, M. Niu, C. Guo, L. and Yu, Y., 2011. Replacement of fish meal with blend of rendered animal protein in diets for Siberian sturgeon (Acipenser baerii Brandt), results in performance equal to fish meal fed fish. Aquaculture Nutrition, 17: 1389-1401. DOI: 10.1111/j.1365-2095.2010.00773.x## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ برآورد میزان تنوع ژنتیکی در ذخیره مولدین فیل‌‌ماهی (Huso huso Linnaeus, 1758) با استفاده از داده‌های حاصل از توالی یابی ژنوم</TitleF>
		<TitleE>Genomic-based investigation of genetic diversity in broodstock of beluga (Huso huso Linnaeus, 1758)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>فیل&#8204;&#8204;ماهی به عنوان اصلی&#8204;ترین گونه پرورشی از ماهیان خاویاری در ایران مطرح بوده که ذخیره مولدین کنونی آن از تعداد محدودی مولد وحشی در دو گذشته ایجاد شده است. فقدان گونه&#8204;&#8204;های شناسنامه&#8204;دار یکی از مهم&#8204;ترین عوامل محدودکننده در توسعه صنعت آبزی&#8204;پروری ماهیان خاویاری در ایران بوده است. از این&#8204;رو، در پروژه حاضر و برای اولین بار از تکنیک توالی&#8204;&#8204;یابی مبتنی بر ژنوم[1] به منظور برآورد تنوع ژنتیکی و تهیه شناسنامه مولکولی مبتنی بر ژنوم از ذخیره مولدین فیل&#8204;&#8204;ماهی موجود در انستیتو ماهیان خاویاری، استفاده شد. توالی&#8204;&#8204;یابی ژنومی منجر به تولید GB294 داده حاصل از 261974459 خوانش ژنومی شد که در نهایت باعث شناسایی 1836 نشانگر SNP[2] در ژنوم فیل&#8204;&#8204;ماهی شد که بیشترین تعداد آن بر کروموزوم شماره 58 مشاهده شد. نتایج حاصل از تجزیه&#8204;&#8204;وتحلیل SNPs کشف&#8204;&#8204;شده نشان داد که میزان هتروزیگوسیتی موردمشاهده در ذخیره مولدین فیل&#8204;&#8204;ماهی موجود در انستیتو، 35/0 است. همچنین 105 آلل در ذخیره مولدین مورد بررسی یافت شد که بیانگر تنوع آللی مناسب در این گونه بود. نتایج حاصل از روابط هم&#8204;&#8204;تباری با استفاده از مارکرهای SNP شناسایی شده برای اولین بار نشان داد که ذخیره ژنتیکی مولدین فیل&#8204;&#8204;ماهی در انستیتو در دو خوشه ژنتیکی، قابل تقسیم بندی هستند. میزان همخونی در مولدین فیل&#8204;&#8204;ماهی مورد بررسی 02/0 برآورد گردید که این میزان پایین همخونی در کنار ساختار جمعیتی مختلط مورد مشاهده در آزمون PCA می&#8204;تواند بیانگر تنوع بالا در مولدین وحشی ایجادکننده جمعیت حاضر باشد. با توجه به دسترسی بسیار محدود به مولدین وحشی برای غنی&#8204;سازی خزانه ژنی گله&#8204;های پرورشی، پیشنهاد می&#8204;&#8204;گردد تا با استفاده از روش&#8204;&#8204;های نوین مبتنی بر ژنومیکس در زمینه شناسایی خزانه&#8204;های ژنی، حفظ ساختارهای ژنتیکی و تکثیر هدفمند بر اساس اطلاعات ژنتیکی در بازسازی ذخایر و آبزی&#8204;پروری اقدام گردد.
&#160;

[1] Genotyping-by sequencing

[2] Single nucleotide polymorphism (SNP)</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
Sturgeons (Acipenseriformes) are of the most commercially and scientifically important fish species in the globe. These fish are mostly anadromous, spending most of the life cycle in the marine and brackish waters and migrating to the freshwater rivers to spawn (Kottelat and Freyhof, 2007). The Caspian Sea basin has been the main refuge for six species of sturgeons namely Huso huso, Acipenser persicus, Acipenser stellatus, Acipenser guldenstaedtii, Acipenser nudiventris and Acipenser ruthenus, all of which under critically endangered level of the IUCN red list (IUCN, 2025). Generally speaking, the number of sturgeon species has declined, and the beluga (H. huso) is currently in the most critical situation due to a decline in the number of adults leading to local extinctions of the wild populations (Dudu et al., 2014). It is worth noting that female beluga does not spawn every year and the optimal reproductive performance of these fish occurs at an age equivalent to twice the age of first sexual maturity, which can be considered as a limiting factor in the survival of this species considering the shrinking populations (Boscari et al., 2021). Several factors such as overfishing and poaching for trade of caviar and meat, dam construction, loss of nursery grounds, pollution, global warming, and reduced volume of freshwater flowing into the seas are considered to be the most important components in the decline of wild sturgeon populations. In order to compensate the loss of wild populations of H. huso and on the other hand providing the human society required caviar and protein, Iranian Fisheries Organization started the restocking activity since five decades ago and stablished sturgeon aquaculture from two decades ago. Due to the sharp decrease in wild mature beluga of the southern Caspian Sea during the last decades, nowadays most of the aquaculture and restocking activities are forced to be focused on the brood stock generated from few wild parents in the past. Therefore, it is necessary to use modern molecular methods and prepare a genomic-based certificate to protect genetic reserves and enhance the genetic diversity of the native beluga in the south of the Caspian Sea. Genetic diversity represents the variations in the number and type of alleles available in chromosomal loci, which is also considered the main basis for the adaptation of species and populations against changing environmental conditions. While several molecular markers such as SSR, AFLP, and mtDNA, have been widely used during the four decades in fisheries studies (Robledo et al., 2018), these days due to the revolution in the genome sequencing technologies (NGS) more robust genotyping methods such as Genotyping-by Sequencing (GBS) can provide more diverse, sensitive and accurate estimations by screening thousands of variant markers throughout the whole genome of organisms even in species without reference genome (Sonah et al., 2013; Andrews et al., 2016; Barr&#237;a et al., 2018; Liu et al., 2018). Therefore, during the present study for the first we used a genome-based technique known as GBS in order to estimate the amount of genetic diversity and identify possible genetic nuclei in H. huso brood stock available at International Sturgeon Research Institute (ISRI).
Methodology
The feeding was stopped a week before sampling and each fish specimen was PIT tagged for later traceability purposes. Caudal fin tissues of 23 Huso huso was sampled and preserved in absolute ethanol for later molecular experiments. DNA extraction was done from the fin tissues through Phenol-Chloroform method with minor modifications (Jafari et al., 2022) and their quality and quantity in terms of DNA integrity, purity and concentration were determined using 0.8% agarose gel and Nano Drop instrument (ND 1000). After DNA samples were qualitatively approved, DNA pellets were sent to Novogene for 150bp PE sequencing on a lane of Illumina Novaseq 6000. Quality of the raw reads generated by sequencing were assessed through Trim Galore (https://www.bioinformatics.babraham.ac.uk/projects/trim_galore/) and only window reads with mean quality of 20 were kept in the final dataset. The clean data set then mapped to the genome reference of Huso huso using Bowtie2 (Langmead and Salzberg, 2012) and the SNP calling was performed based on Stacks. After conducting SNP calling, SNPs were filtered based on parameters such as MAF of 0.05, LD and Hardy-Weinberg equilibrium. Dispersal of fish individuals were visualized using Principal Component Analysis (PCA) based on the two first components in R (Team, 2013). Furthermore, FineRADstructure was used to illustrate the probable genetic clusters based on coancestry information through SNPs (Malinsky et al., 2018).
Results
The sequence quality analysis showed that the quality of the sequences was high with an average of 92.55. In total, 294 Gb of DNA data obtained from GBS libraries contained an average of 41% guanine (G) and cytosine (C) bases in the genome of Huso huso. PE genomic sequencing produced 261,974,459 reads, with an average alignment of 90% to the reference genome (Table 1). The average number of reads obtained from DNA sequencing in each specimen was about 11 million reads. The results of variant calling showed that a total of 1836 SNP markers with a minimum allele frequency of 0.05 were called from genome sequencing in H. huso with the maximum number of SNPs detected on chromosome 58 (Fig. 1). Based on the results obtained from SNPs obtained from genomic sequencing, the amount of genetic diversity observed in the H. huso broodstock was 0.35. Also, the inbreeding and nucleotide diversity were calculated to be 0.02 and 0.28, respectively (Table 2). The distribution of genetic diversity in the H. huso broodstock using the two first components of PCA is depicted in Figure 2. Based on the results of the PCA, the first two components accounted for 31.89% of the variance. The results of the phylogenetic relationships based on coancecstry relationship also showed that the studied broodstock of H. huso can be considered in two main genetic sub-groups (Fig. 3).
Discussion and conclusion
Identifying genetic reserves and maintenance of genetic diversity are among the most important measures in managing broodstock either in a sustainable aquaculture activity or in a restocking program. In sturgeons&#8217; aquaculture, there is a particular concern about the reduction of genetic diversity in intensive beluga farming. Preservation of an appropriate level of genetic diversity within the population is of great importance in diminishing negative effects of inbreeding and genetic drift. In the present study, and to the best of our knowledge for the first time in Iran, the identification of genetic groups in the broodstock of Huso huso available at the International Sturgeon Research Institute was carried out using GBS method. Accordingly, creation of a genetic certificate using 1836 SNP markers obtained from GBS was successfully implemented on 23 H. huso. Based on the obtained results from 1836 SNP marker, the observed heterozygosity was 0.36 in the investigated broodstock of H. huso. Observed heterozygosity is the most common indicator of genetic diversity used in determining the genetic health of fish broodstocks. Alongside with the observed heterozygosity, allelic richness should also be taken into consideration in assessment of genetic diversity. Results of the SNP markers showed a considerable number of alleles (An= 105) in the studied broodstock of H. huso, indicating a satisfactory level of heterogeneity in this broodstock. This was also supported by the small value of inbreeding (Fis= 0.02). The UPGMA tree based on coancestry information revealed an admixture pattern of genetic clustering in H. huso. It seems that wild parents from different populations had been used in generating the broodstock of H. huso at ISRI during the past decades. However, based on the genetic clustering heatmap it is suggested to consider two genetic nuclei in the investigated broodstock of H. huso in order to keep the genetic diversity for future sustainable aquaculture purposes.
Conflict of interest
The authors declare that they have no conflict of interest.
Acknowledgment
Hereby we wish to appreciate Iranian Fisheries Science Research Institute and Iranian Fisheries Organization for their financial support and also providing laboratory required equipment to conduct the current project.</CONTENT>
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		<RECEIVE_DATE>
			2025/02/112025/07/7
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		<RECEIVE_DATE_FA>
			1404/4/16
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		<ACCEPT_DATE>
			2025/08/12025/08/1
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		<ACCEPT_DATE_FA>
			1404/5/10
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		<AUTHORS>
			<AUTHOR>
				<Name>امید</Name>
				<MidName></MidName>
				<Family>جعفری</Family>
				<NameE>Omid</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jafari</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>jaafari.omi@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>ناصر</Name>
				<MidName></MidName>
				<Family>کرمی راد</Family>
				<NameE>Naser</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Karamirad</FamilyE>
				<Organizations>
				<Organization>سازمان شیلات ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Naserkaramiradddd@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>گلشن</Family>
				<NameE>Mehdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Golshan</FamilyE>
				<Organizations>
				<Organization>مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Mahdigolshan@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی نقی</Name>
				<MidName></MidName>
				<Family>سرپناه</Family>
				<NameE>Alinaghi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sarpanah</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Alinaghisarpanahhh@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهرشاد</Name>
				<MidName></MidName>
				<Family>زین العابدینی</Family>
				<NameE>Mehrshad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Zeinolabedini</FamilyE>
				<Organizations>
				<Organization>پژوهشگاه بیوتکنولوژی کشاورزی ایران، سازمان تحقیقات، آموزش و ترویج کشاورزی، کرج، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Mzeinalabediniii@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>اسماعیل</Name>
				<MidName></MidName>
				<Family>عبداله زاده</Family>
				<NameE>Esmaeil</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Abdollahzadeh</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>abdolahzadehhhh@rocketmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>حسن زاده صابر</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hassanzadeh Saber</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>meraj.saberrrr@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مریم</Name>
				<MidName></MidName>
				<Family>نصراله پورمقدم</Family>
				<NameE>Maryam</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Nasrolahpourmoghadam</FamilyE>
				<Organizations>
				<Organization>سازمان شیلات ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Pourmoghadamm@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>شکوری</Family>
				<NameE>Mehdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shakoori</FamilyE>
				<Organizations>
				<Organization>سازمان شیلات ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mshakouriiiii@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمود</Name>
				<MidName></MidName>
				<Family>محسنی</Family>
				<NameE>Mahmood</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohseni</FamilyE>
				<Organizations>
				<Organization>انستیتو تحقیقات بین المللی ماهیان خاویاری، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، رشت، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mohseniiii@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Gene pool</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Genomics</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Inbreeding</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>SNP</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Sturgeons</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>چندشکلی تک‌نوکلئوتیدی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خزانه ژنی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>درون‌آمیزی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ژنومیکس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماهیان خاویاری</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Andrews, K.R., Good, J.M., Miller, M.R., Luikart, G. and Hohenlohe, P.A., 2016. Harnessing the power of RADseq for ecological and evolutionary genomics. Nature Reviews Genetics, 17(2), pp.81-92.##Barría, A., Christensen, K.A., Yoshida, G.M., Correa, K., Jedlicki, A., Lhorente, J.P., Davidson, W.S. and Yáñez, J.M., 2018. Genomic predictions and genome-wide association study of resistance against Piscirickettsia salmonis in coho salmon (Oncorhynchus kisutch) using ddRAD sequencing. G3: Genes, genomes, genetics, 8(4), pp.1183-1194.##Boscari, E., Marino, I.A., Caruso, C., Gessner, J., Lari, M., Mugue, N., Barmintseva, A., Suciu, R., Onara, D., Zane, L. and Congiu, L., 2021. Defining criteria for the reintroduction of locally extinct populations based on contemporary and ancient genetic diversity: The case of the Adriatic Beluga sturgeon (Huso huso). Diversity and Distributions, 27(5), pp.816-827.##Catchen, J., Hohenlohe, P.A., Bassham, S., Amores, A. and Cresko, W.A., 2013. Stacks: an analysis tool set for population genomics. Molecular ecology, 22(11), pp.3124-3140.##Çiftci, Y., Eroğlu, O. and Firidin, Ş., 2013. Mitochondrial cytochrome b sequence variation in three Sturgeon species (A. stellatus Pallas, 1771, A. gueldenstaedtii Brandt, 1833, H. huso Linnaeus, 1758) from the Black Sea Coasts of Turkey. Turkish Journal of Fisheries and Aquatic Sciences, 13(2).##Dudu, A., Georgescu, S.E. and Costache, M., 2014. Molecular analysis of phylogeographic subspecies in three Ponto-Caspian sturgeon species. Genetics and molecular biology, 37, pp.587-597.##Freyhof, J., Bergner, L. and Ford, M., 2020. Threatened Freshwater Fishes of the Mediterranean Basin Biodiversity Hotspot: Distribution, extinction risk and the impact of hydropower. EuroNatur and RiverWatch. i-viii, pp.1-348.##Friedrich, T., Reinartz, R. and Gessner, J., 2019. Sturgeon re‐introduction in the Upper and Middle Danube River Basin. Journal of Applied Ichthyology, 35(5), pp.1059-1068.##IUCN. 2025. The IUCN Red List of Threatened Species. Version 2025-1. https://www.iucnredlist.org. Accessed on 02.07.2025.##Jafari, O., Nasrolahpourmoghadam, M. and Zeinalabedini, M., 2025. 16S rRNA revealed a low rate of maternal genetic variations in Cyprinus carpio Linnaeus, 1758 across the southern Caspian Sea. International Journal of Aquatic Biology, 13(1), pp.1-7.##Jafari, O., Zeinalabedini, M., Robledo, D., Fernandes, J.M., Hedayati, A.A. and Arefnezhad, B., 2022. Genotyping-by-Sequencing reveals the impact of restocking on wild common carp populations of the Southern Caspian Basin. Frontiers in Ecology and Evolution, 10, p.872176.##Kottelat, M. and Freyhof, J., 2007. Handbook of European freshwater fishes (Vol. 13). Cornol, Switzerland: Publications Kottelat.##Langmead, B. and Salzberg, S.L., 2012. Fast gapped-read alignment with Bowtie 2. Nature methods, 9(4), pp.357-359.##Liu, S., Ferchaud, A.L., Grønkjær, P., Nygaard, R. and Hansen, M.M., 2018. Genomic parallelism and lack thereof in contrasting systems of three‐spined sticklebacks. Molecular ecology, 27(23), pp.4725-4743.##Malinsky, M., Trucchi, E., Lawson, D.J. and Falush, D., 2018. RADpainter and fineRADstructure: population inference from RADseq data. Molecular biology and evolution, 35(5), pp.1284-1290.##Moghim, M., Javanmard, A., Lolaei, F., Taghavi, M.J. and Bakhshalizadeh, S., 2025. Nuclear Multi‐Microsatellite Marker Profiling Provides Clues to Molecular Genetic Diversity in Culture‐Based Caspian Beluga Sturgeon (Huso huso) Broodstocks: Ecological Mirror for Restoration. Veterinary Medicine and Science, 11(3), p.e70255.##Najafikhah, A., Jafari, O., Nasrolahpourmoghadam, M. and Zeinalabedini, M., 2025. Molecular genetic assessments of the ongoing restocking activities on Salmo caspius Kessler, 1877. Journal of Fish Biology.##Robledo, D., Palaiokostas, C., Bargelloni, L., Martínez, P. and Houston, R., 2018. Applications of genotyping by sequencing in aquaculture breeding and genetics. Reviews in aquaculture, 10(3), pp.670-682.##Sonah, H., Bastien, M., Iquira, E., Tardivel, A., Légaré, G., Boyle, B., Normandeau, É., Laroche, J., Larose, S., Jean, M. and Belzile, F., 2013. An improved genotyping by sequencing (GBS) approach offering increased versatility and efficiency of SNP discovery and genotyping. PloS one, 8(1), p.e54603.##Team, R. C., 2013. R: A Language and Environment for Statistical Computing. Vienna: R Foundation for Statistical Computing.##Wang, J., Sun, Z., Jiang, L. and Hu, Y., 2022. Developing microsatellite duplex PCR reactions for sterlet (Acipenser ruthenus) and their application in parentage identification. Scientific Reports, 12(1), p.12036.##Zerunian, S., 2003. Piano d'azione generale per la conservazione dei Pesci d'acqua dolce italiani (No. 17). Ministero dell'ambiente e della tutela del territorio, Direzione per la protezione della natura.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ سمیت تحت‌‌کشنده حشره‌‌کش دیازینون بر رشد، زنده‌مانی، فعالیت آنزیم‌های آنتی‌‌اکسیدانی و گوارشی پریان میگو 
(Phallocryptus spinosa Milne-Edwards, 1840)</TitleF>
		<TitleE>Sublethal toxicity of the Diazinon insecticide on the growth, survival, antioxidant and digestive enzymes activity of Fairy shrimp (Phallocryptus spinosa)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>آلودگی محیط&#8204;&#8204;زیست در اثر استفاده از حشره&#8204;&#8204;کش&#8204;&#8204;ها در فعالیت&#8204;&#8204;های کشاورزی، تهدیدی جدی برای بوم&#8204;&#8204;سازگان&#8204;&#8204;های آبی محسوب می&#8204;شود که می&#8204;تواند چرخه زندگی و ذخایر زیستی بسیاری از گونه&#8204;های زی&#8204;&#8204;شناوران جانوری (ریزسخت&#8204;&#8204;پوستان) را تحت تأثیر قرار دهد. از این&#8204;رو، در مطالعه حاضر اثر سمیت حشره&#8204;&#8204;کش دیازینون بر رشد، زنده&#8204;مانی، فعالیت آنزیم&#8204;های آنتی&#8204;&#8204;اکسیدانی و گوارشی در پریان میگو ( Phallocryptus spinosa) مورد بررسی قرار گرفت. غلظت کشندگی میانی (LC50) برای مرحله&#8204;های ناپلی و بلوغ و در ساعت&#8204;های 24، 48، 72 و 96 با استفاده از تجزیه&#8204;وتحلیل آماری پروبیت تعیین گردید. به&#8204; منظور بررسی اثر غلظت&#8204;&#8204;های تحت&#8204;&#8204;کشنده دیازینون، میانگین غلظت&#8204;های LC50 96 ساعته استفاده شد و ناپلی&#8204;ها در قالب 4 تیمار شامل گروه شاهد، 25 درصد LC50، 50 درصد LC50 و 100 درصد LC50 به مدت 7 روز پرورش داده شدند. نتایج نشان داد، غلظت&#8204;های مختلف دیازینون باعث کاهش درصد زنده&#8204;مانی و رشد پریان میگو (P. spinosa) در روزهای 3، 5 و 7 پرورش شد (05/0&#62;p). فعالیت آنزیم&#8204;&#8204;های آنتی&#8204;&#8204;اکسیدانی (سوپر اکسید دیسموتاز، کاتالاز و گلوتاتیون پراکسیداز) و محتوای مالون دی&#8204;&#8204;آلدئید در غلظت&#8204;&#8204;های مختلف سم دیازینون افزایش یافت (05/0&#60;p). همچنین سطح فعالیت آنزیم&#8204;&#8204;های گوارشی (پروتئاز، لیپاز و آلفا آمیلاز) نیز در غلظت&#8204;&#8204;های مختلف سم دیازینون افزایش یافت (05/0&#60;p). بر اساس نتیجه&#8204;گیری نهایی می&#8204;توان بیان کرد که حشره&#8204;&#8204;کش دیازینون منجر به کاهش زنده&#8204;&#8204;مانی و رشد و تغییر در فعالیت فعالیت آنزیم&#8204;های آنتی&#8204;&#8204;اکسیدانی، محتوای مالون دی&#8204;&#8204;آلدئید و آنزیم&#8204;&#8204;های گوارشی در پریان میگو (P. spinosa) شد. بنابراین، بایستی در ارتباط با چگونگی مدیریت در دفع پساب&#8204;های آلوده به سموم کشاورزی توجه بیشتری صورت پذیرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction Population growth and limited production inputs have forced farmers to use pesticides (Zand et al., 2002), and aquatic ecosystems are consistently exposed to these pollutants (Mansingh and Wilson, 1995). Pesticide contamination in aquatic ecosystems poses a serious threat to the foundation of the food chain (Aydın and K&#246;pr&#252;c&#252;, 2005; De Prado et al., 2012). Pesticides at the chronic level led to destructive effects in various physiological functions (Varo et al., 2002; Koprucu and Koprucu, 2006). Additionally, organophosphorus pesticides have been shown to induce oxidative stress, alter growth rates, and disrupt reproductive indices in the larvae of the shrimp Streptocephalus dichotomus (Arun Kumar and Javahar, 2014). Diazinon is one of the most important organophosphorus pesticides. As a persistent pesticide, it is highly toxic to fish and aquatic invertebrates (Coupe et al., 2000; Samadi et al., 2019). This chemical is easily washed away after use, entering aquatic environments in significant quantities (Aydın &#38; K&#246;pr&#252;c&#252;, 2005). Many species of large branchiopods occur in temporary habitats surrounding agricultural areas and farmlands, which serve as locations where Phallocryptus spinosa can be found (Atashbar et al., 2014). Phallocryptus spinosa inhabits temporary freshwater to brackish water bodies, the hydroregime patterns of which are highly unpredictable. These habitats typically fill in early spring and dry out by summer (Atashbar et al., 2014). Environmental pollution from diazinon-one of the most widely used agricultural pesticides-affects the life cycle of zooplankton, such as fairy shrimp, and threatens their populations. Thus, understanding the impact of such substances on the environment, particularly aquatic ecosystems, is essential. Therefore, this study aimed to investigate the effects of diazinon insecticide toxicity on the growth, survival, and activity of antioxidant and digestive enzymes in P. spinosa larvae.  Methodology This study was conducted at the Artemia and Aquaculture Research Institute of Urmia University. P. spinosa shrimp cyst hatching was performed following the method recommended by Atashbar et al. (2012). To determine the 24-hour LC50 of diazinon, a preliminary range-finding test was first conducted using 30 shrimp larvae (in triplicate) (Lan and Lin, 2005). Based on these results, three experimental treatments (Table 1) were selected to investigate the effects of sublethal diazinon concentrations on shrimp rearing conditions. Survival and growth rates were assessed on days 1, 3, 5, and 7 using the methods of Rahimi and Nejatkhah Manavi (2011) and Agh et al. (2008). The activities of SOD, CAT and GPX enzymes were measured according to Yazdanparast et al. (2008). Malondialdehyde (MDA) activity&#160;was determined based on thiobarbituric acid inhibition by MDA in the crude enzyme extract (Ledwożyw et al., 1986). Digestive enzyme activities were measured as follows: Alkaline protease: Garcia-Carreno and Haard (1993), Lipase: Iijima et al. (1998), Alpha-amylase: Bernfeld (1955). Data were analyzed using one-way ANOVA in SPSS (version 21), with a significance level (Type I error) set at &#945; = 0.05. Results The comparison of mean survival percentages (Table 3) revealed a significant decrease due to diazinon exposure (p &#60; 0.05 Day 3: a significant difference (p&#60;0.05) was observed between treatment 1 (control) and treatment 4 (100% diazinon). Day 5: significant differences (p&#60;0.05) were detected between treatment 1 and treatments 2 (25% diazinon), 3 (50% diazinon), and 4. Also, treatments 2 and 3 vs. treatment 4. Day 7: significant differences (p&#60;0.05) occurred between treatment 1 and treatments 2, 3, and 4 and between the treatment 2 and treatments 3 and 4. The highest survival rate was recorded in treatment 1, while the lowest was in treatment 4 (100% diazinon) (p&#60;0.05). Comparison of mean growth indices (Table 4) revealed a significant decrease due to diazinon exposure (p&#60;0.05). The significant differences were observed as follows: day 3: treatment 1 (control) vs. treatments 3 (50% diazinon) and 4 (100% diazinon), day 5: treatment 1 vs. treatments 3 and 4; treatment 2 (25% diazinon) vs. treatment 4; day 7: treatment 1 vs. treatments 2, 3, and 4; treatment 2 vs. treatments 3 and 4; treatment 3 vs. treatment 4. The highest growth rate was observed in treatment 1 (control), while the lowest occurred in treatment 4 (100% diazinon) (p&#60; 0.05). The results for whole-body antioxidant enzyme activity and malondialdehyde (MDA) levels (Figure 1) showed significant increases due to diazinon exposure (p&#60;0.05). Significant differences were observed in: SOD activity: treatment 1 (control) vs. treatments 2 (25% diazinon), 3 (50% diazinon), and 4 (100% diazinon); CAT activity: treatment 1 vs. treatments 3 and 4; GPX activity: treatment 1 vs. treatments 2, 3, and 4; treatment 3 vs. treatments 2 and 4; MDA content: treatment 1 vs. treatments 2, 3, and 4; treatment 4 vs. treatments 2 and 3. The results of whole-body digestive enzyme activity (Figure 2) showed significant increases due to diazinon exposure (p&#60;0.05). Alkaline protease, lipase, and &#945;-amylase in treatment 1 (control) showed significant differences compared to treatments 2 (25% diazinon), 3 (50% diazinon), and 4 (100% diazinon) (p&#60;0.05). The &#945;-Amylase in treatment 4 differed significantly from treatments 2 and 3 (p&#60;0.05). The lowest and highest levels of alkaline protease activity were observed in treatments 1 and 4, respectively, and the lowest and highest activity of lipase and alpha-amylase enzymes were observed in treatments 1 and 3, respectively (p&#60;0.05). Discussion and conclusion The results of this study demonstrated that shrimp larval survival decreased with increasing diazinon concentration. This aligns with findings by Taylor et al. (1998), where pollutant exposure affected vital functions in zooplankton, leading to population density reduction, decreased oxygen consumption, and nutritional limitations that ultimately impact survival rates. Additionally, shrimp larval growth declined at higher diazinon concentrations. Asadpour et al. (2012) attributed such growth reduction to disturbances in feeding behavior and alterations in biochemical and physiological responses to pollutants. Toxins reduce growth through absorption and organ damage (Cong et al., 2009; Rudnicki et al., 2009; Aggarwal et al., 2013). Our results demonstrated elevated levels of SOD, CAT, GPX, and MDA following diazinon exposure. The increased SOD and CAT enzyme levels reflect stimulated free radical elimination (Rumley and Paterson, 1998), while elevated GPX activity indicates an enhanced antioxidant defense capacity against radical chain reactions in P. spinosa (Schneider et al., 2005). The rise in MDA content suggests diazinon-induced lipid peroxidation (Jafari et al., 2012). We also observed increased digestive enzyme activity at various diazinon concentrations. This may result from toxin-induced stress altering feeding behavior and subsequent digestive enzyme secretion (Suzer et al., 2006). In summary, diazinon exposure at different concentrations: (1) reduced survival and growth rates, (2) disrupted vital physiological functions in P. spinosa larvae. Conflict of interest The authors declare no conflict of interests. Acknowledgment We extend our heartfelt thanks to the Office of Vice Chancellor for Research and Artemia and Aquaculture Research Institute of Urmia University for enabling this research.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>29</FPAGE>
			<TPAGE>42</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/02/112025/07/72025/02/20
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/12/2
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/08/12025/08/12025/08/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/5/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>بهروز</Name>
				<MidName></MidName>
				<Family>آتشبار کنگرلویی</Family>
				<NameE>Behrooz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Atashbar Kangarloei</FamilyE>
				<Organizations>
				<Organization>گروه اکولوژی و مدیریت ذخایر آبی، پژوهشکده آرتمیا و آبزی‌پروری، دانشگاه ارومیه، ارومیه، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>b.atashbar@urmia.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مجتبی</Name>
				<MidName></MidName>
				<Family>پوراحد انزابی</Family>
				<NameE>Mojtaba</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Pourahad Anzabi</FamilyE>
				<Organizations>
				<Organization>گروه شیلات و آبزیان، دانشکده منابع طبیعی، دانشگاه ارومیه، ارومیه ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>adel.porahad@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رامان</Name>
				<MidName></MidName>
				<Family>امینی</Family>
				<NameE>Raman</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Amini</FamilyE>
				<Organizations>
				<Organization>گروه شیلات و آبزیان، دانشکده منابع طبیعی، دانشگاه ارومیه، ارومیه ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>ramanamini75@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Diazinon</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Growth</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Survival</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Antioxidant enzymes</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Digestive enzymes</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Phallocryptus spinosa</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>دیازینون</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رشد</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زنده‌مانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آنزیم‌‌های آنتی‌‌اکسیدانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آنزیم‌های گوارشی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Phallocryptus spinosa</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Aggarwal, V., Deng, X., Tuli, A. and Goh, K.S., 2013. Diazinon- chemistry and environmental fate: A California perspective. In: Whitacre, D.M. (eds) Reviews of Environmental Contamination and Toxicology. pp 107-140. DOI: 10.1007/978-1-4614-5577-6_5##Atashbar, B., Agh, N., Manaffar, R., Van Stappen, G., Mohammadyari, Ali., Mertens, J. and Beladjal, L., 2016. Morphometric and preliminary genetic characteristics of Branchinecta orientalis populations from Iran (Crustacea: Anostraca). Zootaxa 4109 (1): 031–045 DOI: 10.11646/zootaxa.4109.1.3##Alishahi, M. and Dezfuly, T.Z., 2019. Comparative toxicities of five herbicides on nauplii of Artemia franciscana as an ecotoxicity bioindicator. Iranian Journal of Fisheries Sciences, 18(4): 716-726. DOI: 10.22092/ijfs.2019.118284##Alishahi, M., Heidari, B., 2010. Investigating the toxicity of silver nanoparticles in Urmia lake Artemia. Journal of modern veterinary research 8, 49-54. (in Persian)##Amiard-Triquet, C., Amiard, J.C. and Rainbow, P.S., 2012. Ecological biomarkers: indicators of ecotoxicological effects. CRC Press, United States of America. pp 279-306.##Angelibert, S., Marty, P., Cereghino, R. and Giani, N., 2004. Seasonal variations in the physical and chemical characteristics of ponds: implications for biodiversity conservation. Aquatic Conservation: Marine and Freshwwater Ecosystems, 14(5): 439-456. DOI: 10.1002/aqc.616##Arun Kumar, MS. and Javahar, Ali., 2014. Effect of two organophosphorus pesdicides on the reproductive bionomics of freshwater Fairy shrimp Streptocephalus dichotomus (Baird, 1860) (Crustacea: Anostraca). International Journal of Bioassays, 3(9): 3305-3312. ##Asadpour, Y.A., Nejatkhah Manavi, P. and Baniamam, M., 2012. Evaluating the Bioaccumulation of Nickel and Vanadium and their effects on the growth of Artemia urmiana and A. franciscana. Iranian Journal of Fisheries Sciences, 12(1):183-192. DOI: 20.1001.1.15622916.2013.12.1.15.8##Atashbar, B., Agh, N., Beladjal, L., Jalili, R. and Mertens, J., 2012. Effects of temperature on survival, growth, reproductive and life span characteristics of Branchinecta orientalis G. O. Sars, 1901 (Branchipoda, Anostraca) from Iran. Crustaceana, 85: 1099–1114. DOI: 10.1163/15685403-00003115.##Atashbar, B., Agh, N., Van Stappen, G. and Beladjal, L., 2014. Diversity and distribution patterns of large branchiopods (Crustacea: Branchiopoda) in temporary pools (Iran). Journal of Arid Environments, 111:27-34. DOI: 10.1016/j.jaridenv.2014.07.005##Ates, M., Daniels, J., Arsalan, Z. and Farah, I.O., 2013a. Comparative evaluation of impact of Zn and ZnO on brine shrimp (Artemia salina) larvae: effects of particle size and solubility on toxicity. The Royal Society of Chemistry, 15: 225-233. DOI: 10.1039/c2em30540b##Ates, M., Daniels, J., Arsalan, Z., Farah, I.O. and Rivera, H.F., 2013b. Effects of aqueous suspensions of titanium dioxide nanoparticles on Artemia salina assessment of nanoparticle aggregation, accumulation and toxicity. Environmental Monitoring and Assessment, 85: 3339-3348. DOI: 10.1007/s10661-012-2794-7##Aydın, R. and Köprücü, K., 2005. Acute toxicity of diazinon on the common carp (Cyprinus carpio L.) embryos and larvae. Pesticide biochemistry and physiology, 82(3): 220-225. DOI: 10.1016/j.pestbp.2005.03.001##Bakhtiyari, R., Sarvi Moghanlou, K., Atashbar Kangarloei, B., Imani, A., Pourahad Anzabi, M., 2023. Changes in growth, survival, and some physiological indices of Urmia Lake Artemia (Artemia urmiana) under chronic toxicity of Cypermethrin insecticide. Iranian Scientific Fisheries Journal, 32(1): 95-108. DOI: 10.22092/ISFJ.2023.129148 (In Persian).##Bernfeld, P., 1955. Amylase. In: Colowick, S.P. and Kaplan, N.O. (eds) Methods in Enzymology. Academic Press, New York. pp 149-158. DOI: 10.1016/0076-6879(55)01021-5##Brix, K.V., Cardewell, R.D. and Adans, J.V., 2003. Chronic toxicity of arsenic to the Great Salt Lake brine shrimp, Artemia franciscana. Ecotoxicology and Enviromental Safety, 54: 169-175. DOI: 10.1016/S0147-6513(02)00054-4##Brix, K.V., Gerdes, R.M., Adams, W.J. and Grosell, M., 2006. Effect of copper, cadmium, and zinc on the hatching success of brine shrimp (Artemia franciscana). Archives of Environmental Contamination and Toxicology, 51: 580-583. DOI: 10.1007/s00244-005-0244-z.##Cong, N.V., Phuong, N.T. and Bayley, M., 2009. Effects of repeated exposure of diazinon on cholinesterase activity and growth in snakehead fish (Channa striata). Ecotoxicology and Environmental Safety, 72(3): 699-703. DOI: 10.1016/j.ecoenv.2008.10.007##Coupe, R.H., Manning, M.A., Foreman, W.T., Goolsby, D.A. and Majewski, M.S., 2000. Occurrence of pesticides in rain and air in urban and agricultural areas of Mississippi, pril–September 1995. Science of the Total Environment 248(2), 227-240. DOI: 10.1016/s0048-9697(99)00545-8##Coutteu, P., 1996. Micro- algea. In: Lavens, P. and Sorgeloos, P. (eds) Manual on the production and use of the live food for aquaculture. FAO, Rome. pp 9-60.##De Prado, R., Jorrín, J. and García-Torres, L., 2012. Weed and crop resistance to herbicides. Springer Science &#38; Business Media, Berlin, Germany. 356 p.##Federici G., Shaw B.J. and Handy, R.D., 2007. Toxicity of titanium dioxide nanoparticles to rainbow trout (Oncorhynchus mykiss): gill injury, oxidative stress, and other physiological effects. Aquatic Toxicology, 84(4): 415-430. DOI: 10.1016/j.aquatox.2007.07.009.##Gambardella,C., Mesaric, T., Milivojevic, T., Sepcic, K., Gallus, L., Cabone, S., Ferrando, S. and Fammali, M., 2014. Effects of selected metal oxide nanoparticles on Artemia salina larvae evaluation of mortality and behavioral and biochemical responses. Environmental Monitoring and Assessment, 186(7): 4249-4259. DOI: 10.1007/s10661-014-3695-8##Garcia-Carreno, F.L., Haard, N.F., 1993. Characterization of proteinase classes in Langostilla Pleuroncodes planipes and Crayfish Pacifastacus astacus extracts. Journal of Food Biochemistry, 17: 97–113. DOI: 200902104610913018##Ghamarshenas, S., Atashbar Kangarloei, B., Sarvi Moghanlou, K., Imani, A., Pourahad Anzabi, M., 2023. Effect of chronic toxicity of diazinon insecticide on growth, survival and physiological activities of Urmia Lake Artemia (Artemia urmiana). Journal of Fisheries, 76(2): 237-249. DOI: 10.22059/JFISHERIES.2023.351498.1353 (in persian).##Hadjispyrou, S., Kungolos, A., Anagnostopoulos, A. 2001. Toxicity, bioaccumulation, and interactive effects of organotin, cadmium, and chromium on Artemia franciscana. Ecotoxicology and Environmental Safety, 49(2): 179-186. DOI: 10.1006/eesa.2001.2059##Iijima, N., Tanaka, S., Ota, Y., 1998. Purification and characterization of bile salt-activated lipase fro hepatopancrease of red sea bream (Pagarus major). Fish Physiology and Biochemistry, 18: 59–69. DOI: 10.1023/A:1007725513389##Imani, A., Bani, M.S., Noori, F., Farzaneh, M. and Moghanlou, K.S., 2017. The effect of bentonite and yeast cell wall along with cinnamon oil on aflatoxicosis in rainbow trout (Oncorhynchus mykiss): Digestive enzymes, growth indices, nutritional performance and proximate body composition. Aquaculture 476: 160-167. DOI:10.1016/J.AQUACULTURE.2017.04.023##Jafari, M., Salehi, M., Asgari, A., Ahmadi, S., Abbasnezhad, M., Hajihoosani, R. and Hajigholamali, M., 2012. Effects of paraoxon on serum biochemical parameters and oxidative stress induction in various tissues of Wistar and Norway rats. Environmental Toxicology Pharmacology, 34: 876-887. DOI: 10.1016/j.etap.2012.08.011##Kardavani, P., 2005. Geohydrology. Tehran universty 3, 1-367. (In Persian)##Kasumyan, A.O., 2000. Effects of chemical pollutants on foraging behavior and sensitivity of fish to food stimuli. Journal of Ichthyology, 41(1): 76-87##Koprucu, S. and Koprucu, K., 2006. Acute toxicity of organophosphorous pesticide diazinon and its effects on behavior and some hematological parameters of fingerling european catfish (Silurus glanis L.). Pesticide Biochemistry and Physiology, 86: 99-105. doi.org/10.1016/j.pestbp.2006.02.001##Lan, C.H. and Lin, T.S., 2005. Acute toxicity of trivalent thallium compounds to Daphnia magna. Ecotoxicology and Environmental Safety, 61(3): 432-435. DOI: 10.1016/j.ecoenv.2004.12.021##Ledwozyw, A., Michalak, J., Stepien, A.K. and Adziolka, A., 1986. The relationship between plasma triglycerides, total lipids and lipid peroxidation products during huma atherosclerosis. Clinica Chimical Acta, 155: 275-284. DOI: 10.1016/0009-8981(86)90247-0.##Limon-Pacheco, J. and Gonsebatt, M.E., 2009. The role of antioxidants and antioxidant-related enzymes in protective responses to environmentally induced oxidative stress. Mutation Research- Genetic Toxicology and Environmental Mutagenesis, 674:137-47. DOI: 10.1016/j.mrgentox.2008.09.015.##Mansingh, A. and Wilson, A., 1995. Insecticide Contamination of Jamaican Environment Iii. Baseline Studies on the Status of Insecticidal Pollution of Kingston Harbor. Marine Pollution Bulletin, 30: 640-645. DOI: 10.1016/0025-326X(95)00038-O##Mohammadi, S., Sarvi Moghanlou, K., Atashbar, B., Imani, A., 2016. Studying the chronic effects of silver nanoparticles on the growth, survival and reproductive characteristics of Urmia Lake Artemia (Artemia urmiana). Iranian Journal of Fisheries Sciences, 25(4): 63-75. DOI: 10.22092/ISFJ.2017.110299 (in Persian).##Mohammadi, S., Sarvi Moghanlou, K., Manaffar, R., Atashbar Kangarloei, B. and Libralato, G., 2025. Effects of chronic toxicity of the heavy metal Cadmium on the growth, survival, digestive enzymes, and some reproductive indices of Artemia urmiana. Iranian Journal of Fisheries Sciences, 33(3): 77-90. DOI: 10.22092/ISFJ.2024.131971 (in Persian).##Mohiseni, M., Farhanghi, M., Mahiseni, A.A., Mirvaghefi, A., Shokouh, S.Z., 2008. The effect of age on the sensitivity of Artemia urmiana nauplius to different concentrations of diazinon insecticide. Journal of Agricultural Sciences and Natural Resources, 16(3), 77-85. (In Persian)##Novakova, J., Danova, D., Striskova, K., Hromada, R., Mickova, H. and Rabiskova, M., 2007. Zinc and cadmium toxicity using a biotest with Artemia franciscana. Acta Veterinaria Brno, 76(4): 635-642. DOI: 10.2754/avb200776040635##Nwani, C.D., Ifo, C.T., Nwamba, H.O., Ejere, V.C., Onyishi, G.C., Oluah, S.N., Ikwuagwu, O.E. and Odo, G.E., 2014. Oxidative stress and biochemical responses in the tissues of African catfish Clarias gariepinus juvenile following exposure to primextra herbicide. National Library of Medicine, 38(3): 278-285. DOI: 10.3109/01480545.2014.947503##Pierre, S., Tarnowska, K., Hachfi, L., Coupe, S., Simide, R., Couvray, S., Garnier, C., Grimaldi, M., Richard, S., Gaillard, S. and Grillasca, J.P., 2011. Effects of water temperature increase and heavy metals contamination on WAP65 gene expression in sea bass (Dicentrarchus labrax) liver. Cellular and Molecular Biology, 57(2): 1614-1622. DOI: 10.1170/205##Pimentel, D., 2005. Environmental and economic costs of the application of Pesticide Primarily in United States Environment. Development and Sustainability, 7(2): 229-252.##Qu, R., Feng, M., Wang, X., Qin, L., Wan, C., Wang, Z. and Wang, L., 2014. Metal accumulation and oxidative stress biomarkers in liver of freshwater fish Carassius auratus following in vivo exposure to waterborne zinc under different pH values. Aquatic Toxicology, 150(2): 9-16. DOI: 10.1016/j.aquatox.2014.02.008##Ramesh, R., Dube, K., Reddy, A.K., Rangacharyulu, P.V., Venkateshwarlu, G. and Jayasankar, P., 2017. Effect of varying protein levels on growth and digestive enzyme activities of pengba Osteobrama belangeri (Valenciennes, 1844). Indian Journal of Fisheries, 64: 206–213##Rahimi, B. and Nejatkhah Manavi, P. 2011. LC50 and bioaccumulationof Cd in different life stages of Artemia urmiana. Iranian Scientific Fisheries Journal, 20(1): 53-64. DOI: 10.22092/ISFJ.2017.109975 (in persian).##Rudnicki, C.A.M., Melo, G.C., Donatti, L., Kawall, H.G. and Fanta, E., 2009. Gills of juvenile fish piaractus mesopotamicus as histological biomarkers for experimental sublethal contamin- ation with the Organophosphorus Azodrin® 400. Brazilian Archives of Biology and Technology, 52(6): 1431-1441. DOI: 10.1590/S1516-89132009000600015 ##Rumley, A.G. and Paterson, J.R., 1998. Analytical aspects of antioxidants and free radical activity in clinical biochemistry. Annals of Clinical Biochemistry, 35: 181-200. DOI: 10.1177/000456329803500202##Rungraungsak-Torrissen, K., 2007. Digestive efficiency, growth and qualities of muscle and oocyte in Atlantic salmon (Salmo salar L.) fed with krill meal as an alternative protein source. Journal of Food Biochemistry, 31: 509–540. DOI: 10.1111/J.1745-4514.2007.00127.X##Samadi, H., Javadian, S.R. and Imanpour, M.R., 2019. Effect of sub-lethal toxicity of diazinon on steroid detoxification and quality of sexual production in male goldfish breeders (Carassius auratus). Iranian Journal of Fisheries Sciences 29(6), 133-142. DoI: 20.1001.1.10261354.1399.29.6.7.5 (in Persian)##Schneider, C.D., Barp, J., Ribeiro, J.L., Bello, K.A. and Oliveira, A.R., 2005. Oxidative stress after three different intensities of running. The Canadian Journal of Applied Physiology, 30:723-34. DOI: 10.1139/h05-151##Suzer, C., Saka, S. and Firat, K., 2006. Effects of illumination on early life development and digestive enzyme activities in common pandora Pagellus erythrinus L. larvae. Aquaculture, 260(1): 86-93. DOI: 10.1016/j.aquaculture.2006.06.025##Taylor, G., Baird, D.J. and Soares, A.M., 1998. Surface binding of contaminants by algae: consequences for lethal toxicity and feeding to Daphnia magna. Environmental Toxicology Chemistry, 17: 412-419. DOI: 10.1002/etc.5620170310##Valavanidis, A., Vlahogianni, T., Dassenakis, M. and Scoullos, M., 2006. Molecular biomarkers of oxidative stress in aquatic organisms in relation to toxic environmental pollutants. Ecotoxicology and Environmental Safety, 64(2): 178-189. DOI: 10.1016/j.ecoenv.2005.03.013##Varó, I., Serrano, R., Navarro, J.C., López, F.J. and Amat, F., 1998. Acute lethal toxicity of the organophosphorus pesticide chlorpyrifos to different species and strains of Artemia. Bulletin of Environmental Contamination and Toxicology, 61(6): 778-785. DOI: 10.1007/s001289900828##Varó, I., Navarro, J.C., Amat, F. and Guilhermino, L., 2002. Characterisation of cholinesterases and evaluation of the inhibitory potential of chlorpyrifos and dichlorvos to Artemia salina and Artemia parthenogenetica. Chemosphere, 48: 563-569. DOI: 10.1016/s0045-6535(02)00075-9##Yazdanparast, R., Bahramikia, S. and Ardestani, A., 2008. Nasturtioum officinale reduces oxidative stress and enhances hyper cholesterolaemic rats. Chemico- Biological Interactions, 172: 176-184. DOI: 10.1016/j.cbi.2008.01.006.##Yuksel, F., Aydin, R., Serdar, O. and Pala, A., 2020. Examining the biochemical effect of malathion pesticide on Gammarus pulex (L., 1798). Journal Fresenius environmental bulletin, 29: 9490-9497.##Zand, E., Baghestani, M.A., Shimi, P. and Faghih, S.A., 2002. Analysis of herbicide management in Iran. Pest and Plant Diseases Research Institute PP, 1-32. (in Persian)## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ ارزیابی ویژگی‌های اقتصادی-اجتماعی تعاونی‌های صید پره استان گلستان</TitleF>
		<TitleE>Evaluation of socio-economic characteristics of beach seine fishing cooperatives in Golestan Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>این پژوهش با هدف ارزیابی فرصت&#8204;های شغلی، هزینه&#8204;ها، دستمزد و حقوق افراد شاغل، سودآوری فعالیت و ویژگی&#8204;های جمعیت&#8204;شناسی تعاونی&#8204;های صید پره استان گلستان برای سال بهره&#8204;برداری 1400-1399 انجام شد. داده&#8204;ها و اطلاعات تحقیق به روش پیمایشی و از طریق پرسشنامه از 10 تعاونی صید پره نمونه مستقر در ساحل شرقی (صیدگاه گمیشان) و ساحل غربی (صیدگاه میانکاله) جمع&#8204;آوری شد. 16 تعاونی صید پره فعال، تعداد ۴۱۶ فرصت&#8204; شغلی ثابت را ثبت کردند که میانگین موقعیت شغلی به ازاء هر تعاونی10&#177;26 نفر محاسبه شد. تعداد کل افراد شاغل تعاونی&#8204;ها 587 نفر با میانگین (&#177; انحراف معیار) 13&#177;37 نفر به ازاء هر تعاونی به&#8204;دست آمد. میانگین ساعات کاری سالانه پرسنل شاغل در کل ساحل و ساحل غربی به&#8204;&#8204;ترتیب 23 و 37 درصد بیشتر از استاندارد کشوری و در ساحل شرقی 16 درصدکمتر بوده است. هزینه&#8204;های پرسنلی بیشترین سهم (۳/67 درصد) و هزینه&#8204;های تعمیر و نگهداری دومین رتبه را در بین هزینه&#8204;های متغیر نشان داد (۷/17 درصد). میانگین دستمزد ماهانه هر پرسنل شاغل در کل تعاونی&#8204;ها 1155876&#177;2526786 تومان برآورد شد که برای پرسنل شاغل در ساحل غربی (1291226&#177;2709892 تومان) 29 درصد بیشتر از پرسنل ساحل شرقی (786939 &#177;2099540 تومان) بود. برای رسیدن به نقطه سر به سر درآمدها، مقدار صید هر تعاونی باید ۵۶ برابر مقدارصید موجود افزایش یابد. میانگین سنی افراد شاغل 3/7&#177; 5/48 سال، میانگین تعداد خانوار هر پرسنل 42/0&#177;۴ نفر و سهم ماهیگیری پره در معیشت و درآمد افراد شاغل ۴۲ درصد تعیین شد. شاخص&#8204;&#8204;های اقتصادی نشان داد که ماهیگیری پره در حال حاضر فاقد سوددهی بوده است و ادامه فعالیت توجیه اقتصادی ندارد. کاهش تعداد اعضاء فعال تعاونی&#8204;های پره با هدف افزایش سهم دستمزد افراد شاغل و نوسازی تجهیزات صیادی به منظور کاهش هزینه&#8204;&#8204;های تعمیر و نگهداری برای افزایش عملکرد اقتصادی تعاونی&#8204;ها پیشنهاد می شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
Based on socio-economic studies, fishing is considered a complex activity worldwide, arising from the interrelation of different groups of fishermen, limited and valuable resources, and an increasing demand for supply in the consumer market (Pinello et al., 2017). The main objectives of socio-economic studies are to analyze the livelihoods of people directly involved in the fisheries, employment opportunities, profitability levels of the activity, and demographic patterns. Beach seine fishing, in the form of fishing cooperatives, is the only permitted fishing gear for bony fish in Iranian waters of the Caspian Sea during the six-month fishing season from mid-October to mid-April. Various studies have evaluated the social problems (Forouhesh Tehrani, 2013), economic conditions (Dad et al., 2013; Yazdani et al., 2017) of bony fish from beach seine fishing cooperatives. The beach seine fishery plays a crucial role in the livelihoods and income of local fishermen, and it also serves as a significant source of protein for coastal communities. However, there is a lack of comprehensive information on the socio-economic performance of the fishery. This study aimed to evaluate various socio-economic indicators of existing beach seine cooperatives in the Golestan province during the 2020-2021 fishing season, including employment, costs, remuneration, profitability, livelihood, and demographics. 
Methodology 
The socio-economic variables were collected through a sampling survey and by completing a questionnaire from the beach seine fishing cooperatives located on the West (Miankaleh) and East (Gomishan) coasts of Golestan province. The survey period spanned one calendar year, coinciding with the fishing season from October 6, 2020, to April 14, 2021. A stratified random sampling strategy based on ecological characteristics was designed (Pinello et al., 2017). Given that the total number of active beach seine fishing cooperatives was less than 50 (13 on the west coast and 3 on the east coast), 50% of the cooperatives were selected for sampling, i.e., 7 cooperatives from the West coast and all 3 cooperatives from the East coast. The questionnaires consisted of 76 separate variables, and the data were analyzed in 4 indicator groups: social, economic, socio-economic indicators, and demographic characteristics (Pinello et al., 2017). Indicators were derived from the questionnaire variables to evaluate the socio-economic status of beach seine cooperatives. 
Results 
The 16 beach seine fishing cooperatives provided a total of 416 employment opportunities, and the contribution of the West coast was 73.6% (306 jobs) and the East coast 26.4% (110 jobs). The average (&#177;SD) working hours per engaged crew based on national full-time equivalent were calculated as 1.23 &#177; 0.3 for the entire coastline and 1.37 &#177; 0.4 and 0.84 &#177; 0.1 for the west and east coasts, respectively. The variable costs along the coast were estimated at 14.4 billion Tomans in Iranian currency, of which personnel costs accounted for 67.3% (9.7 billion Tomans) and repair and maintenance costs, 17.7 % (2.54 billion Tomans). The average monthly remuneration per crew member engaged along the entire coastline was estimated at 2,526,786&#177;1,155,876 Tomans, and on the West and East coasts at 2,709,892&#177;1,291,226 and 2,099,540&#177;786,939, respectively. The economic profit for all the fishing cooperatives and cooperatives on the west and east coasts was negative. The average break-even revenues per cooperative for the entire and the West coast were calculated as 50.8 &#177; 2.3 and 2.8 &#177; 1.4 billion Tomans, respectively, but a negative number for the East coast. The catch to achieve the average break-even revenues would be 1,376,186 &#177; 81,934 kilograms per cooperative for the entire coast and 82,573 &#177; 56,589 kilograms for the Eest coast. The average age of the crew member was 48.5&#177;7.3 years, and the average number of households per crew was 4&#177;0.42. The share of beach seine fishing activities in the household income was 42 %.
&#160;Discussion and conclusion 
The beach seine fishing cooperatives on the West coast create employment opportunities 2.8 times greater than the East coast. The national full-time equivalent working hours indicated that the crew engaged along the entire coast and the west coast work 23% and 37% higher than the national reference level, respectively, and 16% lower on the East coast. Personnel costs, i.e., remuneration, account for the largest share (67.3 %), and repair and maintenance costs ranked second (17.7 %) among the five variable cost indicators, which are consistent with the previous findings for the cooperatives along the Caspian Sea (Salehi et al., 2016). The negative economic profit of the cooperatives reveals that this fishing activity is not profitable. To reach the break-even revenues, the catch amount of each beach seine cooperative must increase 56 times greater than the current catch, that is, it must increase from the current 24.6 &#177;11.3 tons to 1,376.1&#177;81.9 tons per cooperative. The members of the fishing cooperatives are mainly middle-aged people with an average age of 48.5&#177;7.3 years, which is very similar to the average age of fishermen for Kilka fisheries in the Caspian Sea (47.7 years) (Taghavimotlagh et al., 2020). Reducing the number of active members of the beach seine cooperatives and renovating the fishing equipment is proposed to increase the economic performance of the cooperatives.
Conflict of Interest
The authors declare that there are no conflicts of interest.
Acknowledgment
We want to express our gratitude to the Iranian Fisheries Research Sciences Institute for their cooperation and financial support. This study is part of project No. 3-77-1230-043-000628.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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			<PAGE>
			<FPAGE>43</FPAGE>
			<TPAGE>53</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/02/112025/07/72025/02/202025/04/22
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/2/2
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/08/12025/08/12025/08/12025/08/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/5/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سیدعباس</Name>
				<MidName></MidName>
				<Family>حسینی</Family>
				<NameE>Abbas</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hosseini</FamilyE>
				<Organizations>
				<Organization>موسسه تحقیقات علوم شیلاتی کشور</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>ab_hossaini@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نور محمد</Name>
				<MidName></MidName>
				<Family>آبیار</Family>
				<NameE>N.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Abyar</FamilyE>
				<Organizations>
				<Organization>مرکز تحقیقات و آموزش کشاورزی و منابع طبیعی استان گلستان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>abyarnm@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سیدامین الله</Name>
				<MidName></MidName>
				<Family>تقوی مطلق</Family>
				<NameE>S.A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Taghavimotlagh</FamilyE>
				<Organizations>
				<Organization>مؤسسه تحقیقات علوم شیلاتی کشور</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>s_taghavimotlagh@hotmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>غلامرضا</Name>
				<MidName></MidName>
				<Family>دریانبرد</Family>
				<NameE>G.R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Daryanabard</FamilyE>
				<Organizations>
				<Organization>موسسه تحقیقات علوم شیلاتی کشور</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>daryanabard@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>لاریجانی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Larijani</FamilyE>
				<Organizations>
				<Organization>موسسه تحقیقات علوم شیلاتی کشور</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mohamadlarijani@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محسن</Name>
				<MidName></MidName>
				<Family>یحیایی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Yahyaei</FamilyE>
				<Organizations>
				<Organization>اداره کل شیلات استان گلستان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mohsenyahyaei45@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رضا</Name>
				<MidName></MidName>
				<Family>شیرازی</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shirazi</FamilyE>
				<Organizations>
				<Organization>اداره کل شیلات استان گلستان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>shirazi1351@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Beach seine cooperative</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Bony fish</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Golestan province</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>remuneration</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>livelihood</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تعاونی پره</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماهیان استخوانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استان گلستان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>دستمزد</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>معیشت</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Dad, S., Ghorbani, R., Darijani, A., Yulghi, S. and Yahyaee, M., 2013. A survey of profitability and performance of fish beach seine Cooperative Companies in Golestan Province, 2009-2010. Journal of Utilization and Cultivation of Aquatics. Vol. 2(1), 27-40. (in Persian) ##FAO, 2005. Supporting small-scale fisheries through an enabling environment. Committee on Fisheries, Rome, Italy, 7-11 March 2005, COFI/2005/5.##Forouhesh Tehrani, G., 2012. Social Problems of Seine Fishermen and Affecting Factors. Journal of Village and Development. 15(4), 155-178 (in Persian)##General Directorate of Cooperatives, Labor and Social Welfare, 2020a.  https://kordestan.mcls.gov.ir/icm_content/media/image/2020/04/386984_orig.pdf (in Persian) ##General Directorate of Cooperatives, Labor and Social Welfare, 2020b. https://kordestan.mcls.gov.ir/icm_content/media/image/2020/04/386172_orig.pdf (in Persian) ##International Labor Organization. 1996. ##https://www.ilo.org/dyn/normlex/en/f?p=NORMLEXPUB:12100:0::NO::P12100_ILO_CODE:C180##Robles, R. ed., 1999. Review of Mediterranean Fisheries Situation and Management, Informes y estudios COPEMED, n. 1.##Onlus, I., 2006. Evaluation of the capital value, investments, and capital costs in the fisheries sector. No FISH/2005/03. 203 p. ##Pinello, D., Gee, J. and Dimech, M., 2017. Handbook for fisheries socio-economic sample survey–principles and practice. FAO Fisheries and Aquaculture Technical Paper No. 613. Rome, FAO. 118 pp.##Salehi, H., 2016., The current economic status of Fisheries (Fishery and Aquaculture) in Guilan, Mazandaran, and Golestan provinces. Iranian Fisheries Science Research Institute, Tehran. 168 P. (In Persian)##Salarpouri, A., 2022. A study on the effects of the COVID-19 pandemic on fisheries activities in the Caspian Sea, Persian Gulf, and Oman Sea. Iranian Fisheries Science Research Institute, Tehran. 91 P. (In Persian)##Statistical Yearbook of Iranian Fisheries Organization, 2024, Planning and Development Office of the Iranian Fisheries Organization, 64 p. (In Persian)##Taghavimotlagh, S. A., Daryanabard, G.R. and Gee, J., 2020. Socio-economic analysis of kilka fisheries in the southern waters of the Caspian Sea (Iranian waters). Iranian Journal of Fisheries Sciences. 20 (2), 430-448. DOI: 10.22092/ijfs.2021.350934.0.##Taghavimotlagh, S.A., Daryanabard, G.R., and Vahabnejad, A., 2021. Socio-economic analysis of shrimp fishing vessels in Bushehr province and determining the role of this fishery in creating employment and income in 2018. Journal of Fisheries Science and Technology, 10(2):105-117. (In Persian)##Yazdani, S., Riahi, A. and Peykani, G., 2017. The Economic Analysis of Pareh-Cooperatives in the Mazandaran Province. Iranian Journal of Agricultural Economics and Development Research. 48(2), 211-226. (in Persian).## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ تأثیر افزودن تائورین به جیره حاوی پودر چربی بر شاخص‌های خونی، ایمنی، آنزیم‌‌های آنتی‌اکسیدانی و کبدی قزل‌آلای رنگین‌کمان
 (Oncorhynchus mykiss)</TitleF>
		<TitleE>Effects of taurine supplementation in diet containing fat powder on hematological, immunological parameters antioxidant and hepatic enzymes in rainbow trout (Oncorhynchus mykiss)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>در مطالعه حاضر، تأثیر اسید آمینه تائورین بر شاخص&#8204;های خونی، ایمنی، آنزیم&#8204;های آنتی&#8204;اکسیدانی و کبدی در ماهی قزل&#8204;آلای رنگین&#8204;کمان (Oncorhynchus mykiss) تغذیه شده با جیره حاوی پودر چربی مورد بررسی قرار گرفت. جیره&#8204;های آزمایشی شامل کنترل مثبت (حاوی روغن ماهی و روغن کانولا)، کنترل منفی (پودر چربی و بدون تائورین) و جیره&#8204;های مبتنی بر پودر چربی حاوی 5/0، 1 و 2 درصد تائورین بودند. 225 عدد قزل&#8204;&#8204;آلای رنگین&#8204;&#8204;کمان با میانگین وزنی اولیه 03/0&#177;00/12 گرم، به مدت 58 روز، روزانه سه بار در حد سیری با جیره&#8204;های آزمایشی تغذیه شدند. نتایج نشان داد، اختلاف معنی&#8204;&#8204;&#8204;داری در هموگلوبین بین تیمارهای مختلف آزمایشی مشاهده نگردید (05/0&#60;p) درحالی&#8204;که گلبول سفید و قرمز با افزودن 2 درصد تائورین بیشترین مقدار را نشان داد (05/0p&#60;). هماتوکریت و متوسط حجم گلبول قرمز در جیره تائورین 1 درصد و اما متوسط هموگلوبین در گلبول قرمز در جیره کنترل منفی و متوسط غلظت هموگلوبین در گلبول قرمز در جیره تائورین 5/0 درصد در بالاترین سطح قرار داشت (05/0&#62;p). علاوه&#8204;براین، افزودن تائورین 2 درصد به جیره منجر به افزایش غلظت کلسترول، تری&#8204;گلیسرید، پروتئین تام و گلوکز گردید. مقادیر آسپارتات آمینوترانسفراز و آلانین آمینوترنسفراز با افزودن 2 درصد تائورین به جیره حاوی پودر چربی به طور معنی&#8204;داری کاهش یافت (05/0&#62;p). همچنین فعالیت آنزیم&#8204;های کاتالاز و سوپر اکسید دیسموتاز در تیمار حاوی 2 درصد تائورین و فعالیت آنزیم گلوتاتیون پراکسیداز در تیمارهای 1 و 2 درصد تائورین ارتقاء یافت و بالاترین فعالیت مالون &#8204;دی&#8204;آلدهید مربوط به جیره کنترل منفی بود (05/0p&#60;). به&#8204;علاوه، با افزودن 2 درصد تائورین فراسنجه&#8204;های ایمنی (ایمنوگلوبین، کمپلمان و لیزوزیم) بهبود یافتند. بر اساس یافته&#8204;های مطالعه حاضر، افزودن تائورین 2 درصد به منظور بهبود شاخص&#8204;&#8204;های خونی، بیوشیمیایی، فعالیت آنتی&#8204;&#8204;اکسیدانی و ایمنی در قزل&#8204;&#8204;آلای رنگین&#8204;&#8204;کمان تغذیه&#8204;&#8204;شده با جیره مبتنی بر 70 درصد پودر چربی پیشنهاد می&#8204;گردد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
Rainbow trout (Oncorhynchus mykiss) is one of the most important cultured species because of its high adaptability to various environmental conditions, rapid growth in intensive farming systems, and habituation to commercial aquafeeds (Parchami et al., 2022). Fish oil had been a main raw ingredient in aquafeeds for a long time; however, its availability has become increasingly limited (Gasco et al., 2018). In Iran, fat powder, a by-product of oil extraction, has potential for mass production. Nevertheless, the incorporation of fat powder into fish diets may adversely affect fish health due to the presence of saturated fatty acids, low digestibility, and associated side effects (Keramat&#160; Amirkolaie et al., 2014; Adhami and Keramat Amirkolaie, 2016). The complete or partial replacement of fish oil with these saturated oils can negatively impact lipid lipolysis and immune function (Abedian Kenari et al., 2010; Adhami and Keramat Amirkolaie, 2016). Furthermore, diets high in unsaturated fatty acids are associated with increased lipid peroxidation in mitochondria, leading to liver cell damage (Abedian Kenari et al., 2011). Taurine plays a crucial role in fish physiology, including bile acid conjugation, immune regulation, osmoregulation, antioxidant effects, and the development and regeneration of the nervous system (Salze and Davis, 2015; Xu et al., 2020). It also regulates liver oxidative status (Martins et al., 2019), aids in detoxification, and stimulates immune responses in bony fish (Cheng et al., 2018; Dehghani et al., 2020). Recognized as a potent antioxidant, taurine mitigates oxidative stress by acting as a non-specific scavenger of harmful reactive oxygen species, thus protecting cells from oxidative damage and enhancing the synthesis of antioxidant enzymes (Hosseini et al., 2017). This research aims to evaluate the potential of taurine as a valuable additive in aquaculture feed. The current study is designed to assess the effects of taurine on blood indices, immune system function, antioxidant enzyme activity, and liver function in rainbow trout (O. mykiss) fed with a diet containing fat powder.
Methodology
A total of 225 rainbow trout with an average initial weight of 12.00&#177;0.03 g was randomly assigned to 15 tanks, each containing 150 liters of water for 58 days. Five experimental diets were formulated: a fish oil and canola oil-based diet (positive control), fat powder-based diet (approximately 70% of the fat source was derived from fat powder) supplemented with 0% (negative control), 0.5%, 1%, and 2% taurine. The fish were fed three times daily at 8:00, 12:00, and 18:00 until apparent satiation. At the end of the trial, blood samples were taken from the caudal fin of each fish. The samples were allowed to clot and were subsequently centrifuged at 4600 rpm for 10 minutes to obtain serum. Hematological parameters, including red blood cell (RBC) and white blood cell (WBC) counts, hemoglobin concentration, and hematocrit levels, were measured. Additionally, serum biochemical parameters including cholesterol, triglycerides, total protein, glucose, albumin were determined. Hepatic enzyme (aspartate aminotransferase (AST) and alanine aminotransferase (ALT)), antioxidant indices (superoxide dismutase (SOD), glutathione peroxidase (GPx), catalase (CAT) and malondialdehyde (MDA)), and immune indices (complement, lysozyme and immunoglobulin) were also assessed to evaluate the health status of fish fed diet containing taurine and fat powder.
Results
According to the results, the fish fed with 2% taurine indicated the highest levels of WBC and RBC (p&#60;0.05). The highest values of hematocrit and MCV were obtained in fish fed 1% taurine (P&#60;0.05). MCH and MCHC amounts elevated in the negative control group and at the 0.5% taurine dietary level, respectively (p&#60;0.05). In contrast, the concentrations of hemoglobin were not significantly affected by the experimental diets (p&#62;0.05). The serum biochemical parameters showed that the inclusion of 2% taurine led to the highest levels of cholesterol, triglycerides, total protein, and glucose; However, the albumin content remained unaffected (p&#62;0.05). The concentration of triglyceride reduced with the addition of 0.5% taurine to the diet, while the lowest levels of cholesterol and glucose were found in the negative control group (p&#60;0.05). The highest concentration of total protein was observed with the supplementation of 2% taurine (p&#60;0.05). Furthermore, the activities of AST and ALT in negative control were significantly higher than those of fish fed 2% taurine (p&#60;0.05). Antioxidant indices demonstrated significant differences in SOD, GPx, CAT, and MDA among the experimental groups (P&#60;0.05). The highest levels of SOD and GPx were obtained by inclusion of 1.5% and 2% taurine, while the lowest amounts were observed in the negative control (p&#60;0.05). Immunological parameter indicated that the addition of 2% taurine to diet containing fat powder resulted in an improvement of immunoglobulin, ACH50 and Lysozyme compared to the negative control (p&#60;0.05).

Discussion and conclusion
The results of the current study suggest that reduced damage to the blood cells of fish fed a diet supplemented with 2% taurine may lead to an increase in hematocrit, RBC and WBC counts. Previous research indicates that taurine deficiency can contribute to blood cell destruction (Takagi et al., 2006, 2011). Furthermore, taurine plays a crucial role in synthesizing bile acids from cholesterol, which may reduce the need for bile acids and promote greater cholesterol reabsorption. This implies a decrease in hepatic absorption for bile acid synthesis in fish fed with 2% taurine, consistent with findings in rosy barb fish (Pethia conchonius), which taurine significantly increased triglyceride and cholesterol levels (Nejatizadegan et al., 2020). Taurine also interacts synergistically with insulin and insulin-like substances to enhance glucose and amino acid uptake in fish cells (Michelato et al., 2018). Additionally, taurine actively participates in glucose metabolism (Ba&#241;uelos-Vargas et al., 2014). The reduction in ALT and AST levels indicates that there are no adverse effects when taurine added to diet containing fat powder, aligning with similar findings reported in common carp (Cyprinus carpio L.) (Liu et al., 2024). At the same time, the improvement in antioxidant capacity and reduction in fat oxidation demonstrate the protective effects of taurine. In Asian swamp eel (Monopterus albus), the addition of 0.2% taurine to oxidized fish oil was shown to increase antioxidant enzyme activities (SOD, GPx, CAT) while reducing MDA levels (Zhang et al., 2022). The enhancement of immune indices, including ACH50, Lysozyme, and immunoglobulin levels, underscores the importance of taurine in maintaining immune function. Conversely, taurine deficiency has been shown to disrupt immune function (Schuller-Levis et al., 1990). In conclusion, the addition of 2% taurine positively affects bile salt production, fat digestion, and overall fat metabolism. It mitigates the negative effects of fat powder on liver function while improving blood parameters, immune function, and antioxidant activity.
Conflict of interest
There is no conflict of interest between authors.
Acknowledgment
This research was carried out with the assistance of the members of the Fisheries Department at Sari Agricultural Sciences and Natural Resources University, who provided laboratory and workshop facilities for this experiment. We would also like to thank the esteemed management of the Livestock and Aquatic Feed Company for their sincere cooperation in providing the raw materials for the fish diet. Special thanks to the esteemed manager of Kimia Growth Industry for supplying the fat powder.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>55</FPAGE>
			<TPAGE>67</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/02/112025/07/72025/02/202025/04/222025/03/18
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/12/28
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/08/12025/08/12025/08/12025/08/12025/08/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/5/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فاطمه</Name>
				<MidName></MidName>
				<Family>نوروزی</Family>
				<NameE>Fatemeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>norouzi</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>fatemenorouzi1999@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سکینه</Name>
				<MidName></MidName>
				<Family>یگانه</Family>
				<NameE>Sakineh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Yeganeh</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>s.yeganeh@sanru.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فرید</Name>
				<MidName></MidName>
				<Family>فیروزبخش</Family>
				<NameE>Farid</NameE>
				<MidNameE></MidNameE>
				<FamilyE>firouzbakhsh</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>f.firouzbakhsh@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بتول</Name>
				<MidName></MidName>
				<Family>ادهمی</Family>
				<NameE>Batoul</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Adhami</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>amine.adhami@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Sustainable aquaculture</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>amino acid</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>substitution</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fish oil</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>immune system</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آبزی‌‌پروری پایدار</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اسید ‌آمینه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جایگزینی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>روغن ماهی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سیستم ایمنی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Abedian Kenari, A., Mozanzadeh, M.T. and Pourgholam, R., 2010. Effects of total fish oil replacement to vegetable oils at two dietary lipid levels on the growth, body composition, haemato immunological and serum biochemical parameters in Caspian brown trout (Salmo trutta caspius Kessler, 1877). Aquaculture Research, 42(8):1131-1144. Doi:10.1111/j.1365-2109.2010.02701.x##Abedian Kenari, A., Mozanzadeh, M.T. and Pourgholam, R., 2011. Effects of total fish oil replacement to vegetable oils at two dietary lipid levels on the growth, body composition, haemato-immunological and serum biochemical parameters in Caspian brown trout (Salmo trutta caspius Kessler, 1877). Aquaculture Research, 42(8): 1131–1144. Doi:10.1111/j.1365-2109.2010.02701.x##Adeniyi, T.T., Ajayi, G.O., Akinsanya, M.A. and Jaiyeola, T.M., 2010. Biochemical changes induced in rats by aqueous and ethanolic corm extracts of Zygotritonia croceae. Scientific Research and Essays, 5(1):071-076.##Amar, E.C., Kiron, V., Satoh, S., Okamoto, N. and Watanab, E.T., 2000. Effect of dietary betacarotene on the immune response of rainbow trout (Oncorhynchus mykiss). Fisheries Science, 66:1068-1075. Doi:10.1046/j.1444-2906.2000.00170.x##Adhami, B. and Amirkolaie, AK., 2016. Effect of different levels of phospholipid on growth performance, fat digestibility and lipase activity in diet containing fat powder in rainbow trout (Onchorhyncus mykiss). Journal of Fisheries, 69(3): 275-283. Doi:10.22059/jfisheries.2016.61604##Adhami, B., Karamat, A., Orji, H., Kazemifard, M., Mahjoob, S., 2021. Effect of lysophospholipid on growth performance, blood parameters, liver enzymes, and lysozyme activity of rainbow trout (Oncorhynchus mykiss) fed a diet containing fat powder. Fisheries Science and Technology, 10: 272-285. doi: 20.1001.1.23225513.1400.10.3.4.8##Amirkolaie, A.K., Shahkolaie, M.D., Karimzadeh, S. and Khalesi, M., 2014. The potential of soya oil industry products as oil alternatives in rainbow trout (Oncorhynchus mykiss) diet. Aquaculture International, 22:1093-1103. Doi:10.1007/s10499-013-9730-x##Baluchnejad mojarad, T., Roghani, M. and Mafakheri, M., 2010. Neuroprotective effect of silymarin in 6-hydroxydopamine hemi-parkinsonian rat: involvement of estrogen receptors and oxidative stress. Neuroscience letter, 480:206-210. Doi:10.1016/j.neulet.2010.06.038##Bahrekazemi, M., Eslami, M. and Nikbakhsh, J., 2020. The effect of dietary coriander supplementation on growth performance, biochemical responses, carcass proximate composition, and heavy metal accumulation in beluga, (Huso huso). Journal of Applied Aquaculture, 34(1):1-20. Doi:10.1080/10454438.2020.1782798##Bahrkazmi and Islami, 2022. The effect of taurine on growth and feeding efficiency, digestive enzymes and immunity of elephant fish (Huso huso) in low water temperature. Fisheries, 75(1):49-62. Doi:10.22059/jfisheries.2021.329862.1279##Bañuelos-vargas, I., López, L. M., Pérez-jiménez, A. and Peres, H., 2014. Effect of fishmeal replacement by soy protein concentrate with taurine supplementation on hepatic intermediary metabolism and antioxidant status of totoaba juveniles (Totoaba macdonaldi). Comparative Biochemistry and Physiology, Part B, 170:18-25. Doi:10.1016/j.cbpb.2014.01.003##Bavi, Z., Zakeri, M., Mousavi, S.M. and Yavari, V., 2022. Effects of Dietary Taurine on Growth, Body Composition, Blood Parameters, and Enzyme Activities of Juvenile Sterlet (Acipenser ruthenus). Aquaculture Nutrition, 2022(1):1713687. Doi:10.1155/2022/1713687##Boesen, J., Maganga, F.P. and Odgard, R., 1999. Norms, organizations and actual practices in relation to land and water management in Ruaha River Basin, Tanzania. In: Granfelt, T. (ed) Managing the Globalized Environment. Intermediate Technology Publlications, London. pp 88-113.##Bouckenooghe, T., Remacle, C. and Reusens, B., 2006. Is taurine a functional nutrient? Current Opinion in Clinical Nutrition and Metabolic Care, 9(6):728-733. DOI:10.1097/01.mco.0000247469. 26414.55.##Cheng, C.H., Guo, Z.X. and Wang, A.L., 2018. The protective effects of taurine on oxidative stress, cytoplasmic free-Ca2+ and apoptosis of pufferfish (Takifugu obscurus) under low temperature stress. Fish and Shellfish Immunology, 77:457-464. DOI:10.1016/j.fsi.2018.04.022##Clerton, P., Troutaud, D., Verlha, V., Gabraudan, J. and Deschaux, P., 2001. Dietary vitamin E and rainbow trout (Oncorhynchus mykiss) phagocyte functions: effect on gut and on head kidney leucocytes. Fish and Shellfish Immunology, 11:1-13. DOI:10.1006/fsim.2000.0287##Claiborne, A., 1985. Catalase activity. In: Greenwald, R.A. (ed) Handbook of Methods for Oxygen Free Radical Research. 1st ed. CRC Press, Boca Raton, Florida, USA. pp 283–284.##Dong J., Cheng R., and Yang Y., 2018. Effects of Dietary Taurine on Growth, Non-Specific Immunity, Anti-Oxidative Properties and Gut Immunity in the Chinese Mitten Crab (Eriocheir sinensis). Fish &#38; Shellfish Immunology. 82:212–219, Doi:10.1016/j.fsi.2018.08.029, 2-s2.0-85051756863##Dehghani, R., Oujifard, A., Mozanzadeh, M.T., Morshedi, V. and Bagheri, D., 2020. Effects of dietary taurine on growth performance, antioxidant status, digestive enzyme activities and skin mucosal immune responses in yellowfin seabream, Acanthopagrus latus. Aquaculture, 517:734795. DOI:10.1016/j. aquaculture.2019.734795##Drobkin, D.R., 1945. Crystallographic and optical properties of human hemoglobin: proposal for standardization of hemoglobin. American Journal of Medicine Science, 209:268-270. DOI:10.2331/ fishsci.62.938##Gasco, L., Gai, F., Maricchiolo, G., Genovese, L., Ragonese, S., Bottari, T., Caruso, G., Gasco, L., Gai, F., Maricchiolo, G. and Genovese, L., 2018. Sustainable alternatives for dietary fish oil in aquafeeds: actual situation and future perspectives. Feeds for the Aquaculture Sector: Current Situation and Alternative Sources, pp 49-61.##Gesto, M., Madsen, L., Andersen, NR., El Kertaoui, N., Kestemont, P., Jokumsen, A., and Lund, I. 2021. Early performance, stress- and disease-sensitivity in rainbow trout fry (Onchorhyncus mykiss) after total dietary replacement of fish oil with rapeseed oil. Effects of EPA and DHA supplementation. Aquaculture, 536: 736446. DOI: 10.1016/j.aquaculture.2021.736446##Güroy, D., Karadal, O., Güroy, B., Emre, Y., Emre, N., Eraslan, D., Yallm, F., Mantoǧlu, S. and Demir, A., 2024. Dietary taurine improves the growth performance, health status and liver histopathology of meagre (Argyrosomus regius) fed a reduced fish meal diet. Annals of Animal Science, 24(3). DOI: 10.2478/aoas-2024-0011##Gunathilaka, G.L.B.E., Kim, M.G., Lee, C.h., Shin, J., Lee, B.J. and Lee, K.J., 2019. Effects of taurine supplementation in low fish meal diets for red seabream (Pagrus major) in low water temperature season. Fisheries and Aquatic Science, 22:23-33. DOI: 10.1186/s41240-019-0138-z##Hayyan, M., Hashim, M.A. and inashef, I.M., 2016. Superoxide ion: generation and chemical implications. Chemical Review, 116:3029-3085. DOI:10.1021/acs.chemrev.5b004070##Huang, M., Yang, X., Zhou, Y., Ge, J., Davis, D.A., Dong, Y., Gao, Q. and Dong, S., 2021. Growth, serum biochemical parameters, salinity tolerance and antioxidant enzyme activity of rainbow trout (Onchorhyncus mykiss) in response to dietary taurine levels. Marine Life Science and Technology, 1-14. DOI:10.1007/s42995-020-00088-2##Hoston, A.H., 1990. Blood and circulation. In: Shreck, C.B. and Moyle, P.B. (eds) Methods in Fish Biology. American Fisheries Society, Bethesda, Maryland. pp 273-335.##Lawrence, R.A. and Burk, R.F., 1976. Gluthatione peroxidase activity in selenium deficiency rat liver. Biochemical and Biophysics Research Communications, 71:952-958. DOI:10.1016/0006-291X(76)90747-6##Li, M., Lai, H., Li, Q., Gong, S. and Wang, R., 2016. Effects of dietary taurine on growth, immunity and hyperammonemia in juvenile yellow catfish, (Pelteobagrus fulvidraco) fed all-plant protein diets. Aquaculture, 450:349-355. DOI:10.1016/j.aquaculture.2015.08.013##Lim, S.J., Oh, D.H., Khosravi, S., Cha, J.H., Park, S.H., Kim, K.W., Lee, K.J., 2013. Taurine is an essential nutrient for juvenile parrot fish Oplegnathus fasciatus. Aquaculture, 414: 274–279. DOI:10.1016/j.aquaculture.2013.08.013##Liu, D., Mi, J., Yan, X., Qin, C., Wang, J. and Nie, G., 2024. Taurine Alleviated the Negative Effects of an Oxidized Lipid Diet on Growth Performance, Antioxidant Properties, and Muscle Quality of the Common Carp (Cyprinus carpio L.).  Aquaculture Nutrition, 5205506. DOI: 10.1155/2024/5205506##Martins, N., Magalhaes, R., Castro, C., Couto, A., Díaz, P., Aires, R. and Teles, O., 2019. Taurine modulates hepatic oxidative status and gut inflammatory markers of European seabass (Dicentrarchus labrax) fed plant feeds tuffs based diets. Amino acids, 51(9):1307-1321. DOI:10.1007/s00726-019-02769-4##Magalhães, R., Martins, N., Martins, S., Lopes, T., Díaz-Rosales, P., Pousão-Ferreira, P., Oliva-Teles, A. and Peres, H., 2019. Is dietary taurine required for white seabream (Diplodus sargus) juveniles. Aquaculture, 502:296-302. DOI:10.1016/j.aquaculture.2018.12.019##Michelato, M., Furuya, W.M., Gatlin, D.M., 2018. Metabolic responses of Nile tilapia Oreochromis niloticus to methionine and taurine supplementation. Aquaculture, 485: 66–72. DOI: 10.1016/j.aquaculture.2017.11.003##Moss, D. and Henderson, A., 1999. Clinical enzymology. In: Burtis, C.A. and Ashwood, F.R. (eds) Tietz textbook of clinical chemisry. 3rd ed. WB Saunders Company, Philadelphia. 721 P.##Mozanzadeh, M.T., Bahabadi, M.N., Morshedi, V., Oujifard, A., Agh, N., Ghasemi, A., Maneii, K., Ebrahimi, H., Hamedi, S. and Tamadoni, R., 2024. Effects of Dietary Taurine on Maturation Indices, Antioxidant Capacity, Ovaries Amino and Fatty Acids Profile, and Vitellogenin Gene Transcription Level in Penaeus vannamei Female Brooders. Aquaculture Nutrition, 2024(1):5532545. DOI:10.1155/2024/5532545##Nejatizadegan, P., Hayarati, P., Darafshan, S. and Morshedi, S., 2020. The effects of different levels of amino acid taurine in the diet on the colorability of pink barb fish (Pethia conchonius). Aquatic Nutrition, 6(2):48-39. DOI:10.22124/janb.2021.16792.1091##Parchami, A., Kabootari, J., Mohabi, A. and Pouyapur, V., 2022. Effects of aqueous extract of Panax ginseng on histomorphometric characteristics of liver and some biochemical parameters of blood serum in rainbow trout (Oncorhynchus mykiss). Journal of Aquaculture Development, 16(4):37–49.##Peter, N., Pradhan, C., Dileep, N., Musharraf, M. and Thazhakot Vasunambisan, S., 2022. Dietary taurine improved growth performance, nutrient utilization, and antioxidant enzyme activities in pangasius (Pangasianodon hypophthalmus). Journal of the World Aquaculture Society, 53(1):106-121. DDOI:10.1111/jwas.12778##Hoseini, M., 2017. A Review on the Importance of Taurine in Aquaculture and Its Role in Fish Growth and Physiology. Journal of Aquatic Exploitation and Cultivation, 6(3):51-59. Doi: 10.22069/japu.2018.13422.1381.##Huxtable, R.J., 1992. Physiological actions of taurine, Physiological Reviews, 72(1):101-163. DOI:10. 1152/physrev.1992.72.1.101##Sadeghi, A., Pourmozaffar, S., Gozari, M., 2020. The Effect of LivorGol Medication on Growth Indices and Gonadal Development at Different Dietary Fat Levels in Goldfish (Carassius auratus). Animal Environment, 12(1): 323-330. ##Salze, G.P., Davis, D.A., 2015. Taurine: A critical nutrient for future fish feeds. Aquaculture, 437:215-229. DOI:10.1016/j.aquaculture.2014.12.006.##Salze, G.P., Spangler, E., Cobine, P.A., Rhodes, M., Davis, D.A. 2016. Investigation of biomarkers of early taurine deficiency in Florida pompano (Trachinotus carolinus). Aquaculture, 451: 254–265. DOI:10.1016/j.aquaculture.2015.09.019##Schuller-Levis, G., Mehta, P.D., Rudelli, R. and Sturman, J., 1990. Immunologic consequences of taurine deficiency in cats. Journal of Leukocyte Biolog, 47:321-331. DOI:10.1016/j.aquaculture.2014. 12.006##Shi, Y., Hu, Y., Wang, Z., Zhou, J., Zhang, J., Zhong, H., Fu, G. and Zhong, L., 2021. The protective effect of taurine on oxidized fish-oil-induced liver oxidative stress and intestinal barrier-function impairment in juvenile Ictalurus punctatus. Antioxidants, 10(11):1690. DOI:10.3390/antiox10111690##Siwicki, A.K., Anderson, D.P. and Rumsey, G.L., 1994. Dietary intake of immunostimulants by rainbow trout affects non-specific immunity and protects against furunculosis. Veterinary Immunology and Immunopathology, 41:125-139. DOI:10.1016/0165-2427(94)90062-0##Takagi, S., Murata, H., Goto, T., Ichiki, T., Endo, M., Hatate, H., Yoshida, T., Sakai, T.,Yamashita, H. and Ukawa, M., 2006. Efficacy of taurine supplementation for preventing green liver syndrome and improving growth performance in yearling red [sea bream (Pagrus major) fed low-fishmeal diet]. Fisheries Science, 72(6):1191-1199. Doi:10.1111/j.1444-2906.2006.01276.x##Takagi, S., Murata, H., Goto, T., Hatate, H., Endo, M., Yamashita, H., Miyatake, H. and Ukawa, M., 2011. Role of taurine deficiency in inducing green liver symptom and effect of dietary taurine supplementation in improving growth in juvenile red sea bream (Pagrus major) fed non-fishmeal diets based on soy protein concentrate. Fisheries Science, 77(2):235-244. DOI:10.1007/s12562-011-0322-2##Wang, X., He, G., Mai, K., Xu, W. and Zhou, H., 2016. Differential regulation of taurine biosynthesis in rainbow trout and Japanese flounder. Scientific Reports, 6:21231. DOI:10.1038/srep21231##Winterbourn, C.C., Hawkins, R.E., Brian, M. and Carrell, R.W., 1975. The estimation of red cell superoxide dismutase activity. The Journal of Laboratory and Clinical Medicine, 85(2):337-341.##Xu, H., Zhang, Q., Kim, S.K., Liao, Z., Wei, Y., Sun, B., Jia, L., Chi, S. and Liang, M., 2020. Dietary taurine stimulates the hepatic biosynthesis of both bile acids and cholesterol in the marine teleost, tiger puffer (Takifugu rubripes). British Journal of Nutrition, 123:1345-1356. DOI:10.1017/S0007114520000161##Zhang, J., Che, C., Cai, M. and Hu, Y., 2022. Taurine improves health of juvenile rice field eel (Monopterus albus) fed with oxidized fish oil: Involvement of lipid metabolism, antioxidant capacity, inflammatory response. Aquaculture Reports, 27,101388. DOI:10.1016/j.aqrep.2022.101388##Zhang, M., Qin, C., Sun, Z., Jiang, H., Wang, Z., Lin, Y. and Li, M., 2024. Taurine can play a positive role in growth, liver health and resistance to Aeromonas hydrophila of yellow catfish (Pelteobagrus fulvidraco) exposed to ammonia stress for a long time. Aquaculture Reports, 38:102347. DOI:10.1016/j.aqrep.2024.102347## ##</REF>
			</REFRENCE>
		</REFRENCES>

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	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ پایش میکروبی منابع آب سطحی در حوضه آبریز سرشاخه‌های رودخانه سیروان (سنندج) طی سال‌های 1403-1402</TitleF>
		<TitleE>Microbial monitoring of surface water resources in the Sirvan River tributary catchment basin (Sanandaj) during 2023-2024</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>پایش میکروبی منابع آب سطحی به&#8204;ویژه در نواحی حساس مانند حوضه&#8204;های آبریز سدها، نقش حیاتی در حفظ سلامت عمومی و پایداری اکوسیستم&#8204;های آبی ایفاء می&#8204;کند. این مطالعه با هدف بررسی وضعیت آلودگی میکروبی در حوضه آبریز رودخانه سیروان در استان کردستان طی سال&#8204;های آبی 1403-1402 انجام شد. نمونه&#8204;برداری&#8204;ها به &#8204;صورت ماهانه و با رعایت شرایط استریل از شش ایستگاه منتخب شامل ایستگاه 1 (بالادست قشلاق، زیر پل)، ایستگاه 2 (شاخه قشلاق رود قبل از تصفیه خانه)، ایستگاه 3 (شاخه قشلاق رود، پایین دست تصفیه خانه)، ایستگاه 4 (شاخه قشلاق رود، حدود 3 کیلومتر پایین&#8204;تر از ایستگاه 2)، ایستگاه 5 (شاخه گاوه رود) و ایستگاه 6 (شاخه سیروان، پشت سد) انجام گرفت. شاخص&#8204;های میکروبی شامل شمارش کل باکتری&#8204;ها، کلیفرم&#8204;های کل، کلیفرم&#8204;های مدفوعی و &#160;Escherichia coliبا استفاده از محیط&#8204;های کشت پلیت کانت آگار و ECC کروم آگار مطابق با استاندارد APHA &#160;(2017) اندازه&#8204;گیری شدند. نتایج نشان داد که بار میکروبی در ایستگاه&#8204;ها تفاوت معنی&#8204;داری دارد (05/0p&#8804;) به&#8204;طوری&#8204;که ایستگاه ۴، واقع در پایین&#8204;دست تصفیه&#8204;خانه، دارای بیشترین میزان آلودگی بود و در ماه آبان غلظت کلیفرم&#8204;های کل تا ۷۰۰۰۰۰ واحد تشکیل&#8204;دهنده کلنی در 100 میلی&#8204;&#8204;لیتر ثبت شد. در مقابل، ایستگاه ۵ واقع در منطقه&#8204;ای با کمترین فعالیت انسانی، دارای کمترین بار میکروبی بود. تحلیل فصلی داده&#8204;ها نیز بیانگر افزایش قابل&#8204;ملاحظه شاخص&#8204;های آلودگی در فصل تابستان به&#8204;ویژه در ایستگاه&#8204;های مجاور فعالیت&#8204;های انسانی و کشاورزی بود. یافته&#8204;های این تحقیق نشان&#8204;دهنده نقش مؤثر فاضلاب&#8204;های انسانی، رواناب&#8204;های کشاورزی و ناکارآمدی سیستم&#8204;های تصفیه در کاهش کیفیت بهداشتی منابع آب سطحی منطقه است. با توجه به اهمیت رودخانه سیروان در تأمین آب شرب و کشاورزی استان کردستان، نتایج این مطالعه می&#8204;تواند مبنایی برای شناسایی نقاط بحرانی، اصلاح زیرساخت&#8204;های تصفیه و تدوین برنامه&#8204;های پایش و مدیریت مستمر کیفیت آب سطحی در سطح حوضه آبریز باشد.</CONTENT>
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			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
The Sirvan River is a vital freshwater source in Kurdistan Province, flowing through both urban and rural landscapes. Its proximity to human settlements, agricultural zones, and livestock operations increases the risk of contamination from untreated wastewater and surface runoff. Consequently, microbial monitoring of surface water within this watershed is essential for evaluating the region&#8217;s sanitary and environmental conditions. Microorganisms in aquatic ecosystems, beyond their ecological functions, are widely recognized as reliable indicators of water quality. Fluctuations in microbial populations often signal the presence of pollutants such as domestic sewage, animal waste, and nutrient compounds (Bradshaw et al., 2016). Among these indicators, coliform bacteria particularly fecal coliforms and Escherichia coli are of critical importance due to their intestinal origin and thermotolerance, making them precise markers of contamination from human and animal sources (Aenab and Singh, 2015). Numerous international studies have explored the factors influencing the presence and distribution of indicator bacteria in surface waters. For example, Pall et al. (2013) and Islam et al. (2017) examined the roles of temperature, precipitation, land use, and wastewater treatment efficiency in microbial load variation. Newton and McMahon (2011) investigated the relationship between organic and inorganic compounds and microbial community structure in lakes. At the watershed scale, Flood et al. (2022) highlighted the influence of geological and hydrological features on microbial contamination in rivers. Similarly, Park et al. (2021) demonstrated the impact of vegetation cover and land slope on bacterial distribution in South Korea. In Iran, several studies have addressed microbial water quality. Roshani-Sefidkouhi et al. (2025) assessed the Chahnimeh reservoirs in Sistan and Baluchestan Province, while Khatib Haghighi and Ghaani (2018) evaluated urban and rural drinking water sources in Gilan Province using total and fecal coliform indicators. However, most of these investigations were limited to cross-sectional designs or specific seasons. Comprehensive studies on spatial and seasonal variations of microbial indicators in Iranian rivers particularly the Sirvan River remain scarce. This study presents a year-long monitoring of microbial indicators, including total coliforms, fecal coliforms, and E. coli, across six stations in the Sirvan River watershed, covering a full hydrological cycle (July 2023 to June 2024). By analyzing seasonal and spatial trends and examining the influence of surrounding human activities, this research offers a novel approach to surface water quality assessment. The findings aim to identify pollution hotspots, evaluate sanitary conditions, and inform water quality management strategies for Kurdistan Province and similar regions.
Results
Microbial contamination in the Sirvan River watershed was assessed by quantifying total bacteria, total coliforms, fecal coliforms, and E. coli across multiple stations and seasons during 2023&#8211;2024. Maximum recorded values were 1&#215;10⁸ CFU/100 ml for total bacteria, 7&#215;10⁵ for total coliforms, 4.2&#215;10⁵ for fecal coliforms, and 3.7&#215;10⁵ for E. coli. The highest total bacterial count occurred at Station 2 in November 2023, while peak coliform and E. coli levels were observed at Station 4 in January 2024. Seasonal analysis revealed that bacterial concentrations peaked in summer (6.56 &#177; 0.32 log CFU/100 ml) and were lowest in winter (5.55 &#177; 0.87 log CFU/100 ml). Spatially, Station 3 consistently exhibited the highest bacterial load, while Station 2 had the lowest. Statistically significant differences were found between winter and other seasons (p&#8804;0.05), as well as among stations (p&#8804;0.05). Total coliforms followed a similar seasonal pattern, with highest mean counts in summer (4.87&#177;0.77 log CFU/100 ml), followed by autumn (4.27&#177;0.95), spring (3.86&#177;0.50), and winter (3.12&#177;1.91). Stations 3 and 4 were the most contaminated, while Stations 1 and 5 consistently showed the lowest levels. Seasonal variation in total coliforms was statistically significant (p&#8804;0.05), with summer values markedly higher than winter. Fecal coliforms also peaked in summer (3.23&#177;1.72 log CFU/100 ml) and were lowest in winter (2.72&#177;1.72). Station 4 recorded the highest levels, significantly differing from other stations (p&#8804;0.05), while Stations 1 and 5 had the lowest. However, seasonal differences in fecal coliforms were not statistically significant. E. coli concentrations were highest in summer (3.09&#177;1.58 log CFU/100 ml) and lowest in winter (2.97&#177;1.51). Stations 3 and 4 again showed the highest contamination, with statistically significant differences compared to other stations (p&#8804;0.05). Stations 1 and 5 did not show significant contamination levels. Seasonal variation in E. coli density was not statistically significant. Overall, the data revealed pronounced spatial heterogeneity in microbial contamination, with consistently elevated levels at Stations 3 and 4 areas characterized by intensive human and agricultural activity. Seasonal effects, particularly during summer and autumn, were major contributors to increased bacterial loads due to higher temperatures and runoff. These findings underscore the need for targeted pollution control measures in identified hotspots within the Sirvan River catchment.

Discussion and conclusion&#160; 

The elevated bacterial concentrations observed in downstream stations (2, 3, and 4) of the Sirvan River reflect the impact of human activities, including the discharge of untreated or partially treated sewage and agricultural runoff (Helmer and Hespanhol, 1997; Agarwal and Rajwar, 2010; Aenab and Singh, 2015). These conditions are exacerbated by warm water temperatures, reduced flow rates, increased evaporation, and higher pollutant loads factors consistent with microbial contamination patterns in similar ecosystems (Rusi&#241;ol et al., 2020; Rather et al., 2023; Al-Afify et al., 2023). The presence of E. coli in elevated concentrations is a clear indicator of fecal contamination and poses serious health risks to communities near the river. The findings highlight the inadequacy of existing wastewater treatment systems and the urgent need for infrastructure upgrades to mitigate pollution. Lower bacterial concentrations at upstream sites suggest the effectiveness of natural filtration by vegetation, topographical separation from pollution sources, and hydrological buffering (Yaghoubzadeh and Safari, 2016; Wang et al., 2022). This study reinforces the importance of regular microbial water quality monitoring in the Sirvan River watershed using robust indicators such as E. coli. Effective management requires prioritizing the identification and control of both point and non-point source pollution, especially during peak contamination seasons. Strategies should include improved wastewater treatment, public awareness campaigns, and ecological restoration of water bodies. Integrated watershed management, supported by collaboration among water, health, and environmental authorities, is essential for safeguarding water quality and public health.

Conflict of interest
The authors declare that they have no conflict of interest
Acknowledgment
We hereby sincerely thank the Caspian Sea Ecology Research Center and Iranian Fisheries Science Research Institute for providing the scientific and laboratory basis for this research.</CONTENT>
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			2025/02/112025/07/72025/02/202025/04/222025/03/182025/07/26
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/5/4
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/08/12025/08/12025/08/12025/08/12025/08/12025/08/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/5/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>زهرا</Name>
				<MidName></MidName>
				<Family>یعقوب زاده</Family>
				<NameE>zahra</NameE>
				<MidNameE></MidNameE>
				<FamilyE>yaghoubzadeh</FamilyE>
				<Organizations>
				<Organization>پژوهشکده اکولوژی دریای خزر، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، ساری، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>za_yaghoub@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فائزه</Name>
				<MidName></MidName>
				<Family>ترک پهنابی</Family>
				<NameE>Faezeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Turk Pahnabi</FamilyE>
				<Organizations>
				<Organization>پژوهشکده اکولوژی دریای خزر، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، ساری، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>pahnabifaezeh@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Microbial monitoring</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fecal coliform</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Escherichia coli</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Sirvan River</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>water quality</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پایش میکروبی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کلیفرم مدفوعی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Escherichia coli</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رودخانه سیروان</KeyText>
			</KEYWORD>

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

		<REFRENCES>
			<REFRENCE>
				<REF>Aenab, A.M. and Singh, S.K., 2015. Critical assessment of river water quality and wastewater treatment plant (WWTP). International Journal, 3(1), pp.405-411.##               https://www.researchgate.net/publication/271643514##Agarwal, A.K. and Rajwar, G.S., 2010. Physico-chemical and microbiological study of Tehri dam reservoir, Garhwal Himalaya, India. Journal of American science, 6(6), pp.65-71.##               https://www.researchgate.net/publication/287643511## ##Al-Afify, A.D., Abdo, M.H., Othman, A.A. and Abdel-Satar, A.M., 2023. Water quality and microbiological assessment of Burullus Lake and its surrounding drains. Water, Air, &#38; Soil Pollution, 234(6), p.385.  DOI:10.1007/s11270-023-06351-3##Alonso, J.L., Amoros, I., Chong, S. and Garelick, H., 1996. Quantitative determination of Escherichia coli in water using CHROMagar® E. coli. Journal of microbiological methods, 25(3), pp.309-315.  DOI:10.1016/0167-7012(96)00002-4##Alonso, J.L., Soriano, A., Carbajo, O., Amoros, I. and Garelick, H., 1999. Comparison and recovery of Escherichia coli and thermotolerant coliforms in water with a chromogenic medium incubated at 41 and 44.5 C. Applied and Environmental Microbiology, 65(8), pp.3746-3749. DOI:10.1128/AEM.65.8.3746-3749.1999##APHA (American Public Health Association), 2017. Standard method for examination of water and wastewater. American public health association publisher, 18thedition, Washington, USA.1113P.##Bradshaw, J.K., Snyder, B.J., Oladeinde, A., Spidle, D., Berrang, M.E., Meinersmann, R.J., Oakley, B., Sidle, R.C., Sullivan, K. and Molina, M., 2016. Characterizing relationships among fecal indicator bacteria, microbial source tracking markers, and associated waterborne pathogen occurrence in stream water and sediments in a mixed land use watershed. Water research, 101, pp.498-509.##Byappanahalli, M.N., Nevers, M.B., Korajkic, A., Staley, Z.R. and Harwood, V.J., 2012. Enterococci in the environment. Microbiology and Molecular Biology Reviews, 76(4), pp.685-706. DOI:10.1128/mmbr.00023-12##Pall, E., Niculae, M., Kiss, T., Şandru, C.D. and Spînu, M., 2013. Human impact on the microbiological water quality of the rivers. Journal of medical microbiology, 62(11), pp.1635-1640.##Corsi, S.R., De Cicco, L.A., Hansen, A.M., Lenaker, P.L., Bergamaschi, B.A., Pellerin, B.A., Dila, D.K., Bootsma, M.J., Spencer, S.K., Borchardt, M.A. and McLellan, S.L., 2021. Optical properties of water for prediction of wastewater contamination, human-associated bacteria, and fecal indicator bacteria in surface water at three watershed scales. Environmental Science &#38; Technology, 55(20), pp.13770-13782.##             DOI: 10.1021/acs.est.1c02644##Dagher, L.A., Hassan, J., Kharroubi, S., Jaafar, H. and Kassem, I.I., 2021. Nationwide assessment of water quality in rivers across Lebanon by quantifying fecal indicators densities and profiling antibiotic resistance of Escherichia coli. Antibiotics, 10(7), p.883.##             DOI:10.3390/antibiotics10070883 ##Dimpor, J.J., Lucky, O.P., Kwarkye, D.F., Watts, S., Oguayo, C.P., Ojewole, C.O. and Kusi, J., 2025. Identifying spatiotemporal patterns and drivers of fecal indicator bacteria in an urban lake for water quality assessment and management. Heliyon, 11(1).##Faeeid, M. Babaei, H. Abedini, A., 2015. Investigation of microbial and physicochemical parameters in Anzali Wetland. Quarterly Scientific Research Journal of Wetland Ecobiology , Islamic Azad University, Ahvaz Branch, 7 (3):45-54. (In Persian)##Gao, N., Liang, Y., Li, J., Cui, K. and Lu, W., 2022. Bacterial community composition and indicators of water quality in Caizi Lake, a typical Yangtze-connected freshwater lake. FEMS Microbiology Letters, 369(1), p.fnac084.  DOI:10.1093/femsle/fnac084##Health Canada. Guidelines for Canadian Drinking Water Quality – Technical Document: Total Coliforms. 2022. https://www.canada.ca/en/health-canada/services/publications/healthy-living/guidelines-canadian-drinking-water-quality-guideline-technical-document-total-coliforms.html##Helmer, R. and Hespanhol, I., 1997. Water pollution control: a guide to the use of water quality management principles. CRC Press.##Islam, M.M., Iqbal, M.S., D'Souza, N. and Islam, M.A., 2021. A review on present and future microbial surface water quality worldwide. Environmental Nanotechnology, Monitoring &#38; Management, 16, p.100523.##Islam, M.S., Ahmed, M.K., Habibullah-Al-Mamun, M. and Masunaga, S., 2017. Seasonal variation and land use impact on microbial contamination in Betna River, Bangladesh. Environmental Monitoring and Assessment, 189(3), pp. 1–12.##Khatib Haghighi, M. and Ghaani, M. 2018. Assessment of microbial contamination in drinking water sources in Gilan Province. Iranian Journal of Public Health, 47(9), pp. 1320–1328.##Newton, R.J. and McMahon, K.D., 2011. Seasonal differences in bacterial community composition following nutrient additions in a eutrophic lake. Environmental Microbiology, 13(4), pp.887-899.##Park, S.R., Hwang, S.J., An, K. and Lee, S.W., 2021. Identifying key watershed characteristics that affect the biological integrity of streams in the han river watershed, korea. Sustainability, 13(6), p.3359.##Rather, R.A., Ara, S., Padder, S.A., Sharma, S., Pathak, S.P. and Baba, T.R., 2023. Seasonal fluctuation of water quality and ecogenomic phylogeny of novel potential microbial pollution indicators of Veshaw River Kashmir-Western Himalaya. Environmental Pollution, 320, p.121104. DOI: 10.1016/j.envpol.2023.121104##Roshani-Sefidkouhi, M., Mortezazadeh, F., Eslamifar, M., Babanezhad, E., Sheikhi, M. and Gholami-Borujeni, F., 2025. Water quality assessment using IRWQIsc and NSFWQI water quality indicators; A case study: Talar River (Iran). Heliyon, 11(2).##Rusiñol, M., Hundesa, A., Cárdenas-Youngs, Y.,  Fernández-Bravo, A., Pérez-Cataluña, A., Moreno-Mesonero, L., Moreno Trigos, MY., 2020. Microbiological contamination of conventional and reclaimed irrigation water: Evaluation and management measures. The Science of The Total Environment. 710:1-11. ##    https://doi.org/10.1016/j.scitotenv.2019.136298##Safari, R. and Yaghoubzadeh, Z., 2013. Bacterial Bioindicators in Shirood River in Mazandaran Province. Journal of Mazandaran University of Medical Sciences, 22(98), pp.289-299. (In Persian)##United States Environmental Protection Agency (EPA). Monitoring &#38; Assessment of Fecal Bacteria. Available at: https://archive.epa.gov/water/archive/web/html/vms511.html##Verhougstraete, M.P., Rose, J.B. and Reynolds, K.A., 2015. Microbial water quality in watersheds: Role of geology and land use. Water Research, 75, pp. 1–10.##WHO., 2003. Guidelines for Drinking-water Quality, 3rd ed. World Health Organization, Geneva.##Wang, Y., Guo, M., Li, X., Liu, G., Hua, Y., Zhao, J., Huguet, A. and Li, S., 2022. Shifts in microbial communities in shallow lakes depending on trophic states: feasibility as an evaluation index for eutrophication. Ecological Indicators, 136, p.108691.##             DOI: 10.1016/j.ecolind.2022.108691##Yaghoubzadeh, Z. and Safari, R., 2015. Evaluation of bacterial contamination of surface waters of Haraz River. Cellular and Molecular Research (Iranian Journal of Biology), 28(1), pp.136-144. (In Persian)##Yaghoubzadeh, Z. and Safari, R., 2016. Evaluation of coliform bacteria and Nematode eggs in Haraz River runoff. Iranian Scientific Fisheries Journal, 25(1), pp.29-38. (In Persian)##Yaghoubzadeh, Z. and Safari, R., 2018. Bacterial contamination of Sanandaj Azad dam lake in Kurdestan Province in 2015-16. Journal of Research in Environmental Health, 4(1), pp.36-48. (In Persian)## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

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