<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1400</YEAR>
<VOL>10</VOL>
<NO>3</NO>
<MOSALSAL>37</MOSALSAL>
<PAGE_NO>99</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>مدل‌سازی پارامترهای تولید و پوشش تاجی به منظور معرفی مؤثرترین عامل محیطی در مراتع نیمه‌استپی باغرو، استان اردبیل ایران</TitleF>
		<TitleE>Modeling Production and Canopy Cover Parameters to identify the Most Effective Environmental Factors in Baghrou Semi-Steppe Rangelands of Ardabil Province, Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف از تحقیق حاضر تعیین مؤثرترین عوامل&#8204;محیطی (پستی&#8204; و بلندی، اقلیمی و خاک) بر تغییرات تولید و پوشش تاجی گیاهی و تهیه مدل پیش&#8204;بینی با استفاده از مهم&#8204;ترین عامل در مراتع نیمه&#8204;استپی هیر- باغرو استان اردبیل بود. ابتدا با در نظر گرفتن تیپ&#8204;های گیاهی و عوامل&#8204;محیطی، تولید و پوشش تاجی در مرحله گلدهی کامل گیاهان، با استفاده از پلات&#8204;های یک متر مربعی، برداشت شد. برای تعیین مؤثرترین عوامل&#8204;محیطی در تغییرات تولید و پوشش تاجی، از روش تجزیه به مؤلفه&#8204;های اصلی استفاده شد. برای مدل&#8204;سازیابتدا همبستگی بین تأثیرگذارترین عوامل&#8204;محیطی به&#8204;دست&#8204;آمده از تجزیه به مؤلفه&#8204;های اصلی انجام و عوامل با همبستگی بالا حذف و مدل&#8204;سازی با استفاده از رابطه چندجمله&#8204;ای درجه دو انجام شد. در نهایت مدل&#8204;های به&#8204;دست&#8204;آمده در محیط GIS شبیه&#8204;سازی شد. نتایج نشان&#8204;داد که شش مؤلفه اول با 65/71 درصد، بیش&#8204;ترین تأثیر را بر تغییرات تولید و پوشش تاجی داشت. با توجه به معیار (Root mean squared error =RMSE) نقشه&#8204;های شبیه&#8204;سازی شده تولید (76/0=RMSE) و پوشش تاجی (48/0=RMSE) توسط مهم&#8204;ترین عامل تأثیرگذار به&#8204;دست&#8204;آمده (بارندگی سالیانه) نیز صحت بالایی را نشان&#8204; داد. یافته&#8204;های این تحقیق می&#8204;تواند در مدیریت مراتع در استان اردبیل در راستای ایجاد تعادل بین عرضه و تقاضای تولید و توازن کربن مورد استفاده قرار گیرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The aim of the study was to determine the most important environmental factors (topography, climate, and soil) affecting changes in production and canopy cover of plant variations and to prepare prediction maps, based on the most important factor, in semi-steppe rangelands of Hir-Baghrou, Ardabil province, Iran. First, by detecting the vegetation types and different classes of environmental factors, the production and canopy cover were estimated in 1-m2 plots at full flower stage of dominant species. Then, to determine the most important environmental factors, affecting the production and canopy cover changes, the principal component analysis (PCA) was used. For modeling, first, the correlation between the most effective environmental factors was obtained from the PCA. Then, the highly correlated factors were eliminated and the quadratic polynomial models were obtained. Finally, the obtained models were simulated in GIS. The results of the PCA showed that the first six components with 71.65% had the greatest effect on the production and canopy cover changes. Based on the root mean squared error (RMSE), simulating maps of production (RMSE=0.76) and canopy cover (RMSE=0.48) by effective factor (annual precipitation) showed the highest accuracy. The results of this study can be used to manage the rangelands of Ardabil province to create a balance between supply and demand of production and also to balance carbon.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>15</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/21
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/5/30
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/1
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/8/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فرید</Name>
				<MidName></MidName>
				<Family>دادجو</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dadjou</FamilyE>
				<Organizations>
				<Organization>دانشگاه محقق اردبیلی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>f.dadjou@uma.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>اردوان</Name>
				<MidName></MidName>
				<Family>قربانی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghorbani</FamilyE>
				<Organizations>
				<Organization>دانشگاه محقق اردبیلی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>a_ghorbani@uma.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>معمری</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moameri</FamilyE>
				<Organizations>
				<Organization>دانشگاه محقق اردبیلی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>moameri@uma.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رئوف</Name>
				<MidName></MidName>
				<Family>مصطفی زاده</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mostafazadeh</FamilyE>
				<Organizations>
				<Organization>دانشگاه محقق اردبیلی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Raoofmostafazadeh@uma.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>زینب</Name>
				<MidName></MidName>
				<Family>حزباوی</Family>
				<NameE>Z.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hazbavi</FamilyE>
				<Organizations>
				<Organization>دانشگاه محقق اردبیلی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>z.hazbavi@uma.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Simulation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Rangeland</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Physiography</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Climate</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Soil parameters</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ecoregion</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شبیه‌سازی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مرتع</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پستی و بلندی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اقلیم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پارامترهای خاک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>منطقه اکولوژیک</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.   Abdollahi, J., H. Arzani and H. Naderi. 2011. Effective meteoroidal factors for forage production of Nodoushan steppe rangelands in Yazd province. Iranian Journal of Rangeland 5(1): 45-56. (In Farsi)##2.	Ahmadi, H., K. Javanshir, Gh. A. Ghanbarian and S. H. Habibian. 2002. An investigation ecological characteristic of plant communities in relation to geomorphological units, Case study: Chenar Rahdar region of Fars province. Iranian Journal of Natural Resource 55 (1): 81-94. (In Farsi)##3.	Allan, E., W. W. Weisser, M. Fischer, E. D. Schulze, A. Weigelt and C. Roscher. 2013. A comparison of the strength of biodiversity effects across multiple functions. Journal of Oecologia 173: 223-237.##4.	Beers, T. W., P. E. Dress and L. C. Wensel. 1966. Aspect transformation in productivity research. Journal of Forestry 64: 691-692.##5.	Bork, E. W., T. Thomas and B. Mcdougall. 2001. Herbage response to precipitation in central Alberta boreal grasslands. Journal of Range Management 54: 243-248.##6.	Dadjou, F., A. Ghorbani, M. Moameri and M. Bidar Lord. 2018. Effect of temperature and rainfall on Aboveground Net Primary Production of Hir and Neur rangelands in Ardabil province. Iranian Journal of Range and Desert Research 25 (3): 566–575. (In Farsi)##7.	Ehleringer, J. R., S. Schwinning, and R. Gebauer. 1999. Water use in arid land ecosystems. In: Press, M. C., Scholes, J. D. and M. G. Barker. (Eds.), Physiological Plant Ecology. pp. 347-365, Blackwell Science, Boston, USA.##8.	Ehrlich, P.R. and A. H. Ehrlich. 1991. Healing the planet: Strategies of solving the environmental crisis. Addison Wesley Reading Ma.##9.	Elmojahid, L., X. Leroux, S. Michalet, F. Bellvert, A. Weigelt and F. Poly. 2017. Effect of plant diversity on the diversity of soil organic compounds. Journal of Plos One 12(2): 0170494.##10.	Gervasio Pineiroa, G., S. Perelman, J. P. Guerschman and J. M. Paruelo. 2008. How to evaluate models: Observed vs. predicted or predicted vs. observed? Journal of Ecological Modeling 216: 316-322.##11.	Ggeitury, M., N. Ansari and M. Heshmati. 2007. The effective factors of destruction in Kermanshah rangelands. Iranian Journal of Range and Desert Research 13(4): 314-323. (In Farsi)##12.	Ghorbani, A. and A. Asghari. 2014. Ecological factors affecting the distribution of Festuca ovina in Southeastern rangelands of Sabalan. Iranian Journal of Range and Desert Research 21(2): 368-381. (In Farsi)##13.	Ghorbani, A., F. Dadjou, M. Moameri, M. Bidar Lord and K. Hashemi Majd. 2018. Investigating the relationships between net primary production with physiographic factors in Hir and Neur rangelands in Ardabil province. Iranian Journal of Rangeland 12(1): 73-88. (In Farsi)##14.	Ghorbani, A., F. Dadjou, M. Moameri and A. Biswas. 2020a. Estimating aboveground net primary production (ANPP) using landsat 8-based indices: a case study from Hir_Neur rangelands, Iran. Rangeland Ecology &#38; Management 73(5): 649-657.##15.	Ghorbani, A., M. Moameri, F. Dadjou, S. A. Seyedi Kaleybar, A. Pournemati and Sh. Asghari. 2020b. Determinization of Environmental Factors Effects on Plants Production in QezelOzan-Kosar Rangelands, Ardabil Province. ECOPERSIA 8(1): 47-56.##16.	Griffiths, R. P., M. D. Madritch and A. K. Swansona 2009. The effects of topography on forest soil characteristics in the Oregon Casade Mountains (USA): Implications for the effects of climate change on soil properties. Journal of Forest Ecology and Management 257: 1-7.##17.	Hao, X. and A. Papadopoulos. 2004. Effects of calcium and magnesium on plant growth, biomass partitioning, and fruit yield of winter greenhouse tomato. Hort Science 39(3): 512-515.##18.	Jafari, M., M. A. Zare Chauouki, A. Tavili and A. Kouhandel. 2007. Soil-vegetation relationships in rangelands of Qom Province. Pajouhesh va Sazandegi 19(3): 110-116. (In Farsi)##19.	Jafarian, Z., R. Omidipour and L. Zandi. 2021. Effects of Altitude and Soil Properties on Alpha and Beta Diversity in Plour Rangelands of Mazandaran. Iranian Journal of Applied Ecology 10(1): 79-92. (In Farsi)##20.	Khumalo, G. F. and J. Holechek. 2005. Relationship between Chihuahuan desert perennial grass production and precipitation. Journal of Rangeland and Ecology Management 58(33): 239-246.##21.	Li, H., K. Shi and D. Xu. 2005. Effects of plant process on soil organic carbon concentration. Journal of Applied Ecology 16(6): 8-1163.##22.	Mao, D., Z. Wang, L. Li and W. Ma. 2014. Spatiotemporal dynamics of grassland aboveground net primary productivity and its association with climatic pattern and changes in Northern China. Journal of Ecological Indicators 41: 40-48.##23.	‌Mesdaghi, M. 2015. Range Management in Iran. Seventh ed. Sadjad University of Technology, Mashhad. (In Farsi)##24.	Mirzaei Mossivand, A., A. Ghorbani, M. A. Zare Chahoki, F. Keivan Behjou and K. Sefidi. 2016. Environment factors affecting the distribution of species Prangos ferulacea Lindl. in rangelands of Ardabil Province. Iranian Journal of Rangeland 10(2): 191-203. (In Farsi)##25.	Moore, I. D., R. B. Grayson and A. R. Ladson. 1991. Digital terrain modelling: A review of hydrological, geomorphological, and biological applications. Journal of Hydrological Processes 5: 3-30.##26.	Munkhtsetseg, E., R. Kimura, J. Wang and M. Shinoda. 2007. Pasture yield response to precipitation and high temperature in Mongolia. Journal of Arid Environment 70: 94-110.##27.	Ni, J. 2003. Plant functional types and climate along a precipitation gradient in temperate grasslands, north-east China and south-east Mongolia. Journal of Arid Environments 53: 501-516.##28.	Pornemati, A., A. Ghorbani, J. Sharifi, F. Mirzaei Aghche Gheshlagh, M. Amirkhani and M. Ghodarzi. 2017. Study the effects of elevation, slope and aspect on life form forage production in Sabalan rangelands in Ardabil province. Iranian Journal of Range and Desert Research 24(1): 91-100. (In Farsi)##29.	Rocarpian, P., S. Gachet, K. Metzner and A. Saatkamp. 2016. Moisture and soil parameters drive plant community assembly in Mediterranean temporary pools. Journal of Hydrobiologia 781(1): 55-66.##30.	Ruppert, J. and Ch. A. Lindstadter. 2014. Convergence between ANPP estimation methods in grassland – A practical solution to the comparability dilemma. Journal of Ecological Indicators 36: 524-531.##31.	Sun, J. and W. Du. 2017. Effects of precipitation and temperature on net primary productivity and precipitation use efficiency across China’s grasslands. Journal of GIScience and Remote Sensing 54: 1-17.##32.	Taghipour, A. and S. Rasgar. 2010. Role of physiography on vegetation cover using GIS (Case of Hezarjarib's Rangelands, Mazandaran province). Iranian Journal of Rangeland 4(2): 168-177. (In Farsi)##33.	Tamartash, R. 2012. Investigation on the relationship between vegetation characteristics and topographic factors in utilization units of mountainous rangelands of Vaz, Mazandaran. Iranian Journal of Range and Desert Research 19(3): 469-481. (In Farsi)##34.	Wang, X., F. Li, R. Gao, Y. Luo and T. Liu. 2014. Predicted NPP spatiotemporal variations in a semiarid steppe watershed for historical and trending climates. Journal of Arid Environments 104: 67-79.##35.	Yu, M. M., Y. H. Chen, Z. B. Zhu, L. Liu, L. X. Zhang and Q. S. Guo. 2016. Effect of phosphorus supply on plant productivity, photosynthetic efficiency and bioactive-component production in Prunella vulgaris L. under hydroponic condition. Journal of Plant Nutrition 39(12): 1672-1680. ##36.	Zare Chahouki, M. A., A. Zare Chahouki and M. Zare Ernani. 2010. Effects of topographic and edaphic characteristics on distribution of plant species in Eshtehard rangelands. Iranian Journal of Natural Resources 63(3): 331-340. (In Farsi)##37.	Zareh Hesari, B., A. Ghorbani, F. Azimi Motam, K. Hashmi Majd and A. Asghari. 2014. Study the effective ecological factors on distribution of Artemisia fragrans in southeast faced slopes of Sabalan, Iranian Journal of Rangeland 8(3): 238-250. (In Farsi)##38.	Zarekia, S., Z. Niloofar, A. Ehsani, F. Jafari and H. Yeganeh. 2013. Relationship between rainfall and annual forage production of important range species (Case study: Khoshkerood – Saveh). Iranian Journal of Range and Desert Research 19(4): 614-623. (In Farsi)## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>طبقه‌بندی جوامع گیاهی و ارتباط آنها با عوامل فیزیوگرافیک در جنگل دارابکلای استان مازندران</TitleF>
		<TitleE>Vegetation Classification of Darabkola Forest and Their Relation to Physiographic Factors</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف پژوهش حاضر شناسایی و تشریح واحدهای جامعه&#8204;شناختی جنگل آموزشی و پژوهشی دانشکده منابع طبیعی واقع در شرق شهرستان ساری، استان مازندران است. برای این منظور تعداد 139 قطعه نمونه 400 مترمربعی به صورت سیستماتیک- انتخابی با ابعاد شبکه 400 متری با تأکید بر اصل توده مُعرِّف، در سطح منطقه پیاده شد. طبقه&#8204;بندی جوامع گیاهی با استفاده از روش TWINSPAN اصلاح شده و روش سنتز جدولی براون-بلانکه منجر به شناسایی پنج جامعه گیاهی انجیلی-ممرزستان، آزاد- بلوطستان، تاج ریزی جنگلی-راشستان، پلت- انجیلیستان و فرفیون جنگلی-راشستان به&#8204;همراه چهار زیرجامعه تیپیک بلندمازو، راش، ممرز و لرگ شد. نمایش جوامع گیاهی در امتداد دو محور اول تحلیل تطبیقی قوس&#8204;گیری شده (DCA) نشان داد که قطعات نمونه هر یک از جوامع گیاهی جنگل دارابکلا حاشیه مخصوص به خود را داشته و از یکدیگر متمایز هستند. نتایج تحلیل رگرسیون چندگانه عوامل فیزیوگرافیکی، نشان داد که عامل ارتفاع از سطح دریا به&#8204;صورت معنی&#8204;دار و با ضریب تبیین بالایی با دو محور اول DCA همبستگی دارد. به&#8204;طور کلی، نتایج این پژوهش افزون بر معرفی و تشریح جوامع گیاهی جنگل دارابکلا، می&#8204;تواند قابل استفاده در مطالعه&#8204;ی زیر بنایی سایر تحقیقات به&#8204;منظور شناخت بهتر جنگل داربکلا و درک قوانین بوم&#8204;شناختی موجود در آن باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>This study focused on vegetation classification of Darabkola forest in the middle part of Hyrcanian forests in north of Iran. For this purpose, 139 releves were sampled using systematic- selective method in 400 m grid dimensions by the consideration of indicator stands concept. Based on modified TWINSPAN method and Braun-Blanquet phytosociological method, five associations (Parrotio persicae-Carpinetum betuli, Zelkovo carpinifoliae-Quercetum, Solano kieseritzkii-Fagetum orientalis, Aceri velutini-Parrotietum persicae and &#160;Euphorbio amygdaloidae-Fagetum orientale) and four sub-associations (Zelkovo carpinifoliae-Quercetum castaneifoliae subasso a typical subasso Quercetosum, Zelkovo carpinifoliae-Quercetum castaneifoliae subasso Fagetosum orientale, Aceri velutini-Parrotietum persicae subasso Carpinetusum betuli and Aceri velutini-Parrotietum persicae subasso Pteroetosum fraxinifoliae) were distinguished. Demonstration of plant communities along the first two axes of detrended correspondence analysis (DCA) showed that these associations had almost distinct pattern. Also, results of multiple regression of topographic factors with the two first ordination axes of DCA indicated that elevation was the most important topographic factor in distribution of the associations in the Darabkola forests. In addition, the results of this study can lead to the more efficient management and better protection of Darbakla forest.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>17</FPAGE>
			<TPAGE>33</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/212021/09/1
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/6/10
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/12021/11/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/8/16
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>حامد</Name>
				<MidName></MidName>
				<Family>اسدی</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Asadi</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>h.asadi@sanru.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>حمید</Name>
				<MidName></MidName>
				<Family>جلیلوند</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jalilvand</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>h.jalilvand@sanru.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سید مصطفی</Name>
				<MidName></MidName>
				<Family>مسلمی سید محله</Family>
				<NameE>S. M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moslemi</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>smm797@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Vegetation Classification</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Modified TWINSPAN</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Braun-Blnquet method</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Darabkola forest</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>روش براون-بلانکه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>TWINSPAN اصلاح شده</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جنگل داربکلای مازندران</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Asadi, H., O. Esmailzadeh, S. M. Hosseini, Y. Asri and H. Zare. 2016. Application of Cocktail method in vegetation classification. Taxonomy and Biosystematics 8(28): 21-38. (In Farsi).##2.	Asri, Y. 1995. Phytosociology. Payame Noor University. Tehran, Iran. (In Farsi).##3.	Borji, M., H. Ravanbakhsh, B. Hamzeh’ee, M. Amiri and M. K. Kianian. 2018. A comparison of environmental and vegetation variables between Carpinus betulus and C. × schuschaensis stands in Naghibdeh and Mazdeh forests (Sari, Mazandaran) and introducing a new hornbeam association. Iranian Journal of Forest and Poplar Research 26: 189-201. (In Farsi).##4.	Chytry M and L. Tichy. 2003. Diagnostic, constant and dominant species of vegetation classes and alliances of the Czech Republic: a statistical revision. Masaryk University, Czech Republic.##5.	De Caceres M. and P. Legendre. 2009. Associations between species and Groups of Sites: Indices and Statistical Inference. Ecology 90(12): 3566-3574.##6.	De Cáceres, M. 2013. How to use the indicspecies package (ver. 1.7. 1). R Proj, 29. Spain Available online at: https://vegmod.github.io/software/indicspecies/. Accessed 2020-02-04.##7.	De Caceres, M., M. Chytry, E. Agrillo, F. Attorre, Z. Botta-Dukat, J. Capelo and E. Feoli. 2015. A comparative framework for broad-scale plot-based vegetation classification. Applied Vegetation Science 18(4): 543-560.##8.	Dengler, J., M. Chytry and J. Ewald. 2008. Phytosociology. pp. 2767–2779 In: Jorgensen, S.E. and B.D. Fath. (Eds.), Encyclopedia of ecology. Elsevier, Amsterdam.##9.	Dobrović, I., T. Safner, S. D. Jelaska and T. Nikolić. 2006. Ecological and phytosociological characteristics of the association Abieti-Fagetum. Acta Botanica Croatica 65 (1): 41-55.##10.	Edwards, E. J., D. S. Chatelet, B. C. Chen, J. Y. Ong, S. Tagane, H. Kanemitsu ... and M. J. Donoghue. 2017. Convergence, consilience, and the evolution of temperate deciduous forests. The American Naturalist  190(S1): S87-S104.##11.	Ejtehadi, H., H. Zare, M. Akbarinia and M. Hosseini. 2004. Ecological study of Betula pendula stands in Hyrcanian forests, north Iran. Acta Botanica Hungarica 46: 143–151.##12.	Eshagh Nimvari, J., Gh. Zahedi Amiri, M. R. Marvi Mohajer, M. Asadi and A. Mattaji. 2007. Evaluation and comparison of species diversity in Fagetum orientalis, Carpino-Fagetum orientalis and Querco-Carpinetum betulii communities (Case study :Namkhaneh and Gorazbon Districts-Noshahr). Iranian Journal of Forest and Poplar 14(4): 326-237. (In Farsi).##13.	Esmaeilzadeh, O., H. Asadi and A. Ahmadi. 2013. Phytosociology of Khybus protected area. Journal of Wood and Forest Science and Technology 19: 1–20. (In Frarsi).##14.	Esmaeilzadeh, O., S. M. Hosseini and M. Tabari. 2007. A phytosociology study of English yew (Taxus baccata L.) in Afratakhteh reserve. Pajouhesh and Sazandegi 74: 17–24. (In Frarsi).##15.	Fadl, M. A., H. M. Al-Yasi and E. A. Alsherif. 2021. Impact of elevation and slope aspect on floristic composition in wadi Elkor, Sarawat Mountain, Saudi Arabia. Scientific reports 11(1): 1-10.##16.	Gholizadeh, H., A. Naqinezhad and M. Chytrý. 2020. Classification of the Hyrcanian forest vegetation, Northern Iran. Applied Vegetation Science 23(1): 107-126. ##17.	Goodarzi Gh. R., F. Ahmadloo and Kh. Sagheb-Talebi. 2013. Effects of physiographic factors and Some physical and chemical Soil properties on distribution Amygdalus scoparia Spach. in 4 Areas of Markazi Province. Journal of Wood and Forest Science and Technology 19(3): 59-76. (In Frarsi).##18.	Gu, F., E. Ramezani, K. Alizadeh and H. Behling. 2021. Vegetation dynamics, environmental changes, and anthropogenic impacts on the coastal Hyrcanian forests in northern Iran. Journal of Coastal Research 37(3): 611-619.##19.	Hamzeh’ee, B. 1994. A survey of the plant communities of the Lesakuti forests, 3th series, SE Tonekabon. Research Institute of Forests and Rangeland. Tehran, Iran. (In Frarsi).##20.	Hamzeh’ee, B., A. Naqinezhad, F. Attar, A. Ghahreman, M. Assadi and N. Prieditis. 2008. Phytosociological survey of remnant Alnus glutinosa ssp. barbata communities in the lowland Caspian forests of northern Iran. Phytocoenologia 38: 117–132. ##21.	Jashni, J., M. R. Marvi Mohadjer, Gh. Zahedi Amiri, V. Etemad and B. Hamzehee. 2012. Plant associations in Baharbon district of Kheyroud Forest and its relationship to land forms. Iranian Journal of Forest and Poplar Research 20(3): 402-419. (In Frarsi).##22.	Karami-Kordalivand, P., O. Esmailzadeh, W. Willner, J. Noroozi and S. J. Alavi. 2021. Classification of forest communities (co-) dominated by Taxus baccata in the Hyrcanian forests (northern Iran) and their comparison with southern Europe. European Journal of Forest Research 140(2): 463-476.##23.	Kent, M. 2011. Vegetation description and data analysis: a practical approach. John Wiley &#38; Sons, Amesterdam.##24.	Luther-Mosebach, J., J. Dengler, U. Schmiedel, I. U. Rower, T. Labitzky and A. Grongroft. 2012. A first formal classification of the Hardeveld vegetation in Namaqualand, South Africa. Applied Vegetation Science 15(3): 401-431.##25.	Mattaji, A and S. Babaikafaki. 2006. Investigation on plant associations and physiographical situation to draw plant associations profile in north of Iran (Case study: Kheiroudkenar forest – Noshahr). Iranian Journal of Forest and Poplar Research 14: 258-268. (In Frarsi).##26.	Mirdeylami, S.Z. and Gh. A. Heshmati. 2014. Study of the forest vegetation on the basis of elevation gradient in Touskestan-Charbagh habitat, Golestan province. Journal of Wood and Forest Science and Technology  20(4): 41-60. (In Frarsi).##27.	Mohammadnejad Kiasari, Sh., Kh. Sagheb-Talebi, R. Rahmani, E. Adeli, B. Jafari and H. Jafarzadeh. 2010. Quantitative and qualitative evaluation of plantations and natural forest at Darabkola, east of Mazandaran. Iranian Journal of Forest and Poplar Research 18(3): 337-351. (In Persian).##28.	Mossadegh, A. 1971. Contribution à l’étude des peuplements de Taxus baccata L. en Iran. Revue Forestière Française 23: 645-648.##29.	Naqinezhad, A., H. Bahari, H. Gholizadeh, R. Esmaeili, B. Hamzeh’ee, N. Djamali and H. Moradi. 2012. A phytosociological survey of two lowland Caspian (Hyrcanian) remnant forests, Northern Iran, for validation of some forest syntaxa. Phytologia Balcanica 18: 173–186.##30.	Naqinezhad, A., H. Zare-Maivan and H. Gholizadeh. 2015. A floristic survey of the Hyrcanian forests in Northern Iran, using two lowland-mountain transects. Journal of Forestry Research 26, 187-199.##31.	Noroozi, J., W. Willner, H. Pauli and G. Grabherr. 2014. Phytosociology and ecology of the high-alpine to subnival scree vegetation of N and NW Iran (Alborz and Azerbaijan Mts.). Applied Vegetation Science 17(1):142-161.##32.	Oksanen, J., R. Kindt, P. Legendre, B. O’Hara, M. H. H. Stevens, M. J. Oksanen and  M. A. S. S. Suggests. 2007. The vegan package. Community ecology package 10: 631-637.##33.	Passarge, H. 1981. Carpineta in kartalinischen Kaukasus. Phytocoenologia 9: 533–545.##34.	Pourbabaei, H. 2015. Relationship between vegetation and environmental factors in the Anatolian oak (Quercus petraea L. subsp. iberica (Stev.) Krassiln) habitat: a case study of Asalem forests, Guilan. Journal of Plant Research 28(1): 53-62. (In Frarsi).##35.	Pourbabaei H., V. Rahimi and M N. Adel. 2015. Effect of environmental factors on rangeland vegetation distribution in Divan-Darre area, Kurdistan. Iranian Journal of Applied Ecology 4(11): 27-39. (In Frarsi).##36.	Sagheb-Talebi, K., T. Sajedi and M. Pourhashemi. 2014. Forests of Iran. A treasure from the past, a hope for the future. Springer, Amesterdam.##37.	Tichý, L. 2002. JUICE, software for vegetation classification. Journal of vegetation science 13(3): 451-453.##38.	Walter, H. 2012. Vegetation of the earth and ecological systems of the geo-biosphere. Springer Science &#38; Business Media, Berlin.##39.	Weber, H. E., J. Moravec and J. P. Theurillat. 2000. International code of phytosociological nomenclature. Journal of vegetation Science 11(5): 739-768.##40.	Witte, J. P. M. 2002. The descriptive capacity of ecological plant species groups. Plant Ecology 162(2): 199-213.##41.	Zakeri Pashakolaei M., S. Alvaninejad and O. Esmailzade. 2014. Relationship between plant biodiversity and topographical factors in Forests of west Mazandaran (Case study: Research forest of Tarbiat Modares University). Iranian Journal of Applied Ecology 3(8): 1-16. (In Frarsi).##42.	Zare, H. 2003. Ecological investigation on Betula pendula Roth. sites in Sangdeh and Lar. MSc. thesis Tarbiat Modares University. Tehran, Iran. (In Frarsi).##43.	Zellweger, F., D. Coomes, J. Lenoir, L. Depauw, S. L. Maes, M. Wulf ... and P. De Frenne. 2019. Seasonal drivers of understorey temperature buffering in temperate deciduous forests across Europe. Global Ecology and Biogeography 28(12): 1774-1786.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی میزان مسئولیت‌پذیری و مشارکت محیط‌زیستی مناطق روستایی در حفاظت 
(مطالعه موردی: شهرستان بندرعباس)</TitleF>
		<TitleE>Investigating the Level of Environmental Responsibility and Participation of Rural Areas in Conservation, a case study in Bandar Abbas County</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>هدف از این پژوهش بررسی میزان مشارکت و مسئولیت&#8204;پذیری محیط&#8204;زیستی ساکنین مناطق روستایی شهرستان بندرعباس بود که به شیوه پیمایشی و میدانی انجام شد. با استفاده از فرمول کوکران و جمعیت کل ساکن در روستاها تعدا 366 پرسشنامه به شیوه طبقه&#8204;ای- تصادفی تکمیل شد. پرسشنامه تحقیق در دو بخش مشارکت محیط&#8204;زیستی و مسئولیت&#8204;پذیری محیط&#8204;زیستی در طیف پاسخ پنج گزینه&#8204;ای لیکرت طراحی شد. پایایی پرسشنامه با استفاده از آزمون-آزمون مجدد و محاسبه ضریب آلفای کرونباخ برای پرسشنامه&#8204;های مشارکت و مسئولیت&#8204;پذیری محیط&#8204;زیستی به ترتیب 0/79 و 0/86 محاسبه شد. نتایج نشان داد که مشارکت اقتصادی، مشارکت اجتماعی و مشارکت فرهنگی به ترتیب با 14/37، 13/70 و 12/96 از بیشترین امتیاز در بین جوامع روستایی برخوردار است. در میان ابعاد مسئولیت&#8204;پذیری نیز مسئولیت&#8204;پذیری حقوق بشری با میانگین 19/43 بیشترین میزان مسئولیت&#8204;پذیری در بین ساکنین مناطق روستایی است و پس&#8204;ازآن، به ترتیب مسئولیت&#8204;پذیری قانونی با میانگین 18/6، فکری و درونی با میانگین 17/37 و عملیاتی با میانگین 16/85 قرار دارند. مقایسه میزان مشارکت و مسئولیت&#8204;پذیری در مناطق روستایی شهرستان بندرعباس نشان داد که تفاوت معنی&#8204;دار بین مناطق مختلف روستایی وجود ندارد (P &#62; 0.05). روستاییان در حفظ و نگهداری محیط&#8204;زیست فعالیت و مشارکت دارند که این امر نشان&#8204;دهنده توجه مردم به محیط&#8204;زیست طبیعی منطقه است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The purpose of this study was to investigate the level of environmental responsibility and environmental participation among the residents of rural areas in Bandar Abbas county, which was conducted by survey and field methods. Sample size was determined based on the Cochran&#8217;s formula and the required data were collected through questionnaires. A total of 366 questionnaires were completed in a stratified-random manner. The research questionnaire was designed in two parts: environmental participation and environmental responsibility, using the 5-points Likert scale. The reliability of the questionnaires, calculated by test-retest and Cronbach&#39;s alpha coefficient for the participation and environmental responsibility questionnaires, were 0.79 and 0.86 respectively. Results showed that economic, social and cultural participations with the score of 14.37, 13.70 and 12.96 respectively, have the highest scores in rural communities. Among the dimensions of responsibility, human rights responsibility with an average of 19.43 was the highest score among the residents of rural areas, followed by legal responsibility (18.6), intellectual and internal (17.37) and operational (16.85) responsibility. Comparison of participation and responsibility in rural areas of Bandar Abbas showed that there is no significant difference between different rural areas (P ˃ 0.05). The rural residents are active and involved in environmental protection, showing people&#39;s attention to the natural environment of the region.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>35</FPAGE>
			<TPAGE>46</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/212021/09/12021/07/2
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/4/11
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/12021/11/72021/11/22
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/9/1
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>صابر</Name>
				<MidName></MidName>
				<Family>قاسمی</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghasemi</FamilyE>
				<Organizations>
				<Organization>دانشگاه آزاد اسلامی واحد بندرعباس، ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>saberghasemi@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Participation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Responsibility</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Environmental protection</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Bandar Abbas Rural Areas</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مشارکت</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مسئولیت‌پذیری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>حفاظت محیط زیست</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مناطق روستایی بندرعباس</KeyText>
			</KEYWORD>
		</KEYWORDS>

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

	</ARTICLE>


	<ARTICLE> 
		<TitleF>اثر متغیرهای محیطی بر وقوع و گسترش بیماری طاعون نشخوارکنندگان کوچک در استان مرکزی</TitleF>
		<TitleE>The Effect of Environmental Factors on the Occurrence and Spread of Pest Des Petits Ruminants Disease in Markazi Province, Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>شیوع چند باره طاعون نشخوارکنندگان کوچک (PPR) طی ده سال گذشته در ایران با اثرات ویران &#8204;کننده&#8204;ای بر جمعیت&#8204;های بز وحشی، گوسپند وحشی، و نشخوارکنندگان کوچک اهلی همراه بوده است. پژوهش حاضر با هدف پیش&#8204;بینی گستره&#8204;ی احتمالی وقوع و شیوع بیماری، شناسایی عوامل محیطی و سیمای سرزمین مؤثر بر گسترش آن و شناسایی مسیرهای انتقال بیماری توسط میزبانان وحشی در استان مرکزی انجام شد. با استفاده از مدل بی&#8204;نظمی بیشینه، ارزیابی احتمال رخداد طاعون نشخوارکنندگان کوچک یکبار برای دام و حیات&#8204;وحش به صورت جداگانه و همچنین، برای هر دو گروه به&#8204;طور همزمان انجام گرفت. تئوری مدار&#8204;&#8204;الکتریکی نیز به منظور شناسایی مسیرهای جابه&#8204;جایی و انتقال بیماری از طریق میزبان&#8204;های وحشی ویروس طاعون نشخوارکنندگان کوچک مورد استفاده قرار گرفت. شاخص عملکرد مدل به ترتیب در مدل&#8204;&#8204;های اجرا شده با داده&#8204;های وقوع بیماری در دام، حیات&#8204;&#8204;وحش و دام-حیات وحش 0/727، 0/997 و 0/849 محاسبه گردید. بارش مرطوب&#8204;ترین ماه مهم&#8204;ترین متغیر تأثیر&#8204;گذار بر شیوع بیماری در استان مرکزی شناسایی شد. مسیرهای بالقوه مهاجرتی گوسپند وحشی حاصل از تئوری مدار&#8204;&#8204;الکتریکی منطبق بر مناطق دارای احتمال زیاد وقوع بیماری بود. نتایج مطالعه حاضر می&#8204;تواند در توسعه روش&#8204;های مدیریتی مؤثر بر پیشگیری از شیوع این بیماری کشنده در حیات وحش کشور مؤثر باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The prevalence of the Pest des petits ruminants (PPR) over the past ten years in Iran has resulted in devastating effects on the wild goat (Capra aegagrus) and mouflon (Ovis gmelini) populations, as well as small domestic ruminants. The aim of this study was to identify areas with high risk of PPR outbreak, determine the environmental and landscape factors affecting the spread of the disease, and identify the transmission corridors of the disease through the wild hosts of PPR virus in Markazi province. The risk of occurrence of PPR was mapped once in livestock and wildlife separately and also jointly for both groups using maximum entropy model. An electrical circuit model was used to identify migration corridors and evaluate the transmission of disease through the wild hosts of the PPR virus. The model performance index was calculated 0.727 for livestock, 0.997 for wild ruminants, and 0.849 for both groups. The results showed that precipitation of the wettest month was the most important variable affecting the prevalence of PPR. Potential migration corridors of wild sheep matched the areas where the risk of PPR occurrence was high. The results of the present study can be operative in developing effective methods to prevent the spread of this fatal disease in the country&#39;s wildlife.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>47</FPAGE>
			<TPAGE>64</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/212021/09/12021/07/22021/09/18
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/6/27
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/12021/11/72021/11/222021/12/27
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/10/6
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>اقدس</Name>
				<MidName></MidName>
				<Family>شریفات</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sharifa</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>a.sharifat91@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمودرضا</Name>
				<MidName></MidName>
				<Family>همامی</Family>
				<NameE>M. R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hemami</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mrhemami@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رسول</Name>
				<MidName></MidName>
				<Family>خسروی</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Khosravi</FamilyE>
				<Organizations>
				<Organization>دانشگاه شیراز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>r-khosravi@shirazu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>آزیتا</Name>
				<MidName></MidName>
				<Family>رضوانی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rezvani</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>azita.rezvani@na.iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Landscape connectivity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Wildlife disease</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>Distribution modeling</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Wild ruminants</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>پیوستگی سیمای سرزمین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بیماری‌های حیات‌وحش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بی‌نظمی بیشینه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدل‌سازی پراکنش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نشخوارکنندگان وحشی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Abubakar, M., S.M. Jamal, M.J. Arshed, M. Hussain and Q. Ali. 2009. Peste des petits ruminants virus (PPRV) infection; its association with species, seasonal variations and geography. Tropical animal health and production 41(7): 1197-1202.##2.	Abubakar, M., H. Ali Khan, M.J. Arshed, M. Hussain  and Q. Ali. 2011. Peste des petits ruminants (PPR): Disease appraisal with global and Pakistan perspective. Small Ruminant Research 96(1): 1-10.##3.	Adavodi, R., R. Khosravi, S.A. Cushman and M. Kaboli. 2019. Topographical features and forest cover influence landscape connectivity and gene flow of the Caucasian pit viper, Gloydius caucasicus (Nikolsky, 1916). in Iran. Landscape Ecology 34(11): 2615-2630. ##4.	Aguilar, X.F., M. Mahapatra, M. Begovoeva, G. Kalema-Zikusoka, M. Driciru, C. Ayebazibwe, D. Adwok, M. Kock, J.-P. Lukusa,J. Muro, I. Marco, A. Colom-Cadena, J. Espunyes, N. Meunier, O. Cabezón, A. Caron, A. Bataille, G. Libeau, K. Parekh, S. Parida and R. Kock. 2020. Peste des petits ruminants at the wildlife–livestock interface in the Northern Albertine Rift and Nile Basin, East Africa. Viruses 12(3): 293-311.##5.	Ahmed, M. 2008. Peste des Petits Ruminants transmission and spreading dynamics in the Sudan. PhD thesis University of Khartoum. Khartoum, Sudan.##6.	Anderson, M.C., J.M. Watts, J.E. Freilich, S.R. Yool, G.I. Wakefield, J.F. Mccaalery and A. Fahnestock. 2000. Regression – tree modeling of desert tortoise habitat in central Mojave. Ecological Applications 10: 890-900.##7.	Algeo, T. P., D. Slate, R.M. Caron, T. Atwood, S. Recuenco,M.J. Ducey, R.B. Chipman and M. Palace. 2017. Modeling Raccoon (Procyon lotor) Habitat Connectivity to Identify Potential Corridors for Rabies Spread. Tropical Medicine and Infectious Diseases 2(3): 44. ##8.	Ansari, A. 2017. Habitat evaluation for Persian Gazelle in the Southern half of Markazi province, Iran. Journal of Wildlife and Biodiversity 1(1): 19-23.##9.	Bakkouri, A. 2017. Unfolding the global strategy for the control and eradication of Peste des Petits Ruminants (PPR) in Africa. Available online at: https://www.oie.int/app/uploads/2021/03/2017-afr2-bakkouri-a.pdf . Accessed 11 January 2022.##10.	Baldwin, R.A. 2009. Use of maximum entropy modeling in wildlife research. Entropy 11: 854-866.##11.	Banyard, A.C., S. Parida, C. Batten, C. Oura, O. Kwiatek and G. Libeau. 2010. Global distribution of peste des petits ruminants virus and prospects for improved diagnosis and control. Journal of General Virology 91(12): 2885–97.##12.	Bazarghani, T. T., S. Charkhkar, J. Doroudi and E.B. Hassan. 2006. A review on Peste des petits ruminants (PPR) with special reference to PPR in Iran. Journal of Veterinary Medicine Series B 53: 8-17.##13.	Bellard, C., C. Bertelsmeier, P. Leadley, W. Thuiller and F. Courchamp. 2012. Impacts of climate change on the future of biodiversity. Ecology Letters 15: 365–377.##14.	Berger J, B. Buuveibaata and C. Mishra. 2013. Globalization of the cashmere market and the decline of large mammals in central Asia. Conservation Biology 27: 679–89.##15.	Bundza, A., A. Afshar, T.W. Dukes, G.C. Dulac and S.A. Becker. 1988. Experimental peste des petits ruminants (goat plague) in goats and sheep. Canadian Journal of Veterinary Research 52(1): 46-52.##16.	Cao, Z., Y. Jin, T. Shen, F. Xu and Y. Li. 2018. Risk factors and distribution for peste des petits ruminants (PPR) in Mainland China. Small Ruminant Research 162: 12–16.##17.	Cushman, S. A., E.L. Landguth and C.H. Flather. 2013. Evaluating population connectivity for species of conservation concern in the American Great Plains. Biodiversity and Conservation 22: 2583–2605. ##18.	Daszak, P., A.A. Cunningham and A.D. Hyatt. 2000. Emerging infectious diseases of wildlife - threats to biodiversity and human health. Science 287: 443-449.##19.	Ebrahimzadeh, H., H.S. Kafil and M. Asgharzadeh. 2016. Peste des petits ruminants (PPR): A Serious Threat for Wild Life. Advances in Bioscience and Clinical Medicine 4(2): 49–50.##20.	Esfandabad, B.S., M. Karami, M. Hemami and M. Karami. 2010. Habitat associations of wild goat in central Iran: implications for conservation. European Journal of Wildlife Research 56: 883–894.##21.	Estrada-Pena, A. and J. Venzal. 2007. Climate niches of tick species in the Mediterranean region: modeling of occurrence data, distributional constraints, and impact of climate change. Journal of Medical Entomology 44(6): 1130-1138.##22.	Elith, J. 2017. Predicting distributions of invasive species. Invasive species: Risk assessment and management , Cambridge University Press, London, England.##23.	Froese, J. 2017. Modelling seasonal habitat suitability and connectivity for feral pigs in northern Australia: towards risk-based management of infectious animal diseases with wildlife hosts. School of Agriculture and Food Sciences. PhD thesis.The University of Queensland. Brisbane, Australia. ##24.	Hemmatzadeh, F., W. Boardman, A. Alinejad, A. Hematzade and M.K. Moghadam. 2016. Molecular and serological survey of selected viruses in free-ranging wild ruminants in Iran. PLOS ONE 11(12): e0168756.##25.	Jolles, A.E., B.R. Beechler and B. Dolan. 2015. Beyond mice and men: environmental change, immunity and infections in wild ungulates. Parasite Immunoogy 37: 255–66.##26.	Kaszta, Ż., S. Cushman, D. Macdonald. 2020. Prioritizing habitat core areas and corridors for a large carnivore across its range. Animal Conservation 23(5): 607-616.##27.	Liu, Q., B. Kong, Y. L. Xiong and X. Xia. 2010. Antioxidant activity and functional properties of porcine plasma protein hydrolysate as influenced by the degree of hydrolysis. Food Chemistry 118: 403–410.##28.	Ma, J., J. Xiao, H. Liu, X. Gao, H. Chen and H. Wang. 2017. Spatiotemporal pattern of peste des petits ruminants and its relationship with meteorological factors in China. Preventive Veterinary Medicine 147: 194–198.##29.	Ma, J., X. Gao, B. Liu, H. Chen, J. Xiao and H. Wang. 2019. Peste des petits ruminants in China: Spatial risk analysis. Transboundary and Emerging Diseases 66(4): 1784-1788.##30.	Maiorano, L., L. Chiaverini, M. Falco and P. Ciucci. 2019. Combining multi-state species distribution models, mortality estimates, and landscape connectivity to model potential species distribution for endangered species in human dominated landscapes. Biological Conservation 237: 19-27.##31.	Martin, C., P. P. Pastoret, B. Brochier, M. F. Humblet and C. Saegerman. 2011. A survey of the transmission of infectious diseases/infections between wild and domestic ungulates in Europe. Veterinary Research 42(1). https://doi.org/10.1186/1297-9716-42-70. ##32.	McRae, B. H., B.G. Dickson, T.H. Keitt and V.B. Shah. 2008. Using circuit theory to model connectivity in ecology, evolution. and conservation. Ecology 89(10): 2712–2724.##33.	Miller, R. S., M. L. Farnsworth and J. L. Malmberg. 2013. Diseases at the livestock-wildlife interface: status, challenges, and opportunities in the united states. Preventive Veterinary Medicine 110(2): 119–32.##34.	Munir, M. 2014. Role of wild small ruminants in the Epidemiology of Peste des petits ruminants. Transboundary and Emerging Diseases 61: 411–424.##35.	Niu B, R. Liang, G. Zhou, Q. Zhang, Q. Qu X Su and Q. Chen. 2021. Prediction for global Peste des Petits Ruminants Outbreaks based on a combination of Random Forest algorithms and meteorological data. Frontiers in Veterinary Science 7:570829. https://doi.org/10.3389/fvets.2020.570829 .##36.	Ofori, B. Y., A. J. Stow, J. B. Baumgartner and L. J.  Beaumont. 2017. Influence of adaptive capacity on the outcome of climate change vulnerability assessment. Scientific Reports 7(1): 1-12.##37.	Phillips, S.J., R.P. Anderson and  R.E. Schapire. 2006. Maximum entropy modeling of species geographic distributions. Ecological Modeling 190: 231–259.##38.	Pigott, D. M., N. Golding, A. Mylne, Z. Huang, A. J. Henry, D. J. Weiss, O. J. Brady, M. UG. Kraemer, D.L. Smith, C. L. Moyes, S. Bhatt, P.W. Gething, P. W. Gething, P. W. Horby, I. I. Bogoch, J. S. Brownstein, S. R. Mekaru, A. J. Tatem, K. Khan and S. I. Hay . 2014. Mapping the zoonotic niche of Ebola virus disease in Africa. elife 3: e04395.##39.	Sallam, M. F., A. M. Al Ahmed, M.S. Abdel-Dayem and M. A. Abdullah. 2013. Ecological niche modeling and land cover risk areas for rift valley fever vector, Culex tritaeniorhynchus Giles in Jazan, Saudi Arabia. PLOS ONE 8(6): e65786. ##40.	Santhamani, R., R. P. Singh and F. Njeumi. 2016. Peste des petits ruminants diagnosis and diagnostic tools at a glance: perspectives on global control and eradication. Archives of Virology 161(11): 2953–2967. ##41.	Shahnaseri, G., M.-R. Hemami, R. Khosravi, S. Malakoutikhah, M. Omidi and S. A. Cushman. 2019. Contrasting use of habitat, landscape elements, and corridors by grey wolf and golden jackal in central Iran. Landscape Ecology 34(6):1263-1277. ##42.	Shams Esfandabad, B., M. Karami, M.-R. Hemami, B. Riazi and M.B. Sadough. 2010. Habitat associations of wild goat in central Iran: implications for conservation. European Journal of Wildlife Research (56): 883–894.##43.	Simons, R. R., S. Croft, E. Rees, O. Tearne, M. E. Arnold, and N. Johnson. 2019. Using species distribution models to predict potential hot-spots for rift valley fever establishment in the United Kingdom. PLOS ONE 14(12): e0225250.##44.	Smith, K. F., D.F. Sax and K. D. Lafferty. 2006. Evidence for the role of infectious disease in species extinction and endangerment. Conservation Biology 20(5): 1349–1357.##45.	Sony RK, S. Sen, S. Kumar, M. Sen and K.M. Jayahari. 2018. Niche models inform the effects of climate change on the endangered Nilgiri Tahr (Nilgiritragus hylocrius) populations in the southern Western Ghats , India. Ecological Engineering 120: 355-363.##46.	Taylor, W.P. 1984. The distribution and epidemiology of PPR. Preventive Veterinary Medicine 2: 157-166.##47.	Vander Wal E., D. Garant, S. Calmé, C. A. Chapman, M. Festa-Bianchet, V. Millien, S. Rioux-Paquette and F. Pelletier.2014. Applying evolutionary concepts to wildlife disease ecology and management. Evolutionary Applications 7: 856–868.##48.	Wilcove, D., D. Rothstein, J. Dubow, A. Phillips and E. Losos. 1998. Quantifying Threats to Imperiled Species in the United States. BioScience 48(8):607-615.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی توسعه شبکه مناطق حفاظتی استان مرکزی با استفاده از سنجه‌های سیمای سرزمین</TitleF>
		<TitleE>Assessment of the Conservation Area Network Development in Markazi Province Using Landscape Metrics</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>اولویت&#8204;بندی و انتخاب مناطق نمونه از کل طبیعت جهت حفاظت از تنوع زیستی ضروری است. هدف اصلی این تحقیق ارزیابی توسعه شبکه مناطق حفاظتی با سنجه&#8204;های سیمای سرزمین در استان مرکزی است. بدین منظور از نرم افزارهای MaxEnt، &#160;Marxan، &#160;Fragstst 4.2 &#160;و هشت معیار حفاظتی استفاده شد. &#160;نتایج حاصل با الگوریتم&#8204;های مذاب&#8204;سازی شبیه&#8204;سازی شده، حریص و نادر و سنجه&#8204;های مختلف سیمای&#8204;سرزمین مقایسه شد. برای مدل&#8204;سازی زیستگاه گونه&#8204;ها از روش حداکثر آنتروپی استفاده شد. بررسی نتایج سناریوهای مختلف حفاظتی نشان داد که هدف حفاظتی30 درصد با BLM معادل 30 به&#8204;عنوان مناسب&#8204;ترین گزینه می&#8204;باشد. الگوریتم مذاب&#8204;سازی شبیه&#8204;سازی شده نتایج قابل قبول&#8204;تری را در تمام موارد ارائه داد و نتایج همپوشانی مناطق منتخب حفاظتی با مناطق تحت حفاظت موجود در استان مرکزی نشان داد که در برآوردن هدف حفاظتی 30 درصد تنها دو معیار حفاظتی موفق است. که از لحاظ دستیابی به اهداف حفاظتی، کارایی مناسبی را ندارد. در اغلب سناریوها، هم&#8204;پوشانی شبکه&#8204;های حفاظتی منتخب با مناطق تحت حفاظت موجود کمتر از 45/31 درصد است. نتایج سنجه&#8204;های سیمای سرزمین نشان داد فاصله مناطق حفاظتی از یکدیگر متغییر است. تنوع و فراوانی مناطق حفاظتی کم &#160;است. بنابراین شبکه مناطق حفاظتی استان مرکزی جزء زیست بوم&#8204;های آسیب پذیر با شکنندگی زیاد &#160;قرار دارد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Prioritization and selection of sample areas from the whole nature is necessary to protect biodiversity. The main purpose of this study was to evaluate the development of a network of conservation areas in Markazi province using landscape metrics. For this purpose, we used MaxEnt, Marxan, Fragstat softwares and eight conservation criteria. Results were compared by using simulated sorting, greedy, best and max rarity algorithms and different landscape metrics. Maximum entropy method was used to model the wildlife habitats. The results of different protection scenarios showed that a 30% conservation target with a Boundary Length Modifier (BLM)of 30 is the most appropriate option. The simulated sorting algorithm provided &#160;more acceptable results in all cases. Overlaping &#160;the selected protection areas with the map of protected areas in Markazi province showed that only two protection criteria, out of the 8 selected criteria, are successful in providing the 30% protection target, which is not efficient in terms of achieving protection goals. In most scenarios, the overlap of the selected protection networks with the existing protected areas are less than 31.45%.Results of landscape metrics showed that the distance between conservation areas varies. The diversity and abundance&#160; of the conservation areas are low. . Therefore, the conservation areas in Markazi province are among the vulnerable ecosystems with high fragility.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>65</FPAGE>
			<TPAGE>80</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/212021/09/12021/07/22021/09/182021/09/8
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/6/17
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/12021/11/72021/11/222021/12/272022/02/13
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/11/24
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>امیر</Name>
				<MidName></MidName>
				<Family>انصاری</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ansari</FamilyE>
				<Organizations>
				<Organization>دانشگاه اراک</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>A-ansari@araku.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Marxan</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>MaxEnt</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>Markazi province</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Marxan</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>MaxEnt</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سنجه سیمای‌سرزمین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استان مرکزی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Ardron, J.A., H.P. Possingham and C.J. Klein. 2008. Marxan good practices handbook. External review version, 17 May, 2008.Pacific Marine Analysis and Research Association, Vancouver, BC, Canada. 155 p, viewed 10 December 2010, www.pacmara.org.##2.	Barati, B., B. Raygani, A. Jahani, and L. Zebardast. 2017. Integration assessment of the protected areas using landscape ecological approach (case Study: Kolah Ghazy National Park and Wildlife Refuge). The Journal of Town and Country Planning 9(1): 153-168##3.	Botequila Leitao, A., M. Jozeph and J. Ahern .2006. Measuring landscapes: A planner's handbook##4.	DOE Markazi .2010. Natural Features Atlas of Markazi Province. Publisher: NAQSH-E MANA by Order of Department of Environment Markazi. (In Farsi) ##5.	Esfandeh, S., M. Kaboli and L. Eslami. 2015. A chronological review on application of Marxan tool for systematic conservation planning in landscape. International Journal of Engineering and Applied Sciences 2(12): 2439-3661. (In Farsi)##6.	Esfandeh, S., M. Kaboli and L. Eslami. 2017. Simulated annealing algorithm as a tool for systematic prioritization of protected area in Alborz province, Iran. Journal of Animal Environment 9(1):105-122. (In Farsi)##7.	Game, E.T. and H.S. Grantham. 2008. Marxan User Manual: For Marxan version1,8,10. University of  Queensland, St. Lucia, Queensland, Australia, and Pacific Marine Analysis and Research Association, Vancouver, British Columbia, Canada, viewed 10 December 2010.##8.	Haghverdi, A., A. Jahani, L. Zebardast, M. Makhdoum, H. Goshtasb. 2018. Quantifying the Fragmentation of the Wildlife Habitat Using Landscape Ecology Approach (Case Study (Lar National Park and Varjin Protected Area). Animal Environment 10(2): 21-32.##9.	Karami, A and  J. Feghhi. 2012. Investigation of Quantitative metrics to protect the landscape in land use by sustainable pattern (Case study: Kohgiluyeh and Boyer Ahmad). Journal of Environmental Studies 37(60): 79-88. (In Farsi)##10.	Klein, C. J., Wilson, K. A., Watts, M., Stein, J. Carwardine, J., Mackey, B. Possingham, H. P. 2009. Spatial conservation prioritization inclusive of wilderness quality: A case study of Australia's biodiversity, Biological Conservation. 142(7): 1282-1290.##11.	Leslie, H., M. Ruckelshaus, I. R. Ball, S. Andelman, and P.H. Possingham. 2003. Using sitting algorithms in the design of marine reserve networks. Ecological Applications  69(6): 622-632.##12.	Lessmann, J., J. Munoz and E. Bonaccorso. 2014. Maximizing species conservation in continental Ecuador; a case of systematic conservation planning for biodiverse regions. Ecology and Evolution. doi: 10.1002/ece3.1102.##13.	McGarigal, K. 2002. FRAGSTATS: Spatial Pattern Analysis Program for Categorical Maps, Computer software program produced by the authors at the University of Massachusetts, Amherst. Available at: http:/www.umass.edu/ landeco/research/fragstats/fragstats.html.##14.	Mehri, A., A. Salmanmahiny, S.H. Mirkarimi, and H.R. Rezaei. 2014.  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Hansen and K. Jones. 2008, Prioritizing avian conservation areas for the Yellowstone to Yukon Region of North America. Biological Conservation 141 (4): 908-924.##19.	Phillips, S.J., R.P. Anderson and R.E. Schapire. 2006. Maximum entropy modeling of species geographic distributions. Ecological modelling 190(3).##20.	Possingham, H.P., I.R. Ball and S., Andelman. 2000. Mathematical methods for identifying representative reserve networks. In: Ferson S, Burgman M (Eds.), Quantitative Methods for Conservation Biology. Springer-Verlag, New York, pp: 291-305.##21.	Possingham, H.P., K.A., Wilson, S.J. Andelman, and C.H. Vynne. 2006. Protected areas. Goals, limitations, and design. pp: 507-549 in M. J. Groom, G. K. Meffe, C. R. Carroll, eds. Principles of conservation biology. 3rd ed. Sinauer Associates, Inc. Sunderland, MA.##22.	Rezazadeh, S.,  A., Jahani, M. Makhdoum and H. Goshtasb Meigooni. 2017. 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Possingham. 2005. Efficiency, costs and trade-offs in marine reserve system design. Environmental Modeling and Assessment 10: 203-213.##28.	Wu, R., Y., Long, G.P. Malanson, P.A. Garber, and S. Zhang. 2014. Optimized Spatial Priorities for Biodiversity Conservation in China: A Systematic Conservation Planning Perspective. PLoS ONE 9(7): e103783.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>آشکارسازی رخداد تغییر اقلیم براساس شاخص‌های دمایی گرم در اکوسیستم جنگلی زاگرس؛ استان چهارمحال و بختیاری</TitleF>
		<TitleE>Detection of Climate Change Based on Warm Temperature Indices in Zagros Forest Ecosystem; Chaharmahal and Bakhtiari Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>باوجودی که یکی از مهم&#8204;ترین عوامل موثر بر زوال و خشکیدگی جنگل&#8204;های زاگرس رخداد تغییر اقلیم به&#8204;ویژه طی دو دهه اخیر است، تخریب و زوال جنگل&#8204;های زاگرس هم می&#8204;تواند روند رخداد تغییر اقلیم را در این اکوسیستم تشدید کند. به&#8204;منظور آشکارسازی رخداد تغییر اقلیم در جنگل&#8204;های استان چهار محال و بختیاری با گونه غالب بلوط ایرانی (Quercus brantii)، از داده&#8204;های روزانه پارامترهای دمای حداقل، دمای حداکثر و بارش استفاده شد. داده&#8204;ها از نظر کیفیت و همگنی بررسی و برای ورود به مدل اقلیمی آشکارکننده رخداد تغییر اقلیم آماده شدند. شاخص&#8204;های دمایی گرم آشکارکننده تغییر اقلیم با استفاده از نرم&#8204;افزار ClimPACT در محیط برنامه&#8204;نویسی R 2.10 برای دوره آماری 2019-1992محاسبه شدند. روند تغییرات، خطای شیب روند و معنی&#8204;داری تغییرات با P-Value=0.05 استخراج شد. نتایج نشان داد در تمام سایت&#8204;های پایش زوال شاخص&#8204;های دمایی گرم شامل 2TX2TN SU35 ,SU30 ,SU25 ,TN90p ,TX90p , TX50p, WSDI6 ,WSDI2 روند افزایشی و معنی&#8204;داری داشتند. تغییرات شیب روند شاخص&#8204;ها با شروع پدیده زوال همخوانی داشته و در دو دهه اخیر از شدت بیشتری برخوردار بوده است. با توجه به روند افزایش دما این روند افزایشی شاخص&#8204;ها در سال&#8204;های آینده نیز تداوم داشته و جنگل&#8204;های منطقه با تنش خشکی بیشتری مواجه خواهند شد. آگاهی از شدت تغییرات رخ داده و تداوم آن در آینده می&#8204;تواند مدیران و برنامه&#8204;ریزان اکوسیستم جنگلی زاگرس را در راهکارهای عملیاتی در سازگاری با تغییر اقلیم جهت حفظ و احیاء جنگل یاری کند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Although one of the most important factors affecting the decline and drying of Zagros forests is the occurrence of climate change, especially during the last two decades, the degradation and decline of Zagros forests can intensify the trend of climate change in this ecosystem. In order to detect the occurrence of climate change in the Zagros oak (Quecus brantii) forests of Chaharmahal and Bakhtiari province, daily data of minimum temperature, maximum temperature and precipitation parameters were used. Data were analyzed for quality and homogeneity and prepared to enter into the climate model that reveals the occurrence of climate change. Warm temperature indicators for climate change detection were calculated, using ClimPACT software in R 2.10 programming environment for the &#160;period of 1992-1999. Trend change, trend slope error and significance of changes were extracted at p = 0.05. The results showed that at all monitoring sites, hot temperature indices, including 2TX2TN SU35, SU30, SU25, TN90p, TX90p, TX50p, WSDI6, WSDI2, had a significantly increasing trend. Changes in the slope of the trend of these indicators coincided with the beginning of the decline phenomenon and have been more intense in the last two decades. Due to the increasing trend of temperature, this increasing trend of indicators will continue in the coming years and the forests of the region will face more drought stress. Awareness of the severity of the changes that have occurred and their continuation in the future can help managers and planners of the Zagros forest ecosystem in operational solutions in adapting to climate change to preserve and rehabilitate forests.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>81</FPAGE>
			<TPAGE>99</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2021/08/212021/09/12021/07/22021/09/182021/09/82021/10/10
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1400/7/18
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/11/12021/11/72021/11/222021/12/272022/02/132022/02/6
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/11/17
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فاطمه</Name>
				<MidName></MidName>
				<Family>درگاهیان</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dargahian</FamilyE>
				<Organizations>
				<Organization>موسسه تحقیقات جنگلها و مراتع کشور</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>fatemeh.dargahian@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>پورهاشمی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Pourhashemi</FamilyE>
				<Organizations>
				<Organization>موسسه تحقیقات جنگلها و مذاتع کشور</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>doveyse@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Climate adaptation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Drought stress</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>decline and drying</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Warm temperature indices</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تنش خشکی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سازگاری اقلیمی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص‌های دمایی گرم</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>زوال و خشکیدگی</KeyText>
			</KEYWORD>
		</KEYWORDS>

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

	</ARTICLE>

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