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<JOURNAL>
<YEAR>1404</YEAR>
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	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ چشم‌انداز هوش مصنوعی و یادگیری ماشین در علوم شیلاتی</TitleF>
		<TitleE>Perspective of artificial intelligence (AI) and machine learning (ML) in fisheries science</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>یکپارچه&#8204;سازی هوش مصنوعی و فناوری&#8204;های نوین در علوم شیلات، تحولی اساسی در روش&#8204;های مدیریت منابع دریایی ایجاد کرده است. در مطالعه حاضر، پیشرفت&#8204;های اخیر در روش&#8204;شناسی&#8204; هوش مصنوعی، از جمله یادگیری عمیق و رویکردهای سنتی یادگیری ماشین و کاربردهای آنها در شناسایی ماهی، نظارت بر جمعیت، مدیریت پایدار و ارزیابی ذخایر را تحلیل کرده است. یافته&#8204;ها نشان می&#8204;دهد که فناوری&#8204;های هوش مصنوعی ابزارهای قدرتمندی برای مقابله با چالش&#8204;های پیچیده آتی در شیلات جهانی ارائه می&#8204;دهند که از جمله می&#8204;توان به بهبود دقت شناسایی گونه&#8204;ها، افزایش کیفیت ارزیابی ذخایر، کاهش صید ضمنی و مبارزه با ماهیگیری غیرقانونی اشاره نمود. با این&#8204;حال، تحقق پتانسیل کامل هوش مصنوعی در مدیریت شیلات مستلزم رفع چالش&#8204;های موجود در دسترسی به داده&#8204;ها، حساسیت مدل&#8204;ها و موانع فناوری است. مطالعه حاضر، نقشه راهی برای ادغام مسئولانه فناوری&#8204;های هوش مصنوعی در مدیریت شیلات به&#8204;ویژه در ایران ارائه می&#8204;دهد و هدف آن پشتیبانی از شیوه&#8204;های مؤثرتر و پایدارتر در مواجهه با چالش&#8204;های پیچیده زیست&#8204;محیطی و اجتماعی-اقتصادی است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
The integration of artificial intelligence and emerging technologies into fisheries science has fundamentally transformed marine resource management approaches (Bradley et al., 2019; Ebrahimi et al., 2021). This field has evolved from foundational object-oriented modeling approaches (Bousquet et al., 1994) to sophisticated expert systems such as CANOFISH and ProTuna, which have enhanced management decision accuracy by 85% (Alagappan and Kumaran, 2013). Currently, the integration of emerging technologies including satellite image processing, smart sensor networks (WSN), and deep learning algorithms has created a new paradigm in sustainable marine resource management (Lu et al., 2024). Global fisheries face significant challenges, as FAO reports indicate 94% of aquatic resources are in two distinct states: 60% in full exploitation and 34% at levels beyond biological sustainability (Kumar et al., 2024; Stroe, 2024). This situation is directly related to illegal, unreported, and unregulated fishing (IUU), which accounts for 20-35% of global catch and causes annual economic damages of $10-23.5 billion (Samy-Kamal, 2022; Grey, 2023; Lubchenco and Haugan, 2023). Fishing activities impact not only target species but also non-target species and biodiversity (Liang and Pauly, 2017), while socioeconomic factors contribute additional complexity to fisheries management (Phillipson and Symes, 2013). This review examines technological advancements in fisheries management from 2004-2024, focusing on machine learning developments in conjunction with traditional management approaches. The investigation addresses how artificial intelligence has improved management efficiency, what implementation challenges exist across different contexts, and what frameworks are necessary for sustainable integration of AI in global fisheries management.

Methodology
&#160;This study applies a systematic review methodology that comprises both quantitative and qualitative methods to examine the implementation and effectiveness of AI technologies in fisheries management. The research procedure was a three-phase structured method that started with a full-fledged literature search in the most important scientific databases including the Web of Science, Scopus, and Google Scholar, with a time frame of 2004 to 2024. Then, the investigation proceeded with the analysis of technical reports from international organizations such as FAO and the World Bank to gain an understanding of the practical aspects of the project, as well as broad analyses of case studies from both developed and developing countries to observe real-world implementations and problems. Data analysis included statistical evaluation of the implementation results via comparisons of success rates over different areas and thematic analysis of the implementation challenges. The main point is, studies brought about objective evaluation of the technology impact among the different locations.
Results
Artificial intelligence and emerging technologies have demonstrated significant contributions to fisheries management. In monitoring applications, empirical studies show that machine learning applied to fish species identification from images has achieved 95% accuracy (Silva et al., 2022). Additionally, the integration of Automatic Identification System (AIS) and Vessel Monitoring System (VMS) data has led to a 40% improvement in marine spatial planning (Thoya et al., 2021; Lu et al., 2024). Recent research demonstrates that deep learning models in early detection of environmental threats have accuracy above 90% (Fei et al., 2023), while advanced radar technologies in monitoring wildlife interactions and fishing activities have shown remarkable efficiency (Navarro-Herrero, 2024). The scalability of these solutions has been enhanced through the development of open-source frameworks, enabling traditional fisheries to benefit from advanced technologies (Silva et al., 2022). Implementation challenges span technical domains, with data standardization issues prominent; socioeconomic barriers, which vary significantly between regions; and regulatory constraints, characterized by adaptation delays.
&#160;Discussion and conclusion
The transformative potential of artificial intelligence in fisheries management requires balanced consideration of technical, socioeconomic, and institutional factors for successful implementation. Studies have shown that the integration of remote sensing data with AIS can effectively monitor IUU fishing activities, particularly in regions with limited monitoring capacity (Kurekin et al., 2019). Smart technology implementation in aquaculture has led to significant efficiency improvements through IoT systems and smart sensors, demonstrating the economic value of AI integration (Lan et al., 2022). Local ecological knowledge (LEK) complements scientific data by providing deeper understanding of marine ecosystems (Silvano and Valbo‐J&#248;rgensen, 2008). Successful examples include identification of causes for fish population decline (Dey et al., 2019) and bycatch management (Caz&#233; et al., 2022). The scalable framework for fish image collection and annotation proposed by Silva et al. (2022) demonstrates how technology can be made accessible across different contexts. Three principal directions for future development are identified: standardization of integration protocols, capacity development in developing regions, and adaptive regulatory frameworks. Future initiatives should address implementation barriers, develop comprehensive training programs, and establish regulatory frameworks that facilitate innovation while ensuring sustainable resource management.
Conflict of Interest
The authors declare that there is no conflict of interest in this research work.
Acknowledgment
We sincerely thank the Office of Vice Chancellor for Research and Artemia and Aquaculture Research Institute of Urmia University for the kind support.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>36</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/11/19
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/8/29
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>آذین</Name>
				<MidName></MidName>
				<Family>احمدی</Family>
				<NameE>Azin</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ahmadi</FamilyE>
				<Organizations>
				<Organization>دانشگاه گیلان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>azin.ahmadi6@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>حقی وایقان</Family>
				<NameE>Ali</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Haghi Vayghan</FamilyE>
				<Organizations>
				<Organization>دانشگاه ارومیه</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>a.haghi@urmia.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Artificial Intelligence (AI)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Machine Learning (ML)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Fisheries Resource</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fish and fisheries</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Sustainable Management</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>هوش مصنوعی (AI)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>یادگیری ماشین(ML)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شیلات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدیریت پایدار</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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		<TitleF>مقاله علمی – پژوهشی:‌ تحلیل شاخص‌های اقتصادی مزارع پرورش ماهی قزل‌آلا (مورد مطالعه: استان همدان)</TitleF>
		<TitleE>Analysis of economic indicators of trout farm fisheries (Case study: Hamedan Province)</TitleE>
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			<CONTENT>با توجه به شرایط اقلیمی و بسترهای مناسب همچون وجود رودخانه&#8204;ها و چشمه&#8204;سارهای فراوان در استان همدان، پرورش ماهی می&#8204;تواند جایگاه مهمی در تأمین نیازهای منطقه داشته باشد. ماهی نقش به&#8204;سزایی در تغذیه و سلامت انسان دارد و بخش عمده&#8204;ای از پروتئین حیوانی را تأمین می&#8204;سازد. تحقیق حاضر با هدف تحلیل شاخص&#8204;های اقتصادی مزارع پرورش ماهی قزل آلا در استان همدان انجام شده است. بدین منظور، مزارع تولیدکننده ماهی قزل&#8207;آلا با روش جورسازی به دوگروه تیمار و کنترل تفکیک و داده&#8207;های لازم با استفاده از پرسشنامه در سال 1402 جمع&#8207;آوری شده است. داده&#8207;ها با رویکردی تلفیقی از تحلیل پوششی داده&#8207;ها و شاخص&#8207;های کارایی و اقتصادی و استفاده از نرم&#8204;افزارهای DEAP و SPSS تجزیه&#8204;وتحلیل شد. نتایج این پژوهش نشان داد که به طور متوسط بهره&#8207;وری عوامل تولید در گروه تیمار 6/5 برابر گروه کنترل بوده و میانگین شکاف بین گروه&#8204;های تیمار و کنترل از نظر کارآیی فنی، تخصیصی و اقتصادی به&#8204;ترتیب 1/8، 2/17 و 5/21 درصد است. همچنین نرخ بازدهی داخلی در گروه تیمار 8/33 درصد و نسبت منفعت به هزینه 8/1 است. این دو شاخص در مزارع کنترل به&#8204;&#8204;ترتیب 8/18 درصد و 2/1 است. بنابراین، با استفاده از توصیه&#8204;های تحقیقاتی و ترویج یافته&#8207;های پژوهشی مراکز تحقیقاتی می&#8207;توان این شکاف را تاحد ممکن کاهش داد و منجر به افزایش بهره&#8207;وری عوامل تولید شد.</CONTENT>
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			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
In Southwest Asia and Iran, the fisheries industry is an important sub-sector of agriculture because it provides a portion of the valuable protein for society, employment, and national income. The growth of the aquaculture industry in the world is 4.5% and it is 7% (Agricultural Research, Education and Extension Organization, 2023) in Iran. In addition to providing food for the growing population and creating jobs and income for farmers, this can also play an important role in earning foreign exchange for the country. Aquaculture in the country includes warm-water fish farms (carp), cold-water fish farms (trout), and shrimp farms. According to statistics published by the Iranian Veterinary Organization (2023), Iran ranks first in the world in the production of cold-water fish in freshwater with a production of 237 thousand tons (Iranian Veterinary Organization, 2024). In the west of the country, and especially in Hamedan Province, due to its geographical location, the presence of natural canals, seasonal and permanent rivers, and springs, it is possible to grow and develop trout farms and ponds, which are nutritionally the best type of protein for human consumption. The trout farmers in Hamedan Province produced more than 5,237,000 tons of trout in the year (2021-2022) and sold them fresh in markets inside and outside the province (Census of Jihad Agriculture, 2022-2021). Given the special situation of Hamedan Province in the field of fish production, a comprehensive study has not yet been conducted on the analysis of the economic indicators of trout farms in this province. Therefore, the above study aimed to investigate cold-water fish producing farms that used researchers&#39; recommendations in their management and production methods based on the results of research projects as the treatment group and units that were managed traditionally and without using research recommendations in their management and production as the control group.
Methodology
This research is a descriptive-analytical study that is applied in terms of purpose and is considered a survey in terms of data collection. The statistical population of the research includes cold-water fish producers (trout) in Hamedan province. The sample size of 49 operators was calculated using the Cochran formula and was systematically selected from the list of farms in the province using simple random sampling. The required data was collected and completed through a researcher-made questionnaire in 2023, including 5 sections: fish farm manager&#39;s characteristics (11 questions); fish farm characteristics (30 questions); technical aspects of production (35 questions); fixed investment costs (12 questions) and current costs (11 questions), and by visiting the Fisheries Department and the Agricultural Jihad Organization of the province in person. The opinions of agricultural and fisheries economics experts were used to examine the validity of the questionnaire, and the Cronbach&#39;s alpha test was used to examine the reliability of the questions. Using the matching method, the statistical population was first divided into two groups: the treatment group (units in which the research results were used) and the control group (units that did not use the research results or used them less), and then the two groups were compared using efficiency indicators, internal rate of return, benefit-to-cost ratio, payback period, and production function.
Results&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160;&#160; 
The results of examining the balance of auxiliary variables showed that by performing the matching operation to calculate the effects of the research results on the treatment group, the difference between the means of the two groups decreased. To compare the two treatment and control groups and the effect of the factors of fry, labor, capital, food, and pond area on their production rate, two transcendental and Cobb-Douglas production functions were estimated simultaneously and these two specifications were compared using the F test. According to this function, the most important factor in creating differences between units is the variable of pond area. Among the variables used, in addition to the pond area, food, fry and labor also showed a significant effect on production. The results of the Ramsey reset test indicated that there was no specification bias due to the removal of the important variable. In the treatment unit, regarding the pool area variable, considering the logarithmic specification, it can be said that with a 10% increase in the pool area, it is expected that about 13.1% will be added to production. In terms of the contribution to creating a difference in the production level of the units, the pool area variable is not only significant in terms of the absolute value of the coefficient, but also has a very high difference, so that the other four significant variables, including the fry, food, and labor variables, with a 10% increase, can increase production by 11.9, 9 and 12.5%, respectively, which is very different from the food variable. In the control unit, with a 10% increase in the values ​​of the variables under study, the production rate increases by 5.6% less than the values ​​mentioned in the treatment group. Based on the results, the efficiency of the units under study, including technical, allocative, and economic efficiency, has been examined under two assumptions of constant and variable returns to scale in two treatment and control groups. The results showed that the average technical efficiency of trout farms in the treatment group under CRS conditions is 90.5 percent. While the average technical efficiency in the same group is 91.4 percent. The average scale efficiency of trout farms in the treatment group is 99.02 percent. In the control group, the efficiency under CRS and VRS is 82.2 and 83.3 percent, respectively, and the scale efficiency is 98.7 percent. Technical efficiency in the treatment group is much better than the control group. The use of research recommendations has increased technical efficiency by 8.3 percent under CRS and 8.1 percent under VRS. The average allocative efficiency in the treatment group was estimated to be 86.8 percent under CRS and 87.6 percent under VRS. The allocative efficiency in the control group is 75.3 percent under CRS and 70.4 percent under VRS. The use of research recommendations has increased allocative efficiency by 11.5 percent assuming CRS and 17.2 percent assuming VRS. The average economic efficiency of the fish farming treatment group farms under CRS conditions is 78.6 percent and 80.1 percent under VRS conditions. The economic efficiency in the control group under CRS conditions is 61.9 percent and 58.6 percent under VRS conditions. Considering the technology available in fish farming farms, it is possible to increase profits in control units by 16.7 percent assuming CRS and 21.5 percent assuming VRS. Therefore, by improving the economic efficiency of fish farming in the control group, it is possible to increase product production and profitability of the units. Considering a discount rate of 16%, the internal rate of return and the benefit-cost ratio in the treatment group are 33.8% and 1.8%, respectively. These two indicators in the control group are 18.8% and 1.2%, respectively. The payback period in the treatment and control groups is 4.8 and 7.6 years, respectively. Therefore, it can be said that the investment in both groups is economically justified, while in the treatment group, it is in a better position in this respect.
Discussion and Conclusion&#160;
Based on the results, the application of research recommendations in the trout farming industry will increase the efficiency and effectiveness of this industry. The results of the studies of Rahman et al. (2019); Samat et al. (2024) and Duy et al. (2023) confirm this. Also, the average productivity of production factors in the treatment group (units that used research results in their activities) was 5.9 times higher than the control group, which is in line with the study by Najafi et al. (2018) and Vormedal (2024) that the use of research findings plays an effective role in increasing productivity. It is also necessary to make the activities of production units more competitive by implementing government economic adjustment policies, reducing production subsidies, further convergence of international markets, and increasing the competitive power of units. Therefore, the area of ​​the pond has a significant impact on profitability. Therefore, the results of the research are consistent with the results of the study by Yarahmadi et al. (2022) and Akter et al. (2024), as they showed in their results that the amount of feed consumed and the area of ​​the fish pond had the greatest impact on trout production. In addition to the above, the results showed that the internal rate of return in the treatment group was 33.8 percent and the benefit-to-cost ratio was 1.8. These two indicators in the control group farms were 18.8 percent and 1.2 percent, respectively. The results of Duy et al. (2023) also confirm this issue and stated that training and promotion of research findings had a positive effect on the efficiency and effectiveness of the firms receiving these findings and reduced production costs in these firms. Therefore, by using research recommendations and promoting applied research findings, this gap can be reduced as much as possible and lead to increased efficiency of these types of activities.
Conflict of Interest
The authors declare no conflict of interest.
Acknowledgment
The authors acknowledge the support provided by the Agricultural Research, Extension and Education Organization.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>37</FPAGE>
			<TPAGE>49</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/11/192024/10/3
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/7/12
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/302025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مهسا</Name>
				<MidName></MidName>
				<Family>معتقد</Family>
				<NameE>Mahsa</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Motaghed</FamilyE>
				<Organizations>
				<Organization>گروه برنامه‌ریزی و توسعه کشاورزی، موسسه آموزش و ترویج کشاورزی، سازمان تحقیقات، آموزش و ترویج کشاورزی، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mahsa.motaghed@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>امیر</Name>
				<MidName></MidName>
				<Family>دادرس مقدم</Family>
				<NameE>Amir</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dadras Moghadam</FamilyE>
				<Organizations>
				<Organization>دانشکده مدیریت و اقتصاد، دانشگاه سیستان و بلوچستان، سیستان و بلوچستان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>amdadras@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سید محسن</Name>
				<MidName></MidName>
				<Family>سیدان</Family>
				<NameE>Seyed mohsen</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Seyedan</FamilyE>
				<Organizations>
				<Organization>سازمان تحقیقات، آموزش و ترویج کشاورزی</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>seyedan1969@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Trout</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Data Envelopment Analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>sorting</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>internal rate of return (IRR)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>benefit-cost ratio.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماهی قزل‌آلا</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحلیل پوششی داده‌‌ها</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جورسازی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نرخ بازدهی داخلی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نسبت منفعت به هزینه.</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>Akter, M., Schrama, J. W., Adhikary, U., Alam, M. S., Mamun-Ur-Rashid, M., and Verdegem, M. 2024. Effect of pellet-size on fish growth, feeding behaviour and natural food web in pond polyculture. Aquaculture, 593, 741342. DOI: https://doi.org/10.1016/j.aquaculture.2024.741342.##Alikhani, L., Dashti, G., &#38; Raheli, H. 2015. Technical efficiency and production risk of cold-water fish farms in the Kamyaran County. Journal of Animal Science Research, 25(2), 1-12.‌ (in Persian).##Asadikia, H., Mosavi, S. H., Khalilian, S., and Najafi Alamdarlo, H. 2021. Comparison of technical and economic efficiency of trout farms production from imported and domestic egg. Aquaculture Sciences, 9(1), 35-47.‌ (in Persian).##Becker, s., and Ichino, A. 2002. Estimation of Average Treatment Effects Based on Propensity Scores. The Stata Journal, 2, 358–377. DOI: https://doi.org/10.1177/1536867X020020040##Census of Jihad Agriculture. 2022-2021. Organization of Jihad Agriculture, Hamadan Province, Hamadan Province. (in Persian)##Chary, K., van Riel, A. J., Muscat, A., Wilfart, A., Harchaoui, S., Verdegem, M., ... and Wiegertjes, G. F. 2024. Transforming sustainable aquaculture by applying circularity principles. Reviews in Aquaculture, 16(2), 656-673. DOI: https://doi.org/10.1111/raq.12860.##Coelli, T. J., Rao, D.S.P., O'Donnell, C.J., and Battese, G.E., 2005. An introduction to efficiency and productivity analysis. Springer Science &#38; Business Media.##Dehejia, R. H., and Wahba, S. 2002. Propensity Score-Matching Methods for Nonexperimental Causal Studies. The Review of Economics and Statistics, 84, 151–161.##Duy, D. T., Nga, N. H., Berg, H., and Da, C. T., 2022. Assessment of technical, economic, and allocative efficiencies of shrimp farming in the Mekong Delta, Vietnam. Journal of the World Aquaculture Society.   DOI:10.1111/jwas.12915##FAO. 2018. Fishery statistical collections: Consumption of fish and fishery products. Retrived from: www.fao.org/fishery/ statistics/global-consumption/e.##Farash, Z., Gholamrezaei, C., Ghanbari Mocahed, R., 2017. Investigating the role and importance of sustainable aquaculture in the development of food resources, 11th Congress of the pioneers of progress##Farrell, M. J., 1957. The measurement of productive efficiency. Journal of the Royal Statistical Society: Series A, 120 (3), 253-281. DOI: https://doi.org/10.2307/2343100##Hashemi, dashtaki, S. F., Yazdani, S., and Rafiei, H., 2021. Measuring the technical, allocative and economic efficiency of salmon farming using the data envelopment analysis approach (case study; Fars province), Fifth International Congress on Agricultural and Environmental Development with emphasis on the United Nations Development Program##Iran Statistics Center. 2021. Statistics of the Ministry of Agricultural Jihad, Volume 2, Deputy Planning Department of the Ministry of Agricultural Jihad. (in persian).##Kompas, T., and Che, T.N. 2004. Production and Technical Efficiency on Australian Dairy Farms. International and Development Economics, 4, 57-77.##Li, K., and Prabhala, N. R., 2006. Self-Selection Models in Corporate Finance. Working Paper, Center for Corporate Governance – Tuck School of Business at Dartmouth. DOI:http://dx.doi.org/10.2139/ssrn.843105##Najafi, A., Zeraatkish, S., Mataei, Z., and Gharra, K., 2018. The measurement and total factors productivity analysis of cold-water fish production in Kermanshah province farms; 27 (4) :1-11. URL: http://isfj.ir/article-1-2048-fa.html (in persian)##Oluwatayo, I. B., and Adedeji, T. A. 2019. Comparative analysis of technical efficiency of catfish farms using different technologies in Lagos State, Nigeria: A Data Envelopment Analysis (DEA) approach. Agriculture &#38; Food Security, 8(1), 1-9. DOI: https://doi.org/10.1186/s40066-019-0252-2.##Rahman, M. T., Nielsen, R., Khan, M. A., and Asmild, M. 2019. Efficiency and production environmental heterogeneity in aquaculture: A meta-frontier DEA approach. Aquaculture, 509: 140-148. DOI: https://doi.org/10.1016/j.aquaculture.2019.05.002##Rosenbaum, P., 1995. Observational Studies, New York. Springer V erlag.##Samat, N., Goh, K. H., and See, K. F. 2024. Review of the application of cost–benefit analysis to the development of production systems in aquaculture. Aquaculture, 740816. DOI: https://doi.org/10.1016/j.aquaculture.2024.740816 ·##Statistics fishers Hamedan province. 2022-2021.Management of Fisheries, Jihad Agriculture, Hamadan Province. (in Persian).##Thach, K. S. R., Vo, H. T., and Lee, J. Y., 2021. Technical Efficiency and Output Losses in Shrimp Farming: A Case in Mekong Delta, Vietnam. Fishes, 6(4), 59. DOI: https://doi.org/10.3390/fishes6040059##Vormedal, I., 2024. Sea-lice regulation in salmon-farming countries: how science shape policies for protecting wild salmon. Aquaculture International, 32(3): 2279-2295. DOI: https://doi.org/10.1007/s10499-023-01270-w##Yarahmadi, B., mohamadi Saei, M., Pahlevani, R., and Salehi, M., 2022. Efficiency determination of the trout farm units using a deterministic parametric frontier (DPF) analysis method in Lorestan province (case study of Alshtar city). 15 (4) :127-140. DOI: 10.52547/aqudev.15.4.127## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ اثرات جامدات معلق و رقیق‌سازی ملاس بر رشد، زیست‌توده و پالایش زیستی ریزجلبک سبز Scenedesmus quadricauda</TitleF>
		<TitleE>Effects of suspended solids and dilution of molasses on growth, biomass and biorefinery of the green microalga Scenedesmus quadricauda</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>در این پژوهش اثرات جامدات معلق و رقیق سازی ملاس بر ریزجلبک Scenedesmus quadricauda با هدف تعیین تراکم سلولی، رشد و زیست&#8204;توده جلبکی و ارزیابی پالایش زیستی انجام شد. آزمایش با ۷ تیمار شامل؛ تیمارهای پساب ملاس دارای جامدات معلق در غلظت&#8204;های ۱، ۵ و ۱۰ درصد (حجم/حجم) و پساب ملاس بدون جامدات معلق ۱، ۵ و ۱۰ درصد (حجم/حجم) و تیمار شاهد در محیط کشت BBM برای یک دوره ۱۴ روزه در قالب طرح کاملاً تصادفی در ۳ تکرار انجام شد. ملاس در تمام تیمارها باعث رشد جلبک S. quadricauda گردید و تراکم جلبکی و رشد آن به&#8204;ترتیب دامنه&#8204;ای از 106&#215;۴5/1 -105&#215;25/۷ سلول بر میلی&#8204;لیتر و 10۴/0 &#8211; 0۵۴/0 در روز به&#8204;دست آمد. بیشترین مقدار زیست&#8204;توده تولیدی ۷/۶۳۴۳ میلی&#8204;گرم بر لیتر در تیمار ملاس ۱۰ درصد بدون جامدات معلق به&#8204;دست آمد و در سایر تیمارها دامنه&#8204;ای از ۴۹۶۷ - ۱/۲۱۹۹ میلی&#8204;گرم بر لیتر داشت. در غلظت&#8204;های کم (۱ و ۵ درصد) تأثیر جامدات معلق بر زیست&#8204;توده جلبک قابل&#8204;ملاحظه نبود، اما در تیمار با غلظت ۱۰ درصد و بدون جامدات معلق زیست&#8204;توده بیشتری به&#8204;&#8204;دست آمد (p&#60;0/05). حذف نیترات و فسفات به طور معنی&#8204;داری در تمام تیمارها انجام شد (p&#60;0/05). بیشترین درصد حذف نیترات در تیمار ملاس ۱۰ درصد بدون جامدات معلق (۵۸ درصد) و بیشترین درصد حذف فسفات در تیمار ملاس ۱۰ درصد (۴۸ درصد) به&#8204;&#8204;دست آمد. کاهش BOD و COD در تمام تیمارها قابل ملاحظه بود و برای BOD دامنه&#8204;ای از ۱۹/۹۹- ۳۷/۹۲ درصد و برای COD دامنه&#8204;ای از ۴۶/۹۹-۰۵/۹۴ بود. بیشترین حذف BOD5 (۱۹/99 درصد) در تیمار ملاس 5 درصد و بیشترین درصد حذف COD (4۶/99 درصد) مربوط به تیمار پساب ملاس ۱۰ درصد هر دو تیمار بدون جامدات معلق به&#8204;&#8204;دست آمد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
Algae are the most important photosynthetic groups in aquatic environments, as they are carbon and nitrogen fixers and considered as primary producers (Sigee, 2005; Falkowski and Raven, 2013; Fowler et al., 2013). The growth of algae in wastewater are common phenomenon that has a crucial role in removing minerals and metabolic byproducts. The wastewater from sugar production contains high levels of carbon, nitrogen, and phosphorus, along with high BOD and COD. Molasses is a byproduct of sugar factories and is primarily used as a raw material for yeast production. It also has considerable commercial value in various fermentation processes, animal feed, and biofertilizers (Dahiya et al., 2001; Torabian and Mahjuri, 2004; Kobya and Delipinar, 2008). Molasses contains 45-50% carbohydrates, 15-20% non-aromatic organic compounds, 10-15% ash (minerals), and about 20% water (Kalyuzhnyi and Murray, 2005). Molasses wastewater includes chemicals such as propionic acid, various salts, and fermentation metabolites (Blonskaja and Zub, 2009). In addition to molasses concentration and the stated conditions, which greatly impact the growth of microscopic algae, the role of suspended solids in molasses as another influential factor in algal growth and reproduction can be investigated. The negative effects of suspended solids, particularly at high concentrations are crucial due to their reduction in light intensity. Furthermore, suspended solids can settle on algae surfaces, hindering gas exchange (e.g., oxygen and carbon dioxide), which negatively affects photosynthesis efficiency (Boyd, 2020). On the other hand, the positive effects of suspended solids include stimulating the production of certain secondary metabolites through stress induction in algal cells (Huang et al., 2024).
&#160;This study aims to investigate the role of suspended solids and molasses dilution in the growth and biomass production of the green microalga Scenedesmus quadricauda and its potential for bioremediation. Understanding suspended solids and molasses dilution levels can contribute to the management of algal cultures in terms of optimizing light intensity, turbidity, culture system design, and the production of valuable secondary metabolites.
&#160;Methodology
&#160;Molasses wastewater was collected from the Eqlid Sugar Factory, located in Fars province, Iran. The factory processes sugar beets grown by 800 local farmers. The wastewater sample (10 liters) was collected before entering the treatment section of the factory in November 2023. The green microalga S. quadricauda was cultured in raw pre-treated wastewater, diluted to target concentrations of 1%, 5%, and 10%, under two conditions: with suspended solids and without suspended solids (Table 1) for 14 days. Seven experimental treatments were prepared, including BBM medium (control) and molasses wastewater with and without suspended solids at three dilution levels: 1% (10 ml/L) 5% (50 ml/L) 10% (100 ml/L). These solutions were added to 5-liter glass Erlenmeyer flasks. The initial pH of all cultures was adjusted to 6.8 using concentrated NaOH and HCl solutions. Before introducing the algal stock, all samples were autoclaved at 121&#176;C for 15 minutes. After cooling, 5% (v/v) of the initial algal stock containing 2 &#215; 10⁶ cells/mL was added. The cultures were incubated under appropriate light conditions provided by fluorescent lamps (60 &#181;mol photons/m&#178;/s) with a 12-hour light/12-hour dark photoperiod and gentle aeration. The water temperature in all treatments was kept constant at 25 &#177; 2&#176;C. The experiment followed a completely randomized design with three replicates over 14 days. Daily cell counting of S. quadricauda was performed using a hemocytometer (depth: 0.1 mm, area: 0.0025 mm&#178;), following the method proposed by Martinez et al. (2000). The specific growth rate was calculated using the formula by Omori and Ikeda (1984). To measure biomass, 100 mL of the algal culture was filtered using pre-weighed membrane filter papers (0.45 &#181;m). The filtered samples were dried in an oven at 80&#176;C for 4 hours. Dry Biomass Measurement and Analytical Methods After drying the algal biomass, it was placed in a desiccator to reach equilibrium with the laboratory environment. The dry weight was then measured, and the difference in weight was used to calculate the dry biomass of the algae (Omori and Ikeda, 1984). Nitrate concentrations were measured using a spectrophotometric colorimetric method at 275 nm and 220 nm, using a UV-VIS spectrophotometer (Nanombana UVISNM98 UV-VIS). Phosphate concentration was determined using spectrophotometry at 880 nm, with a JENWAY 6300 spectrophotometer (Baird et al., 2017). The five-day biochemical oxygen demand (BOD₅) was assessed by adding a specific amount of wastewater to a dilution water solution in 300 mL dark Winkler bottles. The dissolved oxygen (DO) content was measured at the start and after five days of incubation at 20&#176;C, using an oxygen meter. The chemical oxygen demand (COD) was determined using potassium dichromate and silver sulfate reagents, with digestion in a COD reactor for 2 hours, followed by absorbance reading at 600 nm using a spectrophotometer (Baird et al., 2017). This study was conducted using a completely randomized design (CRD) with different treatments (Table 1), each with three replicates. One-way ANOVA was used to determine significant statistical differences, and Duncan&#8217;s test and Student&#8217;s t-test were performed for mean comparisons. All statistical analyses were conducted using SPSS software, and the graphs were generated using Excel.
Results
The total suspended solids (TSS) and dissolved solids (TDS) in the raw molasses wastewater were measured at 7697.2 mg/L and 2540.8 mg/L, respectively. The nitrate and phosphate concentrations were 1595.24 mg/L and 12.73 mg/L, respectively. The BOD₅ and COD values of molasses wastewater were 42,790 mg/L and 136,156 mg/L, respectively. The pH was 5.92, and the electrical conductivity (EC) was 3.97 mS/cm. The cell density of S. quadricauda in different treatments, including the control (BBM), molasses wastewater without suspended solids (1%, 5%, 10%), and molasses wastewater with suspended solids (1%, 5%, 10%), was: 1.03 &#215; 10⁶, 1.22 &#215; 10⁶, 1.45 &#215; 10⁶, 7.25 &#215; 10⁵, 1.0 &#215; 10⁶, 9.85 &#215; 10⁵, and 1.05 &#215; 10⁶ cells/mL, respectively. These values correspond to days 14, 14, 14, 14, 11, 14, and 14 of the cultivation period. The highest cell density at the end of the experiment (day 14) was observed in the 1% molasses wastewater with suspended solids treatment. Overall, 1% and 5% molasses wastewater with suspended solids and 1% molasses wastewater without suspended solids showed higher cell densities than the control (BBM). The specific growth rate at the end of day 14 ranged from 0.064 &#8211; 0.104 per day, with the highest growth in the 1% molasses wastewater with suspended solids and the lowest in the 10% molasses wastewater with suspended solids. The biomass concentration ranged from 2199.1 &#8211; 6343.7 mg/L, with the highest value in the 10% molasses wastewater without suspended solids and the lowest in the 1% molasses wastewater with suspended solids. At low concentrations (1% and 5%), suspended solids had no significant effect on biomass. However, at 10% concentration, the treatment without suspended solids resulted in significantly higher biomass production (p &#60; 0.05). The phosphate concentration decreased from 278.3 &#8211; 250.4 mg/L to 206.35 &#8211; 149.4 mg/L (Figure 2B). Nitrate and phosphate removal was significant in all treatments (p &#60; 0.05). The highest nitrate removal (58%) and phosphate removal (46%) were observed in the 10% molasses wastewater without suspended solids (Figure 2C). The BOD₅ removal in molasses wastewater treatments ranged from 92.37 &#8211; 99.19%. The highest BOD value after cultivation was observed in the 5% molasses wastewater with suspended solids, and the lowest in the 5% molasses wastewater without suspended solids and 1% molasses wastewater with suspended solids. The highest BOD₅ removal (99.19%) was found in the 5% molasses wastewater without suspended solids, while the lowest (92.37%) occurred in the 1% molasses wastewater without suspended solids. The COD removal ranged from 94.05 &#8211; 99.46%, with the highest COD after cultivation found in the 10% molasses wastewater, and the lowest in the 1% molasses wastewater without suspended solids.
Discussion and conclusion
After the 14-day cultivation period, the treatments with 1% and 5% molasses containing suspended solids and 1% molasses without suspended solids exhibited higher cell densities compared to the control treatment, whereas other treatments had lower cell densities than the control. Similar to the present study, Farhadian et al. (2022) reported that the highest cell density of the marine microalga Tetraselmis tetrahele was observed in 1% molasses and concluded that the biomass production of T. tetrahele in 1% molasses was higher than in 0.5% diluted molasses. They also found that biomass production in molasses treatments was higher compared to other culture media. The results of this study under mixotrophic conditions showed that the highest biomass production occurred in the 10% molasses treatment without suspended solids. Biomass production showed an increasing trend with increasing molasses concentration from 1% to 10% in treatments without suspended solids. Moreover, the biomass produced in the 1% and 5% molasses treatments was almost equal and higher than in the control treatment. However, in the 10% molasses treatment with suspended solids, a noticeable reduction in biomass production was observed, which could be attributed to reduced light penetration in the culture medium. Suspended solids can limit light penetration into the water column, reducing photosynthesis and subsequently decreasing algal biomass. Suspended solids in water can pose serious challenges to aquatic ecosystems. These particles, often introduced through human activities such as agriculture and industrial pollution, can reduce water clarity, hinder the respiration of aquatic organisms, and even cause direct harm. Studies have shown that suspended solids not only affect water quality but also impact microscopic organisms in aquatic environments. These particles can cover the gills of fish and other aquatic organisms, making respiration difficult. Additionally, they can absorb sunlight, limiting photosynthesis in aquatic plants and disrupting the food chain (Bilotta and Brazier, 2008). In this study, all treatments involving S. quadricauda resulted in nitrate and phosphate uptake. The highest nitrate removal percentage (58%) was observed in the 10% molasses treatment without suspended solids, while the highest phosphate removal percentage (48%) was recorded in the 10% molasses treatment. Heydari et al. (2011) found that S. quadricauda grows well in nitrogen-rich environments, making it suitable for treating nitrogen-enriched wastewater due to its high growth rate and survival. The process of nitrate and phosphate removal by Scenedesmus microalgae has been reported in multiple studies (Oswald and Gotass, 1995; Martinez et al., 2000; Voltolina et al., 2004; Wang and Lan, 2011; Arora et al., 2021). Microalgae utilize nitrogen and phosphorus from wastewater to synthesize energy-storing molecules such as adenosine triphosphate (ATP) and adenosine diphosphate (ADP), as well as genetic material. Additionally, inorganic phosphate forms such as orthophosphate, HPO₄&#178;⁻, and H₂PO₄⁻ are preferred by microalgal cells, which absorb them via phosphorus transporters in the plasma membrane (Ahmed et al., 2022). A comparison of nitrate and phosphate removal percentages across different concentrations (Figure 2&#8211;C) indicated that removal rates were significantly higher in molasses treatments without suspended solids than in those with suspended solids. This suggests that the presence of suspended solids may hinder nitrate and phosphate removal. Therefore, separating suspended solids from the culture medium is crucial for improving the efficiency of algal bioremediation in wastewater treatment. Biochemical Oxygen Demand (BOD) and Chemical Oxygen Demand (COD) were measured and evaluated at the beginning and end of the mixotrophic cultivation experiments.
The highest BOD removal percentage (99.19%) was observed in the 5% molasses treatment without suspended solids, while the lowest BOD removal percentage (92.37%) was recorded in the 1% molasses treatment without suspended solids. Similarly, the highest COD removal percentage (99.46%) was measured in the 10% molasses treatment without suspended solids, whereas the lowest COD removal percentage (94.05%) was found in the 1% molasses treatment without suspended solids. Wang and Lan (2011) stated that biomass production in mixotrophic culture systems is generally higher than in heterotrophic models, possibly due to greater access to carbon sources (CO₂) in mixotrophic conditions. Nagarajan et al. (2019) also reported significant reductions in BOD and COD through microalgal cultivation in wastewater.
The content is subject to carbon reduction. Carbon and organic matter uptake and consumption are also common phenomena in microalgae. Microalgae contribute to the removal of organic substances such as urea and inorganic nutrients, including nitrate and phosphate from wastewater, which helps reduce BOD and COD (Arora et al., 2021). Overall, the results indicate that the biomass obtained from the microalga S. quadricauda, cultivated under mixotrophic conditions in molasses wastewater in this study, has numerous advantages, including a short reproductive cycle, enhanced photosynthesis, higher and more efficient nutrient consumption, and effective bioremediation of wastewater (significant reduction of nitrate, phosphate, color, COD, and BOD).
Acknowledgment
This research was supported by Isfahan University and Technology, Isfahan, Iran.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>51</FPAGE>
			<TPAGE>63</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/11/192024/10/32025/01/26
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/11/7
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/302025/04/302025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>میلاد</Name>
				<MidName></MidName>
				<Family>مسعودی</Family>
				<NameE>Milad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Masoudi</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>m.masoudi@na.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>امیدوار</Name>
				<MidName></MidName>
				<Family>فرهادیان</Family>
				<NameE>Omidavr</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Farhadian</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>omfarhad@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>عیسی</Name>
				<MidName></MidName>
				<Family>ابراهیمی درچه</Family>
				<NameE>Eisa</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ebrahimi</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>e_ebrahimi@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Molasses effluent</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>biomass</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>suspended solids</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پساب ملاس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زیست‌توده</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>جامدات معلق</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ اثر خوراک حاوی پروبیوتیک Lactobacillus acidophilus و پلی‌فنول فرولیک اسید بر ایمنی غیراختصاصی و فعالیت آنزیم‌‌های آنتی‌اکسیدانی در ماهی قرمز
 (Carassius auratus)</TitleF>
		<TitleE>Effect of dietary probiotic Lactobacillus acidophilus and polyphenol ferulic acid on non-specific immunity and antioxidant activity in goldfish (Carassius auratus)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>در مطالعه حاضر، تاثیر جیره&#8204;&#8204;های حاوی پروبیوتیکLactobacillus acidophilus &#160;&#160;(LA) و پلی&#8204;&#8204;فنول فرولیک اسید (FA) را بر عملکرد رشد، میزان ایمنی غیر اختصاصی، و فعالیت آنزیم&#8204;&#8204;های آنتی&#8204;&#8204;اکسیدانی در ماهی قرمز (Carassius auratus) مورد بررسی قرار گرفت. 240 عدد ماهی با وزن اولیه 35/0&#177;34/3 گرم با چهار جیره آزمایشی شامل مقدار صفر از مکمل&#8204;&#8204;های غذایی (T0)، 108&#215; 6 واحد تشکیل دهنده&#8204;&#8204; کلنی بر گرم پروبیوتیک LA (T1)، 100 میلی&#8204;گرم بر کیلوگرم FA (T2) و ترکیبی از LA و FA (T3) به مدت 8 هفته تغذیه شدند. نتایج نشان داد که وزن نهایی، افزایش وزن و نرخ رشد ویژه به طور قابل&#8204;توجهی تحت تأثیر LA و FA قرار گرفتند و بیشترین رشد در تیمار T3 مشاهده شد (P&#60;0.05). سطوح ایمونوگلوبولین تام، IgM و لیزوزیم با رژیم غذایی FA و LA افزایش یافت (05/0&#62;p). سطوح ایمونوگلوبولین تام، IgM و لیزوزیم با رژیم غذایی FA و LA افزایش یافت. فعالیت مالون دی آلدئید (MDA) به&#8204;وسیله جیره&#8204;های آزمایشی کاهش یافت و کمترین مقدار آن به طور قابل&#8204;توجهی در تیمار T3 در مقایسه با گروه شاهد مشاهده شد (05/0&#62;p). ماهی&#8204;هایی که با جیره&#8204;های حاوی LA یا FA تغذیه شده بودند، افزایش قابل&#8204;توجهی در فعالیت کاتالاز (CAT)، سوپراکسید دیسموتاز (SOD) و گلوتاتیون پراکسیداز (GPX) نسبت به گروه شاهد نشان دادند (05/0&#62;p). نتایج نشان داد که این مکمل&#8204;&#8204;های غذایی به صورت هم&#8204;زمان در غلظت&#8204;&#8204;های 100 میلی&#8204;&#8204;گرم بر کیلو&#8204;&#8204;گرم فرولیک اسید و 108&#215; 6 کلنی بر گرم پروبیوتیک LA (T3)، از پتانسیل افزایش رشد، ایمنی ذاتی و آنزیم&#8204;&#8204;های آنتی&#8204;&#8204;اکسیدانی در ماهی قرمز برخوردارند. هر دو مکمل خوراکی اثرات هم&#8204;افزایی نشان دادند و توصیه می&#8204;&#8204;شود از این ترکیبات به طور هم&#8204;زمان برای آبزی&#8204;پروری پایدار استفاده شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
Fish is among the best sources of animal protein but aquaculture industry have faced to many challenges. Global aquaculture productions are vulnerable, and the increasing prevalence of diseases has caused a partial and overall reduction in aquaculture production (Bondad-Reantaso et al., 2005). Factors such as overcrowding in ponds, periodic movement and manipulation, sudden temperature changes, water quality deterioration, and poor nutritional conditions, along with physiological changes in fish such as stress, have heightened susceptibility to infections (Quesada-Garc&#237;a et al., 2013). In aquaculture, the application of natural immuno-stimulants to enhance fish health and boost their resistance to pathogens has shown encouraging results (Habibnia et al., 2024).
Methodology
This study examined the impact of incorporating probiotic Lactobacillus acidophilus (LA) and polyphenol ferulic acid (FA) into the diet of goldfish (Carassius auratus) on growth performance, as well as factors related to immunity and antioxidant activity. A total of 240 fish, initially weighing 3.34 &#177; 0.35 g, were divided into four experimental groups: a control treatment with no food supplement (T0), fed with 6 x 108 CFU/g LA probiotic (T1), fed with 100 mg/kg FA (T2), and fed with a combination of LA and FA (T3) for eight weeks. At the end of feeding trial, the fish were fasted for 24 hours and all the fish in each tank were sampled and then anesthetized with benzocaine at a concentration of 120 mg per liter and weighed individually. Growth performance was then assessed. Thereafter, nine fish (per replication) were randomly selected. The selected fish were then subjected to anesthesia with Benzocaine at a concentration of 120 mg per liter to minimize handling stress. The fish underwent dissection, with the intestine and liver tissues being meticulously separated. Subsequently, these tissues were promptly subjected to freezing using liquid nitrogen and were subsequently preserved at a temperature of -80 &#176;C. To measure lysozyme activity, the sample was added to a suspension of&#160;Micrococcus lysodeikticus&#160;prepared in 0.1 molar citrate phosphate buffer at a pH of 5.8. Optical density was read at a wavelength of 410 nanometers for 5 minutes, with readings taken every 30 seconds. Total immunoglobulin (Ig) levels were determined based on the method by Siwicki et al. (1994). In brief, total protein from the homogenate sample was measured using the microprotein method, followed by precipitation of immunoglobulin molecules with a 12% polyethylene glycol solution. The protein level was then re-measured, and the difference in protein content was considered as the Ig content. The levels of lipid peroxidation products in the fish homogenate were determined based on a previous study (Kei, 1978). Briefly, trichloroacetic acid (20%) (1.25 mL) was mixed with the fish homogenate (0.25 mL) and centrifuged at 2000 g for 10 minutes. Then, 1.25 mL of sulfuric acid (0.05 molar) and 1 mL of thiobarbituric acid (0.2%) were added to the collected precipitate and boiled for 30 minutes. After adding 2 mL of n-butanol, centrifugation (2000 g) was performed for another 10 minutes. The final absorbance was recorded at a wavelength of 532 nanometers. Catalase activity in the fish homogenate was assessed based on a previous study (Goth, 1991). The reaction buffer (1 mL) consisted of hydrogen peroxide (65 mM) and sodium-potassium phosphate buffer (60 mM) mixed with the fish homogenate (0.5 mL) for 1 minute at 37&#176;C. The enzymatic reaction was terminated by adding 1 mL of ammonium molybdate (32.4 mM), and absorbance was recorded at 405 nanometers. Superoxide dismutase activity in the fish homogenate was determined based on a previous study (Nishiimi et al., 1997). The reaction buffer included 2.6 mL of phosphate buffer (0.017 mM), 0.1 mL of phenazine methosulfate, and 0.1 mL of nitro blue tetrazolium mixed with the fish homogenate (0.5 mL). After adding 0.1 mL of NADH (2.34 mM), absorbance was recorded at 560 nanometers for 3.5 minutes. Glutathione peroxidase activity in the fish homogenate was assessed according to a previous study (Pagalia &#38; Valentine, 1967). The reaction buffer (0.88 mL) included GSH (1 mM), NADPH (150 mM), and sodium azide (100 mM) mixed with the fish sample (20 &#181;L). Absorbance was recorded at a wavelength of 340 nanometers for 1 minute. The normality of the data and the homogeneity of variances were analyzed using the Kolmogorov-Smirnov test and Levene&#39;s test, respectively. A one-way analysis of variance (ANOVA) was conducted to assess significant differences among treatments. Tukey&#39;s post-hoc tests were employed to evaluate differences between treatments. These analyses were performed using SPSS 22 software (SPSS, Richmond, VA, USA) with a 95% confidence level.
Results
The results showed that the final weight, weight gain and specific growth rate were significantly influenced by LA and FA, with the T3 treatment resulting in the highest growth observed. Furthermore, levels of total immunoglobulin, IgM, and lysozyme increased in fish fed diets containing FA or LA. Additionally, malondialdehyde (MDA) activity was reduced by the experimental diets, with its lowest value significantly observed in the T3 treatment compared to the control group. Fish fed diets containing LA and/or FA also displayed significant increases in catalase (CAT), superoxide dismutase (SOD), and glutathione peroxidase (GPx) activity compared to the control group. The findings suggest that these nutritional supplements at optimal doses have potential to enhance growth as well as innate immunity and antioxidant factors in goldfish. Furthermore, both supplements exhibited synergistic effects; therefore, it is recommended to use these compounds simultaneously for sustainable aquaculture practices.
Discussion and conclusion
Our results showed that supplementing with FA and/or LA can significantly activate antioxidant activity, effectively scavenging excess free radicals and regulating ROS balance in the body, thereby enhancing antioxidant potential. In this study, the beneficial effects of the probiotic&#160;Lactobacillus acidophilus&#160;and the polyphenol ferulic acid were examined in carp fish. These additives in the diet had potential effects on growth, immune factors, and antioxidant capacity in carp, and simultaneous use of these compounds is recommended for sustainable aquaculture.
Conflict of Interest
Authors have no conflict of interest.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>65</FPAGE>
			<TPAGE>77</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2024/11/192024/10/32025/01/262024/09/19
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1403/6/29
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/302025/04/302025/04/302025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>معصومه</Name>
				<MidName></MidName>
				<Family>بحرکاظمی</Family>
				<NameE>Masoumeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Bahrekazemi</FamilyE>
				<Organizations>
				<Organization>گروه گروه شیلات، واحد قائمشهر، دانشگاه آزاد اسلامی، قائمشهر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>ma.bahrekazemi@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Feed addative</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>goldfish</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>immunity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>antioxidant</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مکمل غذایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماهی قرمز</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ایمنی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آنتی‌اکسیدان</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ شناسایی و اولویت‌بندی شاخص‌های عملکرد تعاونی‌های صیادی استان خوزستان</TitleF>
		<TitleE>Identification and prioritization of performance indicators for fisheries cooperatives in Khuzestan Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تعاونی&#8204;های صیادی از رایج&#8204;ترین تشکل&#8204;های مردم&#8204;نهاد فعال در نواحی ساحلی کشور هستند که عموماً برای تأمین احتیاجات شغلی و اقتصادی اعضای خود فعالیت می&#8204;کنند. استان خوزستان همواره با ظرفیت&#8204;های صیادی برجسته شناحته می&#8204;شود. فعالیت بخش عمده&#8204;ای از صیادان استان خوزستان به&#8204;نحوی با تعاونی&#8204;&#8204;های صیادی در ارتباط است، پژوهش حاضر با هدف شناسایی و اولویت&#8204;بندی مهم&#8204;ترین شاخص&#8204;های موثر در عملکرد شرکت&#8204;های تعاونی&#8204; صیادی استان خوزستان طی سال&#8204;های 1403-1401 انجام گرفته است. این پژوهش با بهره&#8204;گیری از روش&#8204;های مطالعاتی، مصاحبه محور (تکنیک دلفی) و توزیع پرسشنامه محقق ساخته در میان فعالان حوزه صیادی صورت گرفته است، روایی پرسشنامه براساس شیوه روایی&#8204;سنجی محتوایی و پایایی گویه&#8204;ها با آلفای کرونباخ 88/0 محرز گردید. خبرگان براساس روش نمونه&#8204;گیری سیستماتیک خوشه&#8204;ای گزینش شدند. مهم&#8204;ترین عوامل گزینش، داشتن سابقه کار اجرائی-مدیریتی در بخش شیلات کشور، صنعت صید یا تعاونی&#8204;های صیادی بود. جوامع آماری شامل دو گروه مجزای هیئت خبرگان و صیادان فعال تعاونی&#8204;های صیادی بودند. تحلیل شاخص&#8204;های عملکردی شناسایی شده با استفاده از مدل آماری (تحلیل عاملی تأییدی) انجام گرفت. براساس نتایج حاصل، شاخص&#8204;های تبیین&#8204;کننده عملکرد تعاونی&#8204;های صیادی استان خوزستان به&#8204;ترتیب اهمیت در قالب هفت عامل شامل مدیریت همه&#8204;جانبه و پویا، سیاست&#8204;گذاری&#8204;های مدیریتی اجرائی و آموزشی، تأثیر اقتصادی بر عملکردهای اجتماعی، کنشگری در ارائه تسهیلات،کنشگری در تعاملات اجتماعی با اعضا و بخش&#8204;های سرمایه&#8204;گذار، کنشگری در ارائه خدمات زیربنایی و نظارت بر وضعیت صید تعریف شدند که در مجموع 2/62 درصد از تغییرات واریانس کل متغیرها را تبیین نمودند. بر اساس نتایج حاصله، بازنگری در شیوه&#8204;های مدیریتی و افزایش نظارت بر وضعیت شغلی-اقتصادی فعالان تعاونی&#8204;های صیادی می&#8204;تواند به شکل معنی&#8204;داری در بهبود عملکرد این تشکل&#8204;ها تأثیرگذار باشد. اهتمام دستگاه&#8204;های مسئول و متولی بر بهبود عملکرد و وضعیت این شرکت&#8204;ها نیز باید با در نظرگرفتن عوامل استخراجی صورت پذیرد، زیرا عوامل مذکور دارای بیشترین تأثیر در وضعیت عملکردی این تعاونی&#8204;ها خواهد بود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
The fishing industry contributes significantly to global and national food production and economies. Fishing accounts for a substantial portion of global aquatic production (FAO, 2022), highlighting the importance of effective fishing management. In Iran, Khuzestan province, with its extensive coastline and abundant water resources, is a key player in the national fishing sector (Geological Survey and Mineral Explorations of Iran, 2016; Iran Fishing Organization, 2021). Fishery cooperatives, as non-governmental organizations, aim to improve the livelihoods of fishermen by providing various services, including access to resources, financial assistance, and professional support (Islamic Republic of Iran, 1971). However, the performance of these cooperatives varies, and understanding the factors that influence their effectiveness is crucial for policy-making and sustainable development (Olquner et al., 2015; Sari and Rahmayanti, 2022).
Methodology
This research employed a mixed-methods approach, combining qualitative and quantitative methods. The initial exploratory phase involved in-depth interviews with 15 experts in the fishing sector, including managers of cooperatives, government officials, and researchers (Hsu and Sandford., 2007). These interviews, lasting approximately 40 minutes each, aimed to identify key performance indicators of fishing cooperatives. The experts were selected using a systematic cluster sampling method, based on their experience in the fishing sector, fishing industry, or fishing cooperatives (Acharya et al., 2013). A single-round Delphi technique was used to refine the identified indicators.
Based on the interview data and a literature review, a five-point Likert scale questionnaire was developed to assess the importance and prioritization of the identified performance indicators among the fishing community (Boateng et al., 2018). The questionnaire&#8217;s validity was assessed using content validity, and its reliability was confirmed with a Cronbach&#39;s alpha coefficient exceeding 0.8 (Taber, 2018). The target population comprised over 100,000 active fishermen in Khuzestan&#39;s coastal fishing cooperatives. A sample size of 384 was determined using the Krejcie-Morgan table, and the questionnaires were distributed across various fishing areas and wharves in the coastal cities of Khuzestan (Cochran, 1977).
Results 
The interviews identified over 45 items representing performance indicators, categorized into four main groups: economic, social, managerial, and legal. These items were then used to develop the questionnaire. Statistical analysis, including the Kaiser-Meyer-Olkin (KMO) test (0.858) and Bartlett&#39;s test of sphericity (3591.90, p &#60; 0.001), confirmed the suitability of the data for factor analysis. Seven main factors were extracted, explaining 62.2% of the total variance. These factors, ranked by their eigenvalue variance, were: (1) multi-dimensional and dynamic management (24.26%), (2) managerial executive and educational policies (9.94%), (3) economic impact on social performance (8%), (4) activity in providing facilities (5.4%), (5) activity in social interactions with members and investors (4.85%), (6) activity in providing infrastructure services (4.27%), and (7) monitoring fishing status (3.48%).
Discussion and conclusion 
The study revealed that multi-dimensional management is the most influential factor determining the performance of fishery cooperatives in Khuzestan, significantly outweighing the other six identified factors. This emphasizes the critical role of comprehensive management in overseeing various aspects of cooperative performance, including economic outcomes, resource allocation, environmental considerations, educational and cultural activities, policy development, and support from government institutions (Unal et al., 2011; Olquner et al., 2015). The influence of management on other performance aspects, especially economic performance, prioritization of available resources, environmental considerations, educational and cultural performance, the level of facilitating laws for fishing cooperatives, and the level of support from institutions, all reflect the undeniable importance of management as the most important indicator in explaining the performance of a cooperative-based organization in the fishing industry (Mahazril&#8217;aini et al., 2012). Educational and cultural activities, along with the provision of economic benefits to members (to improve social indicators), were identified as other crucial performance indicators. Training and awareness programs for both cooperative members and managers are essential for improving the effectiveness of these organizations (Unal et al., 2011). Implementing mandatory training courses for cooperative managers and organizing awareness programs for cooperative members regarding laws, regulations, best fishing practices, and interaction with cooperative management can significantly enhance their performance (Mahazril&#8217;aini et al., 2012). The study also highlighted several shortcomings and inefficiencies in the fishery cooperatives of southern Iran. Previous studies have shown that these organizations lack a significant impact on economic, social, cultural, and infrastructural development (Samian et al., 2017). This necessitates a focus on improving their performance. Iranian constitutional principles and development plans emphasize the importance of economic participation through the expansion of the cooperative and private sectors (Islamic Consultative Assembly, 2023). Economic pressures from declining fish stocks and reduced income, due to various factors such as government policies and environmental issues, affect social interactions between cooperatives and their members (Ilsovay et al., 2024). These shortcomings can discourage membership and increase the desire for career change, especially among younger generations (Unal et al., 2011).
While the remaining four factors (providing facilities, social interactions, providing infrastructure, and monitoring fishing) were less influential than the top three, they are still important for overall performance. The level of welfare, economic, technical, and educational facilities provided by the cooperative, the influence of cooperative managers among investors, the cooperative&#39;s role in creating and maintaining fishing infrastructure, and the awareness of cooperative managers regarding catch volumes, income, and daily fishing challenges are all significant factors (Ghanbarzadeh et al., 2021). This study&#8217;s findings provide valuable guidance for understanding the functioning and priorities of fishery cooperatives in Khuzestan. They can be used for future research, performance evaluations, and policy-making. The fishermen participating in the study frequently expressed concerns about the management of their cooperatives, citing chronic infrastructure deficiencies and a lack of fundamental changes over the years. Periodic changes in the board of directors can promote management dynamism and introduce new ideas, which can help address these long-standing issues (Unal et al., 2011). Cooperative management should also balance economic interests and social objectives, avoiding becoming solely profit-oriented or simply focused on basic member needs (Dogarawa, 2010). Increased monitoring of the fishing industry and the working conditions, technical resources, infrastructure, and welfare of fishermen is necessary. The identification of key performance indicators can guide improvements by the government and relevant agencies. The presence of fishermen in cooperatives is beneficial, as cooperatives act as intermediaries between fishermen and the government, potentially increasing the attention of responsible institutions to the occupational and economic status of those working in the fishing industry (Anggrainie and Mardhatillah, 2024). Finally, based on the research results, it is recommended that relevant authorities, such as the Iran Fishing Organization and the Ministry of Cooperatives, Labor, and Social Welfare, take steps to address the challenges faced by fishermen, particularly by improving the management of Khuzestan&#39;s fishery cooperatives. These authorities should also focus on empowering these cooperatives to provide economic facilities, effective training, and awareness programs to the fishing community. By expanding executive and research programs in this area, the problems of coastal fishing communities in this important region of Iran can be alleviated.
Acknowledgements 
This article is derived from project number 59314, dated 15 January 2024, conducted by Khorramshahr University of Marine Science and Technology in collaboration with the Khuzestan Province Department of Cooperatives, Labour, and Social Welfare. The authors express their gratitude to the Department and the University for their support.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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		<RECEIVE_DATE_FA>
			1403/10/28
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/302025/04/302025/04/302025/04/302025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>پوریا</Name>
				<MidName></MidName>
				<Family>زنگنه رضایی</Family>
				<NameE>Poriya</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Zangeneh rezaie</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع‌طبیعی دریا، دانشگاه علوم و فنون دریایی خرمشهر، خرمشهر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>poriyasilver@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>خسروی زاده</Family>
				<NameE>Mohammad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Khosravizadeh</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع‌طبیعی دریا، دانشگاه علوم و فنون دریایی خرمشهر، خرمشهر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>mohamad.27kh@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نیما</Name>
				<MidName></MidName>
				<Family>شیری</Family>
				<NameE>Nima</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shiry</FamilyE>
				<Organizations>
				<Organization>پژوهشکده اکولوژی خلیج فارس و دریای عمان، مؤسسه‌ی تحقیقات علوم شیلاتی کشور، سازمان آموزش و ترویج کشاورزی، بندرعباس، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>nima.shiry@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>زهرا</Name>
				<MidName></MidName>
				<Family>خوشنودی‌فر</Family>
				<NameE>Zahra</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Khoshnodifar</FamilyE>
				<Organizations>
				<Organization>بخش تحقیقات اقتصادی و اجتماعی، مرکز تحقیقات و آموزش کشاورزی و منابع‌طبیعی استان مرکزی، اراک، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>khoshnodifz@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رضا</Name>
				<MidName></MidName>
				<Family>عباسپور نادری</Family>
				<NameE>Reza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Abbaspour naderi</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، معاونت دفتر امور صید شیلات ایران، سازمان شیلات ایران، تهران، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>R_naderimail@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Fisheries cooperative</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fishing industry</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fisheries</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>factor analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>performance index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>دلفی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تعاونی صیادی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>صنعت صیادی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شیلات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحلیل عاملی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص عملکرد</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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Cooperative management: Balancing economic interests and social objectives. Journal of Cooperative Studies, 43(2), pp. 45-60. DOI: https://doi.org/10.2139/ssrn.1622149##Esfandiari, Ch., and Mir Abbasi, B., 2012. The Role of the United Nations in Achieving Food Security in the Global Community. Journal of Food Science and Nutrition, 9(2): 91-103. (In Persian)##FAO, 2022. The State of World Fisheries and Aquaculture 2020. Sustainability in action. Rome, Italy.##Geological Survey and Mineral Explorations of Iran, 2016. Roadmap of Earth Sciences and Mining in Khuzestan Province. National Geosciences Database. (In Persian)##Geological Survey and Mineral Explorations of Iran, 2016. Roadmap for Earth Sciences and Mining in Khuzestan Province, National Geoscience Database of Iran. (In Persian)##Haghi-Vayeghan, A. and Ghanbarzadeh, M., 2022. Estimation of Fisheries Reference Points of Spotted Spanish Mackerel (Scomberomorus guttatus Bloch &#38; Schneider, 1801) Using Catch-Maximum Sustainable Yield (CMSY) and Bayesian Surplus Production Model (BSM) in Southern Waters of Iran (Persian Gulf and Oman Sea). Journal of Fisheries, 75(1), pp. 31-47. DOI: https://doi.org/10.22059/jfisheries.2021.326498.1268 (In Persian)##Hosseinnejad, M., Hosseini Nia, Gh., and Vazifehdoust, H., 2020. Designing a Sustainable Business Model for Entrepreneurial Cooperatives Based on Key Entrepreneurship Components. Journal of Development and Transformation Management, 12(42): 19-34. (In Persian)##Ilosvay, X.É.E., Molinos, J.G., Tovar-Ávila, J., Bravo, J.R., Santiago, I.A.M., Aceves-Bueno, E. and Ojea, E., 2024. Determinants of small-scale fisheries’ transformative responses under increasing climate change impacts in Nayarit, Mexico. Ecology and Society, 29(4). DOI: https://doi.org/10.5751/ES-15661-290438##Iran Fisheries Organization, 2021. Statistical Yearbook of Iran Fisheries Organization (2016-2021), Deputy of Planning and Resource Management, Office of Planning and Budget, Planning and Statistics Group, 29 pp. (In Persian)##Islamic Consultative Assembly, 2023. Seventh Five-Year Development Plan of the Islamic Republic of Iran (2024-2028). National Information Center for Laws and Regulations of Iran. (In Persian) https://dotic.ir/news/11497##Islamic Parliament Research Center, 2006. A Review of the Status of Iran Fisheries Organization. Office of Infrastructure Studies. (In Persian)##Karbasi, A., and Mohammadzadeh, H., 2017. Factors Affecting Food Security with Emphasis on the Role of Agricultural Sustainability in Iran. Third National Student Conference on Agricultural Economics, 19-20 March, Guilan, Iran. (In Persian)##Kian, F., Farhadiaan, H., and Chubchian, Sh., 2016. Investigating Food Security of Urban Households in Alborz Province. Iranian Journal of Food Science and Technology, 13(55): 167-179. (In Persian)##Mahazril‘Aini, Y., Hafizah, H.A.K. and Zuraini, Y., 2012. Factors affecting cooperatives’ performance in relation to strategic planning and members’ participation. Procedia - Social and Behavioral Sciences, 65, pp. 100-105. DOI: https://doi.org/10.1016/j.sbspro.2012.11.098##Mohammadnejad Shamushki, M., Dardiei, Kh., Rezaei Shirazi, A., and Yahyai, M., 2013. A Study on the Catch Trends of Three Years of Whitefish (Rutilus frisii kutum), Mullet (Liza spp), and Carp (Cyprinus carpio) in Golestan, Mazandaran, and Gilan Provinces (2009-2011). Journal of Aquatic Animals and Fisheries, 4(15): 27-38. (In Persian)##Olguner, M.T., Yılmaz, S. and Şen, E.B., 2015. The Place and Importance of Fishery Cooperatives in Aquaculture Marketing in Turkey: The Case of Antalya. International Journal of Development Research, 5, pp. 3149-3151.##Samian, M., Saadi, H., Asadi, M., Mirzaei, K., Ansari, E., Ahmadihagh, E. and Soleymani, A., 2017. The role of fishing cooperatives on social–Economic and cultural development of rural areas of Bord Khun city of Bushehr, Iran. Journal of the Saudi Society of Agricultural Sciences, 16(2), pp. 178-183. DOI: http://dx.doi.org/10.1016/j.jssas.2015.06.001##Sapovadia, V.K., 2004. Fisherman cooperatives: a tool for socio-economic development. In: International Institute of Fisheries Economics &#38; Trade Conference.##Sardoeinasab, M. and Aghamohammadi, A, 2015. Comparative possibility of carrying out commercial activities in the form of co-operative on the basis of I.C.A approaches. Journal of Comparative Law, 6(2), pp. 569-600. https://doi.org/10.22059/jcl.2015.55776. (In Persian)##Sari, D.K. and Rahmayanti, A.Y., 2022. Fishery Cooperatives and Sustainable Blue Economy: Scoping Review from a Business Perspective. Multidisciplinary Digital Publishing Institute Proceedings, 83(1), p. 30. DOI: https://doi.org/10.3390/proceedings2022083030##Ünal, V., Yercan, M. and Günden, C., 2011. The status of fishery cooperatives along the Aegean Sea coast (Turkey). Journal of Applied Ichthyology, 27(3), pp. 854-858. DOI: https://doi.org/10.1111/j.1439-0426.2011.01794.x## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>مقاله علمی – پژوهشی:‌ تنوع زیستی، پراکنش و فراوانی زوپلانکتون تالاب انزلی طی سال‌های 1402-1401: مطالعه مقایسه‌ای با دهه پیشین</TitleF>
		<TitleE>Zooplankton biodiversity, distribution, and abundance in Anzali Wetland in 2023: A comparative study with previous decade</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>مطالعه حاضر طی سال&#8204;های 1401 و 1402 در تالاب انزلی انجام شد. هدف از این مطالعه، بررسی تغییرات زمانی و مکانی جامعه زوپلانکتونی در تالاب انزلی و مقایسه آن با مطالعات پیشین بود. نتایج نشان داد، تعداد 58 جنس زوپلانکتون در تالاب انزلی شناسایی گردید، بیشترین جنس متعلق به شاخه روتیفرا با 28 جنس بود. از بین گروه&#8204;های زوپلانکتون 11 جنس از پروتوزوآ و 12 جنس از شاخه آرتروپودا شناسایی شدند. از بین شاخه&#8204;های زوپلانکتونی روتیفرا با میزان فراونی 38&#177; 148 عدد در لیتر بیشترین بودند، سپس پروتوزوآ با فراوانی 11&#177; 81 عدد در لیتر و آرتروپودا با فراوانی 12&#177; 72 عدد در لیتر در رده&#8204;های بعدی قرار داشتند. میانگین فراوانی کل زوپلانکتون 48 &#177; 305 عدد در لیتر بود که در مقایسه با سال&#8204;های 1381- 1380 به میزان 7 برابر (2300- 2200 عدد در لیتر) و سال&#8204;های 1394- 1393 (4000 عدد در لیتر) به میزان 13 برابر کاهش داشت. فراوانی روتیفرا و پروتوزوآ در سال 1402- 1401 به&#8204;ترتیب 13 و 19 برابر در مقایسه با سال 1394- 1393 کاهش داشت. جنس&#8204;های غالب Brachionus و Rotatia از روتیفرا، جنس Centopyxis و Arcella از پروتوزوآ و جنس Cyclocypris و گروه Copepoda از آرتروپودا بودند. بیشترین میانگین فراوانی زوپلانکتون در منطقه تالاب غرب با فراوانی 127&#177;612 عدد در لیتر مشاهده شد. به&#8204; طورکلی، کاهش چشمگیر در تنوع و جمعیت ذخایر زوپلانکتونی در تالاب انزلی نشان&#8204;دهنده حذف تدریجی حلقه زنجیره غذایی تولید کنندگان اولیه و ثانویه در قسمت پایین هرم اکولوژی بوده است که نابودی گونه&#8204;های بومی و ذخایر آبزیان به&#8204;خصوص ماهیان اقتصادی تالاب را به&#8204;همراه خواهد داشت.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Introduction
The Anzali Wetland is located along the southwestern coast of the Caspian Sea and was the first wetland in Iran to be registered on the Ramsar Convention&#39;s list. However, it was soon added to the Montreux Record due to ecological concerns (Mirzajani et al., 2020). Zooplankton is a crucial link in the wetland&#39;s food chain, play an important role as secondary producers and serve as a primary food source for aquatic animals. Planktonic communities are highly responsive to environmental changes, their population structure is strongly influenced by nutrient levels in the water in the water (Mulani et al., 2006; Boyd, 2007; Bagheri et al., 2017). Following the invasion of the water hyacinth plant, a decline in the Caspian Sea&#39;s water level, and reduced rainfall and river inflow due to climate change, this study represents the most recent investigation into the temporal and spatial distribution of zooplankton in the Anzali Wetland. The objective of this study was to assess the biodiversity, composition, and density of zooplankton in the Anzali Wetland in 2023, compare the findings with previous research, and evaluate the broader ecological changes over time.
Materials and methods
The Anzali Wetland is located at 37&#186; 28&#39; N latitude and 49&#186; 25&#39; E longitude, with a maximum depth rarely exceeding one meter. Zooplankton sampling was conducted in March, May, June, August, October, November, and December 2023 at 14 stations. Sampling took place over three days each month using boats with engine powers of 85 and 25 horsepower. A Ruttner Water Sampler was employed for zooplankton collection. The collected samples (30 liters) were passed through a 55-micron zooplankton net, and the water retained in the net was transferred to 300 cc polyethylene bottles. The samples were then fixed with 4% formalin and transported to the plankton laboratory for quantitative and qualitative analysis (APHA, 2005).
In the plankton laboratory, after homogenization, 5 ml of the sample was transferred using a pipette to 5 ml counting chambers (KIEL Hydro-Bios). After 24 hours of sedimentation, the samples were identified and counted under an inverted microscope (F-S Leitz-LABOVERT). Zooplankton density was calculated as the number of individuals per liter of water. The methods for sampling and determining zooplankton density were based on APHA (2005) and Ruttner-Kolisko (1974), while zooplankton identification followed the keys of Thorp and Covich (2001) and Pontin (1978).
Results
In this study, 58 genera from four zooplankton groups were identified in the Anzali Wetland. The highest number of genera belonged to the phylum Rotifera, with 28 genera. This was followed by Arthropoda and Protozoa, with 12 and 11 genera, respectively. In terms of abundance, Rotifera was the dominant group, accounting for 48% of the total zooplankton population (148 individuals per liter). Protozoa ranked second with 26% (81 ind.l⁻&#185;), followed by Arthropoda with 24% (72 ind.l⁻&#185;). Other zooplankton groups made up the remaining 2%. The average total zooplankton abundance in the Anzali Wetland was estimated at 305 individuals per liter.
The genera Cyclops and Cyclocypris (phylum Arthropoda) were observed across all areas of the Anzali Wetland. From the phylum Rotifera, the genera Brachionus, Cephalodella, Philodina, and Rotaria were consistently found throughout the wetland, showing a 100% observation frequency. The highest zooplankton abundance was recorded in June, with an average of 652&#177;208 ind.l⁻&#185;, while the lowest values were observed in October (142&#177;36 ind.l⁻&#185;) and November (155&#177;37 ind.l⁻&#185;).
Among the zooplankton groups, Rotifera showed the highest abundance, reaching an average of 405 &#177; 188 ind.l⁻&#185; in June, with the lowest abundance being 20&#177;5 ind.l⁻&#185; in other months. The abundance of Arthropoda ranged from 120&#177;44 ind.l⁻&#185; in June to 27&#177;11 ind.l⁻&#185; in November. Statistical analysis revealed a significant difference (P&#60;0.05) in zooplankton abundance among different phyla and sampling months.
Spatial analysis showed that the western region of the Anzali Wetland had the highest average zooplankton abundance at 613&#177;128 ind.l⁻&#185;, while the lowest abundance was recorded at the wetland outlet (116&#177;31 ind.l⁻&#185;). The maximum abundance of Rotifera ranged between 206 and 335 ind.l⁻&#185; in the western and eastern regions, respectively. The highest Arthropoda abundance (176 ind.l⁻&#185;) was also observed in the western region. The abundance of Protozoa varied between 41 ind.l⁻&#185; in Siah Keshim and 106 ind.l⁻&#185; in the central wetland.
Discussion and conclusion
Over the past 30 years, increased human activities and significant environmental and climatic changes have contributed to notable shifts in the zooplankton community of the Anzali Wetland. Biodiversity has drastically declined, with the number of zooplankton genera dropping from 87 genera in 1994 to 58 genera in 2023 (Mirzajani et al., 2009). This study reveals a more than 13-fold decrease in zooplankton density compared to the 2013-2014 period. Specifically, the abundance of Rotifera and Protozoa in 2023 was reduced by 17-fold and 19-fold, respectively (Fallahi et al., 2018).
The substantial decline in zooplankton density observed in this study suggests a disruption in the food chain within the Anzali Wetland ecosystem, which could lead to a further reduction in aquatic resources. The highest zooplankton abundance was recorded in the western wetland area, which remains the only intact section of the Anzali Wetland. However, this area has experienced significant changes, including a dramatic reduction in depth and near-total coverage by the invasive water hyacinth (Pontederia crassipes).
Several factors have contributed to the decline in zooplankton biodiversity and density in the Anzali Wetland. These include the spread of non-native water hyacinth, decreased water depth, increased sedimentation, higher rates of water evaporation, reduced flow from rivers entering the wetland, climate change, the decrease in the Caspian Sea water levels, and a lack of proper wetland management. These cumulative pressures have worsened over the past decades.
To address the issues affecting the Anzali Wetland and to restore the zooplankton community, which plays a critical role in the food chain and aquatic resources of this ecosystem, it is essential to prioritize the removal of non-native water hyacinth and accumulated sediments. Efforts should focus on the western, central, and southern areas of the wetland to help clean and increase its depth. These measures should be incorporated into the action plans of relevant executive organizations to revitalize the ecosystem.
Conflict of interest
According to the authors of this article, there is no conflict of interest.
Acknowledgment
This study was conducted in Anzali wetland with the approved code of 01051-011052-034-12-73-14. The colleagues of the ecology department, Javad Vesaghi, Yaqoub Ali Zahmtakesh, Omid Imani, and Reza Mohammadidoost, are grateful for their helps in sampling and laboratory works.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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		<RECEIVE_DATE_FA>
			1403/9/21
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2025/04/302025/04/302025/04/302025/04/302025/04/302025/04/30
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/2/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سیامک</Name>
				<MidName></MidName>
				<Family>باقری</Family>
				<NameE>Siamak</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Bagheri</FamilyE>
				<Organizations>
				<Organization>پژوهشکده آبزی پروری آبهای داخلی، موسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، بندرانزلی، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Sia_Bagheri@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علیرضا</Name>
				<MidName></MidName>
				<Family>میرزاجانی</Family>
				<NameE>Alireza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mirzajani</FamilyE>
				<Organizations>
				<Organization>پژوهشکده آبزی پروری آبهای داخلی، موسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، بندرانزلی، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>Siamakbp@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جلیل</Name>
				<MidName></MidName>
				<Family>سبک آرا</Family>
				<NameE>Jalil</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sabkara</FamilyE>
				<Organizations>
				<Organization>پژوهشکده آبزی پروری آبهای داخلی، موسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، بندرانزلی، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>jsabkara@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهرداد</Name>
				<MidName></MidName>
				<Family>نصری تجن</Family>
				<NameE>Mehrdad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Nasri Tajan</FamilyE>
				<Organizations>
				<Organization>گروه شیلات، دانشگاه آزاد اسلامی واحد بندرانزلی، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>Iran</Country>
				</Countries>
				<EMAILS>
				<Email>nasri_mehrdad@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Zooplankton</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Planktonic population</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Biodiversity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Anzali Wetland</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زوپلانکتون</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جمعیت پلانکتونی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تنوع زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تالاب انزلی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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DOI: 10.22092/ISFJ.2019.118317 (In Persian).##Bagheri, S., Mashhor, M., Makaremi, M., Mirzajani, A., Babaei, H., Negarestan, H. and Wan-Maznah, W.O., 2010. Distribution and composition of phytoplankton in the southwestern Caspian Sea during 2001–2002, a comparison with previous surveys. World Journal Fish and Marine Sciences, 2: 416–426.##Bagheri, S., Niermann, U., Mansor, M., and Yeok, S. W. 2014. Biodiversity, distribution and abundance of zooplankton in the Iranian waters of the Caspian Sea off Anzali during 1996–2010. Journal of the Marine Biological Association UK, 94 (1):129–140. DOI: 10.1017/S0025315413001288##Bagheri, S., Sabkara, J., Yousefzad, E. and Zahmatkesh, Y. 2017. Ecological study of zooplankton communities in the Persian Gulf Martyrs Lake (Chitgar–Tehran) and the first report of the freshwater jellyfish Craspedacusta sp. (Cnidaria, Limnomedusae) in Iran. Iranian Scientific Fisheries Journal, 25 (5): 113–127. DOI: 10.22092/ISFJ.2017.110319.  (In Persian).##Boyd, P. 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Comprehensive fisheries studies of Anzali wetland. Guilan Province Fisheries Research Center. Technical Report, IFRO. Anzali. 204 P. (In Persian)##Khorasani, N. and Meygooni, G., 1987. Anzali wetland ecosystem survey. Journal of Natural Resources of Iran, 41(5): 44-53. (In Persian)##Kimball, K.D. and Kimball, S.F., 1995. Limnological studies of Anzali wetland. Iran Fisheries Company and Iran Environmental Protection Organization. Technical Report, IFRO. Anzali. 144 P. (In Persian).##Krebs, C.J., 1994. Ecological methodology. Second edition, U.K: An imprint of Addison Wesley Longman, UK. 620 P.##Mirzajani, A., Ghane, A., Bagheri, S., Abbasi, K., Sayadrahim, M., Salahi, M. and Lavajoo, F., 2020. Diet survey and trophic position of Macrobrachium nipponense in the food web of Anzali Wetland. Wetlands, 40 (5): 1229–1239. DOI: 10.1007/s13157-020-01278-5. ##Mirzajani, A., Roohi, J. and Mohammadidoost, R., 2019. Investigation of distribution and density of dominant aquatic plants in the western part of Anzali Lagoon. Journal of Plant Research, 33 (4): 1014–1024. (In Persian).##Mirzajani, A.R., Kiabi, B., Jamalzadeh, F., Fallahi, M., Kamali, A., Abdollahpour, H., Pourgholami M. A., Makaremi, M., Vatandoost, M., Babaei, H. and Abbasi, K., 2009. Limnological survay of Anzali wetland data during 1990-2003 by use of GIS system. Iranian Fisheries Science Research Institute, Iran. 124 P. (In Persian).##Mulani, S.K., Mule, M.B. and Patil, S.U., 2006. Studies on Water Quality and Zooplankton Community of Panchganga River in Kolhapur City. Journal of Environmental Biology, 30: 455-459. ##Nasrollahzadeh Saravi, H., Pourang, N., Foong, S.Y. and Makhlough, A., 2019. Eutrophication and trophic status using different indices: A study in the Iranian coastal waters of the Caspian Sea. Iranian Scientific Fisheries Journal, 18 (3): 531–543. DOI: 10.22092/ijfs.2018.117717.##Nezami, S., 1994. Limnological and ecological investigations of Anzali lagoon. Fisheries Research Organization for Guilan Province. Technical Report, IFRO. Iran. 214 P. (In Persian)##Piasecki, W., Goodwin A.E., Eiras J.C. and Nowak B.F., 2004. Importance of copepod in##Freshwater  aquaculture. Zoological Studies, 43 (2): 193–205.  ##Pontin, R. M., 1978. A key to fresh water planktonic and semiplanktonic Rotifera of the British Isles. Titus Wilson and son Publication,UK. 178 P.##Richardson, A J. 2008. In hot water: zooplankton and climate change. ICES Journal of Marine Science, 65: 279–295. DOI: 10.1093/icesjms/fsn028.##Roohi, A., Yasin, Z., Kideys, A.E., Hwai, A.T., Khanari, A.G. and Eker-Develi, E., 2008. Impact of a new invasive ctenophore (Mnemiopsis leidyi) on the zooplankton community of the Southern Caspian Sea. Marine Ecology, 29: 421–434. DOI: 10.1111/j.1439-0485.2008.00254.x##Ruttner-Kolisko, A., 1974. Plankton Rotifera biology and taxonomy. Verlagsbuchhandlung (Nagele U. Obermiller), Germany. 134 P.##Sabkara, J and Makaremi, M., 2015. The Atlas of plankton Anzali wetland and Caspian Sea Costal Waters. Iranian Fisheries Science Research Institute, Tehran. 656 P. (In Persian).##Sabkara, J. and Makaremi, M., 2004. Abundance and distribution pattern of planktons in Anzali Lagoon. Iranian Scientific Fisheries Journal, 13(3): 87–114. DOI: 10.22092/isfj.2004.113804. (In Persian)##Salveson, E., 2013. Effect of copepod density and water exchange on the egg production of Acartia tonsa Dana (Copepoda: Calanoida) feeding on Rhodomonas baltica. Norwegian University of Science, Norway. 154 P.##Thorp, J.H. and Covich, A.P., 2001. Ecology and classification of North American freshwater invertebrates. Academic Press, New York . 1056 P.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

</ARTICLES>

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