<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1404</YEAR>
<VOL>14</VOL>
<NO>2</NO>
<MOSALSAL>52</MOSALSAL>
<PAGE_NO>102</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>ارزیابی جامع چرخه حیات فرش دستباف و آثار محیط‌ زیستی آن: مطالعه موردی استان فارس</TitleF>
		<TitleE>Comprehensive Life Cycle Analysis of Handwoven Carpets and Its Environmental Impact: A Case Study of Fars Province Carpets</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>پژوهش حاضر با هدف ارزیابی پایداری محیط&#8204;زیستی صنعت فرش دستباف استان فارس، با استفاده از روش&#8204;شناسی ارزیابی چرخه حیات &#160;با رویکرد از گهواره تا گور و مدل&#8204;سازی در نرم&#8204;افزار SimaPro انجام شده است. نتایج نشان می&#8204;دهد که فاز تولید با سهم 60 درصدی از کل پیامدها، نقطه داغ اصلی این چرخه محسوب می&#8204;شود. اگرچه این محصول با انتشار تنها 8 کیلوگرم CO2-eq به ازای هر مترمربع، از مزیت کربنی بالایی نسبت به نمونه&#8204;های ماشینی برخوردار است، اما اتکا به روش&#8204;های سنتی رنگرزی و فقدان مدیریت پساب، شاخص سمیت انسانی را به سطح نگران&#8204;کننده 2/2 کیلوگرم معادل ۱و۴-دی&#8204;کلروبنزن (kg 1,4-DCB eq) می&#8204;رساند. افزون بر این، مصرف آب معادل 100 لیتر بر مترمربع و نرخ دفن 60 درصدی ضایعات، حاکی از بهره&#8204;وری پایین منابع و غلبه اقتصاد خطی بر این صنعت است. در نتیجه، دستیابی به پایداری جامع مستلزم گذار از تولید سنتی متکی بر طبیعت به مدیریت مهندسی&#8204;شده و سبز است؛ هدفی که از طریق جایگزینی رنگزاهای سازگار با محیط&#8204;زیست، استقرار سیستم&#8204;های تصفیه پساب و پیاده&#8204;سازی سیاست مسئولیت توسعه&#8204;یافته تولیدکننده (EPR) برای مدیریت بهینه ضایعات محقق خواهد شد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The current study evaluates the environmental sustainability of the hand-woven carpet industry in Fars province using Life Cycle Assessment (LCA) with a cradle-to-grave approach, modeled in SimaPro software. Results show that the production phase accounts for 60% of total environmental impacts, making it the primary hotspot. Although the product emits only 888 kg CO2-eq per square meter&#8212;showing a significant carbon advantage over machine-made alternatives&#8212;reliance on traditional dyeing methods and lack of wastewater management have increased human toxicity to 2.2 kg 1,4-DCB eq. Additionally, water consumption reaches 100 liters per square meter, and with 60% of waste landfilled, resource efficiency is low, reflecting a linear economic model. To achieve sustainability, a shift from traditional, nature-dependent production toward eco-friendly, engineered management is essential. This can be accomplished by replacing conventional dyes with eco-friendly alternatives, establishing wastewater treatment systems, and implementing Extended Producer Responsibility (EPR) policies for better waste management. These measures can help reduce environmental impacts, promote resource efficiency, and support a more sustainable industry in Fars province.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>24</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/28
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/8/6
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/19
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/10/29
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سعیده</Name>
				<MidName></MidName>
				<Family>رفیعی</Family>
				<NameE>Saeedeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rafiei</FamilyE>
				<Organizations>
				<Organization>گروه فرش، دانشکده هنرهای صناعی، دانشگاه هنر شیراز، شیراز، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>s_rafiei@shirazartu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Comprehensive Life Cycle Analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Circular Economy</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Water Consumption</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Energy Consumption</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Carpets</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Fars Province</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحلیل جامع چرخه حیات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اقتصاد چرخشی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مصرف آب</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مصرف انرژی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فرش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استان فارس</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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Life cycle assessment of cotton textile products in Turkey, Resources, Conservation and Recycling, 104(A): 213–223. ##7.	Brown, A., Smith, J. and Johnson, K. 2021. Environmental impacts in traditional textile industries: A life cycle assessment perspective, Journal of Cleaner Production, 280: 124456. ##8.	Carmen, Z. and Daniela, S. 2012. Textile organic dyes – characteristics, polluting effects and separation/elimination procedures from industrial effluents – a critical overview’, in T. Puzyn (ed.) Organic Pollutants Ten Years after the Stockholm Convention. Rijeka: InTech, pp. 55–86.##9.	Chen, H.L. and Burns, L.D.  2006. Environmental analysis of textile products, Clothing and Textiles Research Journal, 24(3): 248-261. ##10.	Curran, M.A. ed., 2012. Life cycle assessment handbook: a guide for environmentally sustainable products. John Wiley &#38; Sons. ##11.	da Silva, A., Campos, E., Ruas, G., Rocha, G., Moris, V. and Silva, D.  2024. Life cycle assessment and circular economy: A case study of the textile processing industry’. Doctoral dissertation. Universidade Federal de São Carlos, Sorocaba Campus, Brazil.##12.	Ekvall, T. and Finnveden, G.  2001. Allocation in ISO 14041—a critical review, Journal of Cleaner Production, 9(3): 197-208. ##13.	Ellen MacArthur Foundation, 2023a. Circular Textiles Policy Toolkit. ##14.	Ellen MacArthur Foundation, 2023b. Textiles System Change: Pathways to Circularity in EU Markets. Cowes: EMF Publishing.##15.	European Environment Agency, 2022a. Circular Economy in Traditional Craft Sectors (EEA Report No. 15/2022). Luxembourg: Publications Office of the European Union. ##16.	European Environment Agency, 2022b. Sustainable Textiles: The Role of Design, Production and Consumption in a Circular Economy. Luxembourg: Publications Office of the European Union.##17.	European Union, 2024.  CircularTex Project (Grant Agreement No. 101135049): Circular Value Chains for the Textile Sector. Horizon Europe Programme.##18.	European Environment Agency (EEA), 2019. Textiles in Europe’s Circular Economy (Briefing No. 10/2019). Copenhagen: EEA. Available at: https://www.eea.europa.eu/publications/textiles-in-europes-circular-economy##19.	United Nations Industrial Development Organization (UNIDO), 2022.  Best Available Techniques for Water Recycling and Reuse in Textile Dyeing and Finishing Plants. Vienna: UNIDO Publications.##20.	Fatoohi, N., 2015. Evaluation of the life cycle of hand-woven carpets from the perspective of environmental sustainability’, Journal of Environment and Development, 8(1): 33–50. (In Persian)##21.	Finkbeiner, M., Inaba, A., Tan, R., Christiansen, K. and Kluppel, H.J. 2006. The new international standards for life cycle assessment: ISO 14040 and ISO 14044, The International Journal of Life Cycle Assessment, 11(2): 80–85. ##22.	Finnveden, G., Hauschild, M.Z., Ekvall, T., Guinee, J., Heijungs, R., Hellweg, S., Koehler, A., Pennington, D. and Suh, S. (2009) ‘Recent developments in life cycle assessment’, Journal of Environmental Management, 91(1): 1–21. ##23.	Fletcher, K. (2008) Sustainable Fashion and Textiles: Design Journeys. London: Earthscan.##24.	Gardetti, M.A. and Torres, A.L. (eds.), 2013. Sustainability in Fashion and Textiles: Values, Design, Production and Consumption. Sheffield: Greenleaf Publishing.##25.	Geyer, R., Jambeck, J.R. and Law, K.L.  2017. Production, use, and fate of all plastics ever made, Science Advances, 3(7): e1700782. ##26.	Global Organic Textile Standard, 2023. Global Organic Textile Standard (Version 7.0). GOTS International Working Group. ##27.	Guinee, J.B. (ed.), 2002. Handbook on Life Cycle Assessment: Operational Guide to the ISO Standards. Dordrecht: Kluwer Academic Publishers.##28.	Guinée, J.B., Gorrée, M., Heijungs, R., Huppes, G., Kleijn, R., de Koning, A., van Oers, L., Wegener Sleeswijk, A., Suh, S., Udo de Haes, H.A., de Bruijn, H., van Duin, R. and Huijbregts, M.A.J. 2002, Handbook on Life Cycle Assessment: Operational Guide to the ISO Standards. Dordrecht: Kluwer Academic Publishers.##29.	Günther, A. and Langowski, H.C. 1997. Life cycle assessment study on resilient floor coverings’, The International Journal of Life Cycle Assessment, 2(2), pp. 73–80. ##30.	Hosseinpour, S., Aghajani, H. and Hashemi, M. 2021. Assessment of heavy metal contamination in carpet dyeing wastewater in Iran’, Environmental Monitoring and Assessment, 193(5): 268. ##31.	International Organization for Standardization (ISO), 2019. Greenhouse Gases – Part 2: Specification with Guidance at the Project Level for Quantification, Monitoring and Reporting of Greenhouse Gas Emission Reductions or Removal Enhancements (ISO 14064-2:2019). Geneva: ISO.##32.	International Trade Centre (ITC). 2023. Sustainability Standards Map: Textiles and Handicrafts. Available at: ##33.	ISO (2006a) ISO 14040:2006 Environmental management — Life cycle assessment — Principles and framework. Geneva: International Organization for Standardization.##34.	ISO (2006b) ISO 14044:2006 Environmental management — Life cycle assessment — Requirements and guidelines. Geneva: International Organization for Standardization.##35.	Laitala, K., Klepp, I.G. and Boks, C.  2011. Changing laundry habits in Norway: Consequences for the environmental impact of clothing, International Journal of Consumer Studies, 35(2): 161–170. ##36.	Laitala, K., Boks, C. and Klepp, I.G.  2015. Making clothing last: A design approach for reducing the environmental impacts, International Journal of Design, 9(2): 93##37.	Laitala, K., Boks, C. and Klepp, I.G. 2018. Changing laundry habits in Norway, International Journal of Consumer Studies, 42(5): 481–491.##38.	Manshoven, S., Christis, M., Vercalsteren, A., Arnold, M., Nicolau, M., Lafond, E., Mortensen, L.F. and Coscieme, L.  2020. Textiles and the Environment in a Circular Economy. Copenhagen: European Topic Centre on Waste and Materials in a Green Economy (ETC/WMGE) for the European Environment Agency (EEA).##39.	Muthu, S.S. (ed.) 2014a.  Roadmap to Sustainable Textiles and Clothing: Eco-Friendly Raw Materials, Technologies, and Processing Methods. Singapore: Springer.##40.	Muthu, S.S. 2014b. Assessing the environmental impacts of textiles and clothing: A review, Journal of Cleaner Production, 68: 211–225. ##41.	Muthu, S.S.  2017. Sustainable recycling of textiles and other materials, in Sustainable Construction and Building Materials. Cambridge: Woodhead Publishing, pp. 179–190.##42.	Muthu, S.S.  2014. Assessing the Environmental Impact of Textiles and the Clothing Supply Chain. Cambridge: Woodhead Publishing. ##43.	Organisation for Economic Co-operation and Development (OECD) 2022. Extended Producer Responsibility (EPR) for Textiles: Policy Guidance and Best Practices. Paris: OECD Publishing. ##44.	Palacio, J. C., &#38; Johnston, C. S. 2020. Life cycle assessment of textile products: A review. Resources, Conservation and Recycling, 157: 104788. ##45.	Parajuly, K., Thapa, K., Cimpan, C., Laner, D. and Wenzel, H. 2020. The impact of improper disposal on the environment: A review of waste management practices in developing countries, Journal of Environmental Management, 263: 110374. ##46.	Parvaresh, F. and Amini, M.H. 2024.  Application of circular economy for sustainable waste management in the carpet industry, International Journal of Research in Industrial Engineering, 13(2): 188–206. ##47.	Pourmoradian, S., Vandshoari, A. and Omarzadeh, D. 2021. An integrated approach to assess potential and sustainability of handmade carpet production in different areas of the East Azerbaijan Province of Iran, Sustainability, 13(4): 2251. ##48.	Rebitzer, G., Ekvall, T., Frischknecht, R., Hunkeler, D., Norris, G., Rydberg, T., Schmidt, W.P., Suh, S., Weidema, B.P. and Pennington, D.W.  2004. Life cycle assessment: Part 1: Framework, goal and scope definition, inventory analysis, and applications, Environment International, 30(5): 701–720. ##49.	Russell, S.J., Waite, M. and Jewell, E.  2014. Sustainable wool production and processing’, in S.S. Muthu (ed.) Roadmap to Sustainable Textiles and Clothing: Eco-friendly Raw Materials, Technologies, and Processing Methods. Singapore: Springer, pp. 289–321. ##50.	Sandin, G. and Peters, G.M. (2018). Environmental impact of textile reuse and recycling – A review, Journal of Cleaner Production, 184: 353–365. ##51.	Sitharaj, A., Balasubramanian, A., Sivalingam, S., Kumar L., R. and Ramesh, M.  2025. Recycling aspects of eco-friendly natural fibers and polymers for the sustainable environment. In: Green Composites and Natural Fibre Reinforcements, pp. 199-220. ##52.	Tabatabaei Hanzaei, S.M. and Moblifard, E.  2021. Analysis of color and fibers strategy of raw materials in the development of green handmade carpets with structural equation modelling approach (Case study: Isfahan handmade carpets), Journal of Textile Science and Technology, 10(4): 91-108. (In Persian)##53.	Thomas, M., Yilmaz, H. and Dincer, I.  2023.  Recovery of process water in textile dyeing using hybrid nanomembrane and solar distillation systems, Journal of Water Process Engineering, 55: 104134. ##54.	United Nations Environment Programme (UNEP) 2012. Global Chemicals Outlook: Towards Sound Management of Chemicals. Nairobi: UNEP.##55.	United Nations Industrial Development Organization (UNIDO) 2022a. Benchmarking Sustainable Handicraft Production in West Asia. Vienna: UNIDO.##56.	United Nations Industrial Development Organization (UNIDO) 2022b. Closed-Loop Water Systems for Textile Dyeing: Technical Guidance for Sustainable Industry Transition. Vienna: UNIDO Publications.##57.	Van der Velden, N.M., Patel, M.K. and Vogtlander, J.G. 2014. LCA benchmarking study on textiles made of cotton, polyester, nylon, acryl or elastane, The International Journal of Life Cycle Assessment, 19(9): 331–356. ##58.	Wheeler, A.C., Rowe, J.B. and Wiedemann, S.G. 2016. A life cycle assessment of the production of wool in Australia, Journal of Cleaner Production, 127: 308-318. ##59.	Wernet, G., Bauer, C., Steubing, B., Reinhard, J., Moreno-Ruiz, E. and Weidema, B.  2016. The ecoinvent database version 3 (part I): overview and methodology, The International Journal of Life Cycle Assessment, 21(9): 1218-1230.##60.	Yaseen, D. A., &#38; Scholz, M. 2019. Textile dye wastewater characteristics and constituents of synthetic effluents: A critical review. International Journal of Environmental Science and Technology, 16(2): 1193-1226. ##61.	Zhang, L., Wang, Y. and Li, X. 2015. Recycling strategies for sustainable textile management: A review, Journal of Cleaner Production, 102: 45-56.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>پویایی عناصر غذایی لاشبرگ بلوط وی ول  (.Quercus libani Oliv)تحت تاثیر گلازنی طی دو زمان مختلف در جنگل های بانه</TitleF>
		<TitleE>Nutrient Dynamics of Lebanon Oak (Quercus libani Oliv.) Leaf Litter Affected by Pollarding at Two Different Times in Forests of Baneh</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>گلازنی در جنگل می تواند بر کمیت و پویایی عناصر غذایی لاشبرگ در طی زمان اثر به جای بگذارد. هدف این پژوهش، مقایسه اثر گلازنی بر ویژگی های شیمیایی لاشبرگ بلوط پس از خزان و نه ماه &#160;بعد بود. به این منظور، یک توده جنگلی کمتر دست خورده (آرامگاه جنگلی) و در مجاورت آن یک گلاجار واقع در روستای مجسه شهرستان بانه انتخاب گردید. در هر توده، 10 قطعه نمونه&#8204; 4 در4 متر انتخاب و نمونه های لاشبرگ، در آبان ماه و در همان قطعات نمونه در تیر ماه سال بعد برداشت شدند. در مجموع 40 نمونه لاشبرگ تهیه وخصوصیات شیمیایی شامل کربن، نیتروژن، فسفر، پتاسیم pH، EC، نسبت C/N و C/P اندازه گیری شد. نتایج نشان داد لاشبرگ های آرامگاه در ابتدای خزان در مقایسه با گلاجار از کیفیت بالاتری برخودار بود که مقدار بالاتر کربن، نیتروژن، پتاسیم و مقدار کمتر نسبت C/N بیانگر آن بود. همچنین در طی زمان، سرعت تجزیه در لاشبرگ های آرامگاه سریع تر از گلاجار بود. به طور کلی می توان گفت با گلازنی و کاهش حجم برگ در فصل رویش و همچنین کاهش لاشبرگ در فصل خزان، شرایط خرد اقیلم در زیر درختان تحت تاثیر قرار گرفته و باعث کاهش کیفیت لاشبرگ ها و پایین آمدن سرعت بازگشت عناصر غذایی به خاک می شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Pollarding in forest can affect quantity and dynamics of leaf litter nutrients over time. The aim of this study was to compare the effect of pollarding on the chemical properties of the oak leaf litter after fall and nine months later. A &#160;sacred grove (less disturbed forest) stand &#160;and a nearby pollarded forest stand (Gallajar) located in the Madjese in Baneh County, were selected. In each stand, ten plots 4&#215;4 meters, were established and leaf litters were collected after leaf fall and nine months later in November of 2022 and July 2023 respectively. Totally, 40 leaf litter samples were collected. The measured chemical properties included carbon, nitrogen, phosphorus, potassium, pH, EC, C/N and C/P ratios. The results indicated that the leaf litter of sacred grove had higher quality than the Gallajar stand at the beginning of autumn, as indicated by the higher concentration of carbon, nitrogen, and potassium, as well as a lower C/N ratio. Additionally, the rate of litter decomposition in the sacred grove was faster than the Gallajar stand. In general, pollarding affected understory microclimate conditions through the reduction of leaves and litter input. Consequently, litter quality declined, and rate of nutrient return to the soil decreased.&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>25</FPAGE>
			<TPAGE>38</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/282025/08/27
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/6/5
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/192026/01/31
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/11/11
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>وحید</Name>
				<MidName></MidName>
				<Family>حسینی</Family>
				<NameE>Vahid</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hosseini</FamilyE>
				<Organizations>
				<Organization>گروه جنگلداری، دانشکده منابع طبیعی دانشگاه کردستان کردستان و مرکز پژوهش و توسعه جنگلداری زاگرس شمالی دکتر هدایت غضنفری، سنندج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>v.hosseini@uok.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>کیومرث</Name>
				<MidName></MidName>
				<Family>محمدی سمانی</Family>
				<NameE>Kyomars</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi Samani</FamilyE>
				<Organizations>
				<Organization>گروه جنگلداری، دانشکده منابع طبیعی دانشگاه کردستان، کردستان و مرکز پژوهش و توسعه جنگلداری زاگرس شمالی دکتر هدایت غضنفری، سنندج، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>k.mohammadi@uok.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فائزه</Name>
				<MidName></MidName>
				<Family>مرادی</Family>
				<NameE>Faezeh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moradi</FamilyE>
				<Organizations>
				<Organization>گروه جنگلداری، دانشکده منابع طبیعی، دانشگاه کردستان، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mfaezeh278@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>C/N Ratio</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Lebanon oak</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Litter quality</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Pollarding</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Northern Zagros.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بلوط وی ول</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زاگرس شمالی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کیفیت لاشبرگ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گلازنی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نسبت کربن به نیتروژن</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1- Anonymous. 2023. Statistical information of the Meteorological Department of Kurdistan Province, Baneh County. (In Persian)  https://wwwirimo.ir ##2- Aponte, C., Garcia, L.V. and Maranon, T., 2012. Tree species effect on litter decomposition and nutrient release in mediterranean oak forests changes over time. Ecosystems, 15: 1204–1218. ##3- Berg, B. and McClaugherty, C., 2014. Plant Litter, Decomposition, Humus Formation, Carbon Sequestration. Springer- Verlag, Berlin.##4- Blair, J.M., 1988. Nutrient release from decomposing foliar litter of three tree species with special reference to calcium, magnesium and potassium dynamics. Plant and Soil, 110: 49-55.##5- Cassani, M.T., Sabatte, M.L., Riveira Rubin, M.A., Sfeir, A.J. and Massobrio, M.J., 2021. Litter decomposition by soil fauna: effect of land use in agroecosystems. Heliyon, 7: e08127.##6- Chen, C., Zhang S., Li, L.D., Liu, Z.D., Chen, J.L., GU, X., Wang, L.F. and Fang, X., 2019. Carbon, nitrogen and phosphorus stoichiometry in leaf, litter and soil at different vegetation restoration stages in the mid-subtropical region of China. Chinese Journal of Plant Ecology, 43(8): 658-671. ##7-Chen, B., Chen, L., Jiang, L., Zhu, J., Chen, J., Huang, Q., Liu, J., Xu, D. and He, Z., 2022. C:N:P stoichiometry of plant, litter and soil along an elevational gradient in subtropical forests of China. Forests, 13 (3): 372.##8- Couteaux, M.M., Bottner, P. and Berg, B., 1995. Litter decomposition, climate and litter quality. Trends in Ecology and Evolution, 10: 63–66.##9- Freschet, G.T., Cornwell, W.K., Wardle, D.A., Elumeeva, T.G., Liu, W., Jackson, B.G., Onipchenko, V.G., Soudzilovskaia, N.A., Tao, J. and Cornellissen, H.C., 2013. Linking litter decomposition of above and belowground organs to plant-soil feedbacks worldwide. Journal of Ecology, 101: 943-952.##10- Ge, X., Lixion, Z., Wenfa, X., Zhilin, H., Xiansheng, G. and Benwang, T., 2013. Effect of litter substrate quality and soil nutrients on forest litter decomposition: A review. Acta Ecologica Sinica, 33(2): 102-108.##11- Ghasemi Aghbash, F., Allah Veisi, G. and Hosseini, V., 2016. Investigating nutrient quality and litter decomposition of Lebanon Oak (Quercus libani) in early stages of decomposition process in the Northern Zagros Forests (Case Study: Hoare Khul Forests in the City of Baneh). Journal of Zagros Forests Researches, 3(1):1-17. (In Persian).##12- Ghasemi Aghbash, F. and zarafshar, M., 2018. Leaf litter decomposition and nutrient dynamics of Persian Oak (Quercus brantii Lindl.) in the Northern Zagros Forests (Case Study: Chahar Zabar forests of Kermanshah). Iranian Journal of Forest, 10(3): 347-359. (In Persian)##13- Hedenec, P., Zheng, H., Pessanha Siqueira, D., Lin, Q., Peng, Y., Schmidt, I.K., Guldberg Froslev, T., Kjoller, R., Rousk, J. and Vesterdal L., 2023. Tree species traits and mycorrhizal association shape soil microbial communities via litter quality and species mediated soil properties. Forest Ecology and Management, 527: e120608.##14- Heiniger, W.R., McBride, R.G. and Clay, D.E., 2003. Using soil electrical conductivity to improve nutrient management. Agronomy Journal, 95: 508-519.##15- Hosseini, V. and Aziz, P., 2006. Determining rate of litter decomposition of Alnus subcordata in Asalem and Vaz regions by C/N index under laboratory conditions. Journal of Applied Sciences, 6 (1): 40-42.##16- Jacob, M., Viedenz, K., Polle, A. and Thomas, F.M., 2010. Leaf litter decomposition in temperate deciduous forest stands with a decreasing fraction of beech (Fagus sylvatica). Oecologia, 164: 1083-1094.##17- Jafari Haghighi M., 2003. Methods of Soil Analysis. Tehran. (In Persian)##18- Kavvadias, V.A., Alifragis, D., Tsiontsis, A., Brofas, G. and Stamatelos, G., 2001. Litterfall, litter accumulation and litter decomposition rates in four forest ecosystems in northern Greece. Forest Ecology and Management, 144: 113-127.##19- - Koosha, N., Mohammadi Samani, K. and Hosseini, V., 2022. Carbon stock and some chemical properties of soil in sacred groves and pollarded forest stands of northern Zagros Forests. Water and Soil, 36(5): 579-591. (In Persian).##20- Laskowski, R., Berg, B., Johansson, M. and McClaugherty, C.A., 1995. Release pattern for potassium from decomposing forest leaf litter. Long-term decomposition in a Scots pine forest. Canadian Journal of Botany, 73: 2019-2027. ##21- Li, Y., Dong, X., Yao, W., Han, C., Sun, S. and Zhao, C., 2022. C, N, P, K stoichiometric characteristics of the “leaf-root-litter-soil” system in dryland plantations. Ecological Indicators, 143: e109371.##22- Manzoni, S., Trofymow, J.A., Jackson, R.B. and Porporato, A., 2010. Stoichiometric controls on carbon, nitrogen, and phosphorus dynamics in decomposing litter. Ecological Monographs, 80: 89–106.##23- Mohammadi Samani, K., Hosseini, V. and Rostami, H., 2022. Physical and chemical properties of soil in sacred groves and surrounding oak woodlands in Baneh County. Forest and Wood Products, 74(4): 383-394. (In Persian).##24- Montane, F., Romanya, J., Rovira, P. and Casals, P., 2013. Mixtures with grass litter may hasten shrub litter decomposition after shrub encroachment into mountain grasslands. Plant and Soil,  368: 459-469 ##25-Mooshammer, M., Wanek, W., Schnecker, B., Wild, B., Leitner, S., Hofhansl, F., Bloxhi, A., Hammerle, I.A., Frank, H. and Fuchslueger, L., 2102. Stoichiometric controls of nitrogen and phosphorus cycling in decomposing beech leaf litter. Ecology, 93: 770-782##26- Osono, T. and Takeda, H., 2004. Potassium, calcium, and magnesium dynamics during litter decomposition in a cool temperate forest. Journal of Forestry Research, 8:23–31##27- Pan, Y., Birdsey, R.A., Fang, J., Houghton, R., Kauppi, P.E., Kurz, W.A., Phillips, L.O., Shvidenko, A., Lewis, L.S., Canadell, G.J., Ciais, P., Jackson, B.R., Pacala, A.S., McGuire, D., Piao, S., Rautiainen, A., Sitch, S. and Hayes, D., 2011. A large and persistent carbon sink in the world&#039;s forests. Science, 333: 998-1003. ##28- Paudel, E., Dossa, G.G.O., De Ble court, M., Beckschafer, P., Xu, J. and Harrison, R. D., 2015. Quantifying the factors affecting leaf litter decomposition across a tropical forest disturbance gradient. Ecosphere, 6 (12): 267. ##29- Plieninger, T., Quintas-Soriano, C., Torralba, M., Mohammadi Samani, K. and Shakeri, Z., 2020. Social dynamics of values, taboos and perceived threats around sacred groves in Kurdistan, Iran. People and Nature, 2(4): 1237-1250. ##30- Quested, H., Eriksson, O., Fortunel, C. and Garnier, E., 2007. Plant traits relate to whole-community litter quality and decomposition following land use change. Functional Ecology, 21: 1016-1026.##31- Ren, Y., Gao, G.L., Ding, G.D., Zhang, Y. and Zhao, P.S., 2024. Patterns and environmental drivers of C, N, and P stoichiometry in the leaf-litter-soil system associated with Mongolian pine forests. Ecology and Evolution, 14 (3): e11172.##32- Sardans, J., Janssens, I.A., Ciais, P., Obersteiner, M. and Penuelas, J., 2021. Recent advances and future research in ecological stoichiometry. Perspectives in Plant Ecology, Evolution and Systematics, 50: e125611.##33- Sari, R.R., Rozendaal, D.M.A., Saputra, D.D., Hairiah, K., Roshetko, J.M. and Noordwijk, M., 2022. Balancing litterfall and decomposition in cacao agroforestry systems. Plant Soil, 473: 251- 271. ##34- Sjors, H., 1959. Changes in pH of leaf litter during a field experiment. Oikos, 10: 225 - 232. ##35- Soto, B. and Diaz-Fierros, F., 1993. Interactions between plant ash leachates and soil. International Journal of Wildland Fire, 3(4): 207-216. ##36- Swift, M.J., Heal, O.W. and Anderson, J.M., 1979. Decomposition in Terrestrial Ecosystems. Blackwell, Scientific Publications, Oxford.##37- Tao, J., Zuo, J., He, Z., Wang, Y., Liu, J., Liu, W. and Cornelissen, J.H.C., 2019. Traits including leaf dry matter content and leaf pH dominate over forest soil pH as drivers of litter decomposition among 60 species. Functional Ecology, 33: 1798–1810.##38- Ubeda, X., Pereira, P., Outeiro, L. and Martin D.A., 2009. Effects of fire temperature on the physical and chemical characteristics of the ash from two plots of cork oak (Quercus suber). Land Degradation &#38; Development, 20(6): 589-608   ##39- Valipour, A., Plieninger, T., Shakeri, Z., Ghazanfari, H., Namiranian, M. and Lexer, M. J., 2014. Traditional silvopastoral management and its effects on forest stand structure in northern Zagros, Iran. Forest Ecology and Managemen, 327: 221-230.##40- Van Groenigen, K.J., Qi, X., Osenberg, C.W., Luo, Y. and Hungate, B. A., 2014. Faster decomposition under increased atmospheric CO2 limits soil carbon storage. Science, 344: 508–509.##41- Wang, B., Blondeel, H., Baeten, L., Djukic, I., De Lombaerde, E. and Verheyen, K., 2019. Direct and understorey-mediated indirect effects of human-induced environmental changes on litter decomposition in temperate forest. Soil Biology and Biochemistry, 138: e107579.##42- Zhang, Q. and Zak, J.C., 1995. Effects of gap size on litter decomposition and microbial activity in a subtropical forest. Ecology, 76:2196–2204.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>پاسخ مورفولوژیکی و ساختاری ریشه نهال ارغوان (.Cercis siliquastrum L) به عملکرد قارچ Glomus mosseae و نانولوله‌های کربنی‌چنددیواره در شرایط تنش خشکی</TitleF>
		<TitleE>Morphological and Structural Root Responses of Cercis siliquastrum L. Seedlings to Performance of Glomus mosseae and Multi-Walled Carbon Nanotubes Under Drought Stress</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تنش خشکی، عامل اصلی محدودکننده استقرار نهال&#8204;های چوبی در اکوسیستم&#8204;های نیمه&#8204;خشک زاگرس است که با کاهش کارایی ریشه، موفقیت برنامه&#8204;های احیایی را تهدید می&#8204;کند. این پژوهش برای نخستین بار، اثرات ترکیبی قارچ میکوریزیGlomus mosseae&#160;نانولوله&#8204;های&#8204;کربنی چنددیواره (MWCNTs) بر صفات مورفولوژیکی و ساختاری ریشه نهال&#8204;های ارغوان (Cercis siliquastrum L.) را تحت تنش خشکی بررسی کرد. تیمارها در قالب طرح کاملاً تصادفی با ساختار فاکتوریل ۳&#215;۲&#215;۳ و سه تکرار برای هر سلول آزمایشی شامل سه سطح تنش خشکی (۱۰۰، ۶۰ و ۲۰ درصد ظرفیت زراعی)، دو سطح قارچ (تلقیح و عدم تلقیح) و سه سطح MWCNTs (۰، ۵۰ و ۱۰۰ mg L⁻&#185;) اجرا شدند. &#160;برهم&#8204;کنش&#8204;های تنش&#215; قارچ بر قطر و تراکم بافت ریشه و تنش&#8204;&#215; قارچ&#215; &#160;MWCNTsبر تراکم بافت ریشه (0/01P&#60;) معنی&#8204;دار بود. در تنش&#8204; شدید (۲۰ %) حجم ۷۱%، وزن&#8204;تر ۶۸%، وزن خشک ۶۵% و طول ریشه ۲۶٪ کاهش یافت. تلقیح قارچ، افزایش 49&#8204;% حجم، ۴۸&#8204;% وزن تر، ۳۹&#8204;% وزن خشک و ۱۶&#8204;% طول ریشه ایجاد کرد. MWCNTs&#160; در غلظت mg L⁻&#185;100 نیز ۵۲ % وزن خشک، ۳۸ % وزن تر، ۲۷&#8204;% حجم و ۲۱&#8204;% طول ریشه را بهبود بخشید. به طور کلی، کاربرد همزمان قارچ میکوریزی و MWCNTs با افزایش کارایی جذب ریشه، رشد نهال&#8204;های ارغوان را تحت تنش خشکی ارتقا داد و به عنوان راهبرد نوین هم&#8204;افزا، پتانسیل بالایی برای احیای جنگل&#8204;های زاگرس دارد. 
&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Drought stress is the primary limiting factor for establishing woody seedlings in semi-arid Zagros ecosystems, reducing root efficiency and threatening restoration success. This study examined the combined effects of Glomus mosseae and Multi-Walled Carbon Nanotubes (MWCNTs) on the root morphological and structural traits of Cercis siliquastrum seedlings under drought conditions. Treatments were arranged in a completely randomized design (CRD) with a 3&#215;2&#215;3 factorial structure and three replications per treatment combination, including three drought levels (100%, 60%, 20% FC), two fungus levels (inoculated/uninoculated), and three MWCNT levels (0, 50, 100 mg L⁻&#185;). Significant interactions (p&#60;0.01) were observed for stress &#215; fungus on root tissue diameter and density, and for stress &#215; fungus &#215; MWCNTs on root tissue density. Under severe stress (20%), root volume, fresh weight, dry weight, and length decreased by 71%, 68%, 65%, and 26%, respectively. Fungal inoculation increased these parameters: volume (49%), fresh weight (48%), dry weight (39%), and length (16%). MWCNTs at 100 mg L⁻&#185; improved dry weight (52%), fresh weight (38%), volume (27%), and length (21%). The combined application of fungus and MWCNTs enhanced seedling growth by improving root uptake efficiency, offering a promising strategy for Zagros forest restoration under drought conditions.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>39</FPAGE>
			<TPAGE>55</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/282025/08/272025/11/29
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/9/8
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/192026/01/312026/02/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/11/18
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>افروز</Name>
				<MidName></MidName>
				<Family>هواسی</Family>
				<NameE>Afrooz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Havasi</FamilyE>
				<Organizations>
				<Organization>علوم جنگل، دانشکده کشاورزی، دانشگاه ایلام، ایلام، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>afroozhavasi@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جعفر</Name>
				<MidName></MidName>
				<Family>حسین زاده</Family>
				<NameE>Jaafar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hosseinzadeh</FamilyE>
				<Organizations>
				<Organization>گروه علوم جنگل، دانشکده کشاورزی، دانشگاه ایلام، ایلام، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>j.hoseinzadeh@ilam.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>حیدری</Family>
				<NameE>Mehdi</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Heydari</FamilyE>
				<Organizations>
				<Organization>گروه علوم جنگل، دانشکده کشاورزی، دانشگاه ایلام، ایلام، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>m.heydari@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جواد</Name>
				<MidName></MidName>
				<Family>میرزایی</Family>
				<NameE>Javad</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mirzaei</FamilyE>
				<Organizations>
				<Organization>گروه علوم جنگل، دانشکده کشاورزی، دانشگاه ایلام، ایلام، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mirzaei.javad@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Root tissue density</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Root volume</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Specific root volume</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Multi-walled carbon nanotubes (MWCNTs).</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تراکم بافت ریشه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>حجم ریشه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نانوفناوری زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>معماری سیستم ریشه‌</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحمل به کم‌آبی.</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1. Abdelhameed, R. E., Gahin, H., and Metwally, R. A., 2025. Kinetin and arbuscular mycorrhizal fungi: vital regulators of Vicia faba plants response and tolerance to drought stress. BMC Plant Biology, 25(1): 1155. ##2.	Ahmadi-Majd, M., Mousavi-Fard, S., Rezaei Nejad, A., and Fanourakis, D., 2022. Carbon nanotubes in the holding solution stimulate flower opening and prolong vase life in carnation. Chemical and Biological Technologies in Agriculture, 9(1): 15.‌##3.	Augé, R. M., 2001. Water relations, drought and vesicular-arbuscular mycorrhizal symbiosis. Mycorrhiza, 11(1): 3-42.‌ ##4.	Comas, L. H., Becker, S. R., Cruz, V. M. V., Byrne, P. F., and Dierig, D. A., 2013. Root traits contributing to plant productivity under drought. Frontiers in Plant Science, 4: 442.‌ ##5.	FAO., 2018. Cercis siliquastrum: Distribution and ecology. Food and Agriculture Organization of the United Nations.##6.	Farooq, M., Wahid, A., Kobayashi, N. S. M. A., Fujita, D. B. S. M. A., and Basra, S. M., 2009. Plant drought stress: effects, mechanisms and management. In Sustainable Agriculture. Springer Netherlands, Dordrecht,‌ pp. 153-188.##7.	García-Perez, J. L., Oliet, J. A., Villar-Salvador, P., and Guzmán, J. E., 2021. Root growth dynamics and structure in seedlings of four shade tolerant Mediterranean species grown under moderate and low light. Forests, 12(11): 1540.‌ ##8.	Ghalandari, S., Kafi, M., Goldani, M., and Bagheri, A., 2019. The effect of drought stress on some of morphological and physiological traits of common bean (Phaseolus vulgaris L.) genotypes. Iranian Journal of Pulses Research, 10(1):114-125.‌ (In Persian).##9.	Ghildiyal, S. K., Sharma, C. M., and Gairola, S., 2010. Variation in morphological characters of mycorrhizal seedlings of various provenances of Pinus roxburghii Sargent. New York Science Journal, 3: 1-8.‌##10.	Hajabbasi, M. A., 2001. Tillage effects on soil compactness and wheat root morphology. Journal of Agricultural Science and Technology, 3(1): 67-77‌. (In Persian).##11.	Hasanabadi, T., Ardakani, M. R., Rejali, F., Paknejad, F., Eftekhari, S. A., and Zargari, K., 2010. Response of barley root characters to co-inoculation with Azospirillum lipoferum and Pseudomonas fluorescens under different levels of nitrogen. American-Eurasian Journal of Agriculture and Environmental Science, 9(2): 156–162.##12.	Hermes, P. H., Gabriela, M. P., Ileana, V. R., Fusaro, C., Fernando, L. V., Mariana, M. A., ... and Fabián, F. L., 2020. Carbon nanotubes as plant growth regulators: prospects. In Green nanoparticles: synthesis and biomedical applications. Cham: Springer International Publishing, pp. 77-115. ##13.	Heydari, M., Anbari, M., Karamshahi, A., Hajinia, S., Valkó, O., and Prévosto, B., 2025. Enhancing Cercis siliquastrum seedling quality to meet ecological challenges in afforestation: influence of the combined effects of light, water stress, and zeolite amendment. 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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی سطح تعارضات بین جوامع محلی و گونه بیگانه مهاجم نوتریا (Myocastor coypus) در شمال غرب ‌ایران</TitleF>
		<TitleE>Assessing the Level of Conflicts Between Local Communities and The Invasive Species Nutria (Myocastor coypus) in Northwest Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف این پژوهش، شناخت نگرش جوامع محلی نسبت به گونه مهاجم نوتریا (Myocastor coypus) در گستره حضور آن در شمال غرب ایران بود. به این منظور، با ۳۱۰ نفر از ساکنان استان&#8204;های آذربایجان غربی، آذربایجان شرقی، اردبیل و گیلان به&#8204;طور تصادفی مصاحبه حضوری انجام شد. یافته&#8204;ها نشان می&#8204;دهند اگر چه فقط 8/1 درصد مصاحبه&#8204;شوندگان خسارت مستقیم نوتریا به محصولات خود را گزارش کردند، اما بخش قابل&#8204;توجهی از شرکت&#8204;کنندگان، این گونه را تهدیدی مهم برای منطقه دانسته و حذف آن را راهکاری مؤثر برای کنترل جمعیت پذیرفتند. تحلیل رگرسیون لجستیک نشان داد افراد با تحصیلات بالاتر و وابستگی اقتصادی بیشتر به فعالیت&#8204;های کشاورزی، نوتریا را تهدید جدی&#8204;تری می&#8204;دانند. علاوه بر این، افرادی که تجربه خسارت داشتند، به شدت آن را تهدیدی برای امنیت غذایی و محیط زیست ارزیابی کردند. مساحتی حدود ۷۷۰۰ کیلومترمربع از منطقه مورد مطالعه به عنوان کانون تعارض نوتریا با سرمایه&#8204;های انسانی برآورد شد، که نزدیک به نه درصد آن با مناطق حفاظت شده هم&#8204;پوشی دارد. توصیه می&#8204;شود در مدیریت تعارض با نوتریا، علاوه بر مداخلات فنی، بر آموزش، مشارکت اجتماعی و لحاظ کردن زمینه&#8204;های اقتصادی-اجتماعی جوامع محلی در طراحی راهکارها تمرکز شود تا هم اثربخشی زیستی و هم پذیرش اجتماعی تضمین گردد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>This study aimed to assess the attitudes and perceptions of local communities towards the invasive nutria (Myocastor coypus) across its distribution range in northwestern Iran. For this purpose, 310 local residents from west Azerbaijan, east Azerbaijan, Ardabil, and Gilan provinces were randomly selected for face-to-face interviews. The findings revealed that although only 8.1% of respondents reported direct damage to their agricultural crops, a considerable proportion of participants considered the nutria a major threat to the region and accepted culling as an effective population control strategy. Logistic regression analysis indicated that individuals with higher education levels and greater economic dependence on agriculture were more likely to perceive nutria as a serious threat. Moreover, those with prior experience of damage strongly viewed the species as a risk to both food security and the environment. Approximately 7700 km&#178; of the study area was identified as a conflict hotspot, of which nearly 9% overlaps with protected areas. It is recommended that in managing nutria-related conflicts, beyond technical interventions, efforts should focus on education, community participation, and integrating the socio-economic context of local communities into the design of management strategies. This integrated approach is essential to ensure both ecological effectiveness and social acceptance</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>57</FPAGE>
			<TPAGE>71</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/282025/08/272025/11/292025/12/3
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/9/12
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/192026/01/312026/02/72026/02/8
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/11/19
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>محمدرضا</Name>
				<MidName></MidName>
				<Family>اشرف زاده</Family>
				<NameE>Mohammad Reza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ashrafzadeh</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی محیط زیست، دانشکدۀ منابع طبیعی و علوم زمین، دانشگاه شهرکرد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mrashrafzadeh@sku.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سید شایان</Name>
				<MidName></MidName>
				<Family>جزایری</Family>
				<NameE>Seyed Shayan</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jazayeri</FamilyE>
				<Organizations>
				<Organization>گروه مدیریت و حفاظت تنوع زیستی، دانشکدۀ منابع طبیعی و علوم زمین، دانشگاه شهرکرد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>shayan.jazayeri@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علیرضا</Name>
				<MidName></MidName>
				<Family>محمدی</Family>
				<NameE>Ali Reza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi</FamilyE>
				<Organizations>
				<Organization>گروه علوم و مهندسی محیط زیست، دانشکده منابع طبیعی، دانشگاه جیرفت، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>armohammadi1989@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی اصغر</Name>
				<MidName></MidName>
				<Family>نقی پور</Family>
				<NameE>Ali Asghar</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Naghipour</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی طبیعت، دانشکدۀ منابع طبیعی و علوم زمین، دانشگاه شهرکرد، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>aa.naghipour@sku.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Nutria</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Biological invasion</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Conflict</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Local communities</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Invasive species management.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نوتریا</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تهاجم زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تعارض</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جوامع محلی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدیریت گونه‌های مهاجم.</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>تحلیل فضایی عرضه، تقاضا و جریان خدمات فرهنگی مرتبط با آموزش محیط‌زیست در شهرستان ملایر</TitleF>
		<TitleE>Spatial Analysis of the Supply, Demand, and Flow of Cultural Ecosystem Services Related to Environmental Education in Malayer County</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>آموزش محیط زیست به&#8204;عنوان یک خدمت اکوسیستمی فرهنگی، سهم طبیعت در تولید و تبادل دانش محیط&#8204;زیستی تعریف می&#8204;شود. در این مطالعه، خدمت آموزش غیررسمی محیط&#8204;زیست در شهرستان ملایر با استفاده از پنج معیار بصری و اکولوژیکی (کاربری زمین، تنوع پوشش&#8204;گیاهی، تنوع ارتفاعی، وجود مناطق حفاظت&#8204;شده و دسترسی) با روش&#8204;های تصمیم&#8204;گیری چندمعیاره، بر اساس نظرات کارشناسان و منابع علمی مدل&#8204;سازی شده است. برای ارزیابی تقاضا، نقشه توزیع جمعیت بر اساس داده&#8204;های سرشماری 1395 تولید و نقشه جریان خدمات آموزش محیط&#8204;زیست با استفاده از روش همه&#8204;جهته و در محیط GIS تهیه و تحلیل شد. نتایج نشان داد که تنوع پوشش&#8204;گیاهی بیشترین اهمیت را در میان معیارها دارد (0/41) و مناطق حفاظت&#8204;شده به&#8204;دلیل تنوع ارتفاعی و پوشش گیاهی بهتر، بیشترین سهم را در ارائه این خدمت دارند. همچنین مقایسه عرضه و تقاضای آموزش محیط&#8204;زیست نشان می&#8204;دهد در مناطق مرکزی، که پوشش&#8204;گیاهی نسبتاً کمتر و تراکم جمعیتی نیز بالاتر است، تطابق منفی دیده می&#8204;شود که این عدد در مناطق شهری به 0/86- می&#8204;رسد. &#160;همچنین نواحی شرقی و جنوب&#8204;شرقی شهرستان بیشترین میزان جریان این خدمت را دارا هستند. تنوع پوشش گیاهی و وجود مناطق حفاظت&#8204;شده، اهمیت آموزش محیط&#8204;زیست در این مناطق را دوچندان می&#8204;کند، زیرا کمبود دانش محیط زیستی می&#8204;تواند به منابع طبیعی آسیب جدی وارد کند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Environmental education, as a cultural ecosystem service, reflects the capacity of natural environments to support learning, awareness, and knowledge transfer. This study aims to spatially model informal environmental education services in Malayer County using five criteria: land use, vegetation diversity, elevation diversity, protected areas, and accessibility. Multi-criteria decision-making methods, based on expert judgment and scientific literature, were applied. A population distribution map was created using 2016 census data to assess demand. The spatial flow of environmental education services was modeled with an omnidirectional flow method within a GIS environment. Results indicate that vegetation diversity is the most influential criterion (0.41), while protected areas significantly contribute due to greater altitudinal heterogeneity and richer vegetation. Comparing service supply and demand reveals a spatial mismatch in central areas, where high population density and limited vegetation lead to negative service flow values, reaching &#8722;0.86 in urban zones. Conversely, the eastern and southeastern regions exhibit higher service flow. These findings underscore the importance of diverse vegetation and protected areas in enhancing environmental education services and highlight the need to promote environmental awareness to prevent natural resource degradation.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>73</FPAGE>
			<TPAGE>89</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/282025/08/272025/11/292025/12/32025/09/20
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/6/29
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/192026/01/312026/02/72026/02/82026/02/25
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1404/12/6
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>الهه</Name>
				<MidName></MidName>
				<Family>خانقلی</Family>
				<NameE>Elaheh</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Khangholi</FamilyE>
				<Organizations>
				<Organization>علوم و مهندسی محیط زیست، دانشکده منابع طبیعی و محیط‌زیست، دانشگاه ملایر، ملایر، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>elaheh.khangholi@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>کامران</Name>
				<MidName></MidName>
				<Family>شایسته</Family>
				<NameE>Kamran</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shayesteh</FamilyE>
				<Organizations>
				<Organization>گروه علوم و مهندسی محیط‌زیست، دانشکده منابع طبیعی و محیط‌زیست، دانشگاه ملایر، ملایر، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>ka_shayesteh@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمدرضا</Name>
				<MidName></MidName>
				<Family>گیلی</Family>
				<NameE>MohammadReza</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Gili</FamilyE>
				<Organizations>
				<Organization>گروه علوم و مهندسی محیط‌زیست، دانشکده منابع طبیعی و محیط‌زیست، دانشگاه ملایر، ملایر، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>environment.rs.gis@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بهناز</Name>
				<MidName></MidName>
				<Family>عطائیان</Family>
				<NameE>Behnaz</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ataeian</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی طبیعت، دانشکده منابع طبیعی و محیط‌زیست، دانشگاه ملایر، ملایر، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>attaeian94@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Mismatch</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Vegetation Cover</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Diversity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Geographic Information System</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Cultural Services.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عدم تطابق</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پوشش‌گیاهی</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>سیستم اطلاعات جغرافیایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خدمات فرهنگی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
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	</ARTICLE>


	<ARTICLE> 
		<TitleF>تحلیل بوم‌شناختی و مدل‌سازی مطلوبیت رویشگاه گونه دارویی آویشن کوهی (Thymus kotschyanus) در حوزه آبخیز طالقان با استفاده از 
مدل آنتروپی بیشینه (Maxent)</TitleF>
		<TitleE>Ecological Analysis and Habitat Suitability Modeling of the Medicinal Plant Thymus kotschyanus in the Taleghan Watershed Using the Maximum Entropy (Maxent) Model</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف این پژوهش تحلیل بوم&#8204;شناختی و مدل&#8204;سازی مطلوبیت رویشگاه گونه دارویی Thymus kotschyanus در حوزه آبخیز طالقان با استفاده از مدل آنتروپی بیشینه (Maxent) بود. تعداد 48 نقطه حضور گونه پس از اعمال فرایند پالایش مکانی به&#8204;منظور کاهش سوگیری نمونه&#8204;برداری در مدل استفاده شد. متغیرهای محیطی شامل عوامل توپوگرافی (ارتفاع، شیب و جهت)، ویژگی&#8204;های خاک، اقلیم و زمین&#8204;شناسی تهیه و کلیه لایه&#8204;ها به قدرت تفکیک مکانی 30&#215;30 متر هم&#8204;مقیاس&#8204;سازی شدند. داده&#8204;های اقلیمی بر اساس میانگین بلندمدت 30 ساله استخراج و دقت درون&#8204;یابی با شاخص&#8204;های ریشه میانگین مربعات خطا و ضریب تعیین ارزیابی شد. مدل با ترکیب ویژگی&#8204;های خطی، درجه دوم و لولا، ضریب منظم&#8204;سازی برابر 1، تعداد 10 تکرار و روش اعتبارسنجی متقابل اجرا گردید. عملکرد مدل خوب ارزیابی شد (سطح زیر منحنی = 0/844) و ضریب کاپا برابر 0/87 به&#8204;دست آمد. آستانه بهینه 43/.0 تعیین شد (حساسیت = 0/81، ویژگی = 0/78). بر اساس شاخص&#8204;های درصد مشارکت و اهمیت جایگشتی، جهت، ارتفاع، رس و ماده آلی بیشترین تأثیر را در پراکنش گونه داشتند. نتایج بیانگر اهمیت عوامل توپوگرافی و ادافیکی در تعیین مطلوبیت رویشگاه گونه در مقیاس حوزه آبخیز است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The aim of this study was to conduct an ecological analysis and habitat suitability modeling of the medicinal plant Thymus kotschyanus in the Taleghan watershed using the Maxent model. A total of 48 occurrence points were spatially thinned to reduce sampling bias. Environmental variables, including topography (elevation, slope, aspect), soil properties, climate, and geology, were prepared and resampled to a common resolution of 30 &#215; 30 m. Climatic data were based on 30-year averages, with interpolation accuracy evaluated using RMSE and R&#178;. The model was run using LQH feature classes, a regularization multiplier of 1, with 10 replicates and cross-validation. It performed well (AUC = 0.844, Kappa = 0.87). The optimal threshold was 0.43, with sensitivity of 0.81 and specificity of 0.78. Aspect, elevation, clay content, and soil organic matter were the most influential variables. Results highlight the significant roles of topographic and soil factors in shaping the habitat suitability for T. kotschyanus.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>91</FPAGE>
			<TPAGE>102</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2025/10/282025/08/272025/11/292025/12/32025/09/202025/06/7
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1404/3/17
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2026/01/192026/01/312026/02/72026/02/82026/02/252026/04/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1405/1/18
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مجتبی</Name>
				<MidName></MidName>
				<Family>اخوان ارمکی</Family>
				<NameE>Mojtaba</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Akhavan Armaki</FamilyE>
				<Organizations>
				<Organization>علوم مرتع، پردیس کشاورزی و منابع طبیعی دانشگاه تهران، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mtakhavan@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>ملیکا</Name>
				<MidName></MidName>
				<Family>هاشمی</Family>
				<NameE>Melika</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hashemi</FamilyE>
				<Organizations>
				<Organization>علوم مرتع، پردیس کشاورزی و منابع طبیعی دانشگاه تهران، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mehashemi@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Maxent</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Species distribution modeling</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Thymus kotschyanus</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Maximum entropy</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Habitat suitabi.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Maxent</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدل‌سازی توزیع گونه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آویشن کوهی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آنتروپی بیشینه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مطلوبیت رویشگاه.</KeyText>
			</KEYWORD>
		</KEYWORDS>

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

	</ARTICLE>

</ARTICLES>

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