<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1400</YEAR>
<VOL>10</VOL>
<NO>1</NO>
<MOSALSAL>35</MOSALSAL>
<PAGE_NO>92</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>مقایسه خوش‌خوراکی چند گونه مرتعی برای چرای گوسفند 
(مطالعه موردی: مراتع روستای ده‌شیخ در استان کهگیلویه و بویراحمد)</TitleF>
		<TitleE>Comparing the Palatability of Some Plant Species for Sheep Grazing (Case Study: Rangelands of Deh- Shiekh in Kohkiloyeh and Boyer Ahmad Province)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>آگاهی از خوش&#172;خوراکی گونه&#8204;های گیاهی در برآورد تولید علوفه قابل&#8204; دسترس دام در هر رویشگاه مرتعی امری ضروری است. در این تحقیق از روش زمان&#8204;سنجی با هدف تعیین خوش&#172;خوراکی سه گونه چند&#8204;ساله Gundelia tournefortii، Bromus tomentellus و Hordeum bulbosum و دو گونه یک&#8204;ساله Aegilops triuncialis و Taeniatherum crinitum در مراتع روستای ده&#8204;شیخ در استان کهگیلویه و بویراحمد استفاده شد، به این صورت که از چرای دو رأس گوسفند از گیاهان مختلف (بعد از یک ساعت چرای عادی با هدف حذف اثر گرسنگی دام) زمان&#8204;سنجی به&#172;عمل آمد و مدت&#8204;زمان چرای دام از هر گونه گیاهی مشخص شده و با توجه به &#8204;کل زمان چرا، درصد خوش-خوراکی هر گونه تعیین شد. نتایج این تحقیق نشان داد گونه&#8204;های مورد مطالعه در زمان&#8204;های مختلف در طول روز دارای خوش&#172;خوراکی یکسانی برای گوسفند هستند. همچنین نتایج نشان داد در مرحله رشد رویشی و گلدهی، گونه Hordeum bulbosum به&#172;ترتیب با 24/01 و 29/70 درصد و در مرحله بذردهی نیز گونه&#8204; Bromus tomentellus با 22/44 درصد، دارای بیشترین خوش&#172;خوراکی بودند؛ بنابراین می&#8204;توان سیستم چرا برای این مرتع را طوری اعمال کرد که هر تیپ گیاهی زمانی مورد چرا واقع شود که در آن مرحله از رشد، گونه&#8204;های تشکیل&#8204;دهنده آن تیپ، بیشترین خوش&#172;خوراکی را برای گوسفند داشته باشند. با اعمال چنین سیستم چرایی، از یک&#8204;طرف عملکرد دام افزایش پیدا می&#8204;کند و از طرف دیگر دام با عدم نیاز به لگدکوبی گونه&#8204;ها برای پیدا کردن گونه خوش&#172;خوراک، باعث از بین رفتن سایر گونه&#8204;ها نمی&#172;شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Awareness of rangelands plants palatability is required for estimating available forage to animals in all plant communities. In this research recording method was used to determine species palatability in rangelands of Deh- Shiekh in Kohkiloyeh and Boyer Ahmad Province. Three perennial species including Gundelia tournefortii, Bromus tomentellus, Hordeum bulbosum and two annual species of Agelups triancialis and Treniatherum crinitum were selected. Livestock grazing from different plants was recorded and the time was measured. After one hour, normal grazing was performed and the duration of livestock grazing on each species was determined. &#160;Based on the duration of &#160;grazing on each species, palatability percentage of each species was estimated. Results showed that the studied species had similar palatability for sheep at different time of the day. Among the species, during vegetative and flowering stages, Hordeum bulbosum showed the highest palatability with an amount of 24.01 and 29.70 percent respectively. Bromus tomentellus showed the highest palatability in seed maturity period (22.44%). Thus, it is possible to control the grazing system to graze each plant type at one stage of growth with the highest palatability. Using this kind of grazing system increases livestock performance, decreases soil compaction and helps to conserve rangeland plants.&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>13</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/11/15
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/8/25
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/2
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/2/12
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>وحید</Name>
				<MidName></MidName>
				<Family>سیاره</Family>
				<NameE>V.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sayare</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>vahid.sayare@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>حسین</Name>
				<MidName></MidName>
				<Family>ارزانی</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Arzani</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>harzani@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علی</Name>
				<MidName></MidName>
				<Family>طویلی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Tavili</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>atavili@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد علی</Name>
				<MidName></MidName>
				<Family>زارع چاهوکی</Family>
				<NameE>M. A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Zare Chahouki</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mazare@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Deh-Sheikh Rangelands</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Palatability</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Phenological stages</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Sheep</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>مراتع ده‌شیخ</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>خوش‌خوراکی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گوسفند</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گونه‌های مرتعی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Alilou, F., F. Keivan Behjou, E. Sheidae Karkaj, R. Ahmadkhani and J. Motamedi. 2017. Surveying effect of livestock grazing management on functional and structural characteristics of ecosystem in khoy mountain rangelands. Iranian Journal of Range and Desert Research 24(3): 596-609. (In Farsi)##2.	Arzani, H. and K. Naseri. 2007. Livestock feeding on pasture. University of Tehran Press, Tehran. (In Farsi)##3.	Arzani, H. and M. Jafari Shalamzari. 2015. Targeted grazing. University of Tehran Press, Tehran. (In Farsi)##4.	Arzani, H. 2011. Forage quality and daily requirement of grazing animal. University of Tehran Press, Tehran. (In Farsi)##5.	Arzani, H., H. Piri Sahragard, J. Turkan and K. Saedi. 2010. Comparison of forage quality of some plant species of Saral Kurdistan rangelands in different phenological stages. Iranian Journal of Rangeland 4(2): 160-167. (In Farsi)##6.	Arzani, H., M. Zohdi, E. Fisher, G. H. Zahedi Amiri, A. Nikkhah and D. Wester. 2004. Phenological effects on forage quality of five grass species. Iranian Journal of Range Management 57: 624-630. (In Farsi)##7.	Baghestani Meybodi, N. and H. Arzani. 2006. An investigation of range plants, palatability and goat behaviour in Posht-Kooh rangelands, Yazd Province. Iranian Journal of Natural Resources 58(4): 109-119. (In Farsi)##8.	Baghestani Meybodi, N., M. Zargaran and A. Javadi. 2010. Investigating the preference value of rangeland species of camel's grazing in Halvansh Tabas area. Iranian Journal of Renewable Natural Resources Research 3(1): 53-61. (In Farsi)##9.	Baghstani Meybodi, N., M. Zare and M. Fayaz. 2013. Study of palpability of range plants in steppe rangelands of Yazd province (case study: the Nodoshan site in Sadogh City). Iranian Journal of Range and Desert Research 20(4): 809-818. (In Farsi)##10.	Charesaz, N., H. Arzani and H. A. Jafari. 2010. Investigation of variations in percentage of soluble carbohydrates in three species of Agropyron intermedium, Bronus tomentellus, Dactylis glomerata in three phonological stages. Rangeland 4(1): 121-129. (In Farsi)##11.	Delavaripour, A. 2005. Comparison of the palatability of some important species of Yazd rangelands in relation to sheep and goat grazing, MSc. thesis. Islamic Azad University, Science and Research Branch, Tehran. (In Farsi)##12.	Ghodsi Rasi, H. and H. Arzani. 1997. Investigation of the factors effective on the palatability of important rangeland species in Chahar Bagh area of Gorgan. Iranian Journal of Pajouhesh-va-Sazandegi 36: 50-53. (In Farsi)##13.	Gibson, R. S. and O. J. H. Bosch. 1996. Indicator species for the interpretation of vegetation condition in the ST Bathans area, Central Otago, New Zealand. New Zealand Journal of Ecology 20(2): 163-172.##14.	Graham, N. K. and A. D. Wilson. 1980. Methods of measuring secondary production from browse. In: Browse in Africa: Papers presented at the International Symposium. ILCA, Addis Ababa, Ethiopia. pp. 255-259.##15.	Habibian, S., H. Arzani and S. Habibian. 2013. Comparison of two methods of preference value determination of plant species for goat in semi-steppe rangelands in Fars Province. Iranian Journal of Plant Ecophysiology 5(13): 81-95. (In Farsi)##16.	Hasani, J. and M. Fayaz. 2014. Investigation on preference value of range species and grazing behavior in Qorveh rangelands of Kurdistan. Iranian Journal of Range and Desert Research 21(2): 357-367. (In Farsi)##17.	Heady, H. F. and R. D. Denis. 1994. Rangeland and ecology and management. West View Press, USA.##18.	Heady, H. F. 1974. Palatability of herbage and animal preference. Journal of Range Management 17: 76-83.##19.	Heshmaty, G., H. Baghani and M. Bazrafshan. 2006. Comparison of nutritional value of 11 rangeland species in the east of Golestan province. Iranian Journal of Research and Development in Natural Resources 73: 90-95. (In Farsi)##20.	Holchek, J. I., C. H. Herbal and R. D. Pieper. 2004. Range management principles and practices. Prentice Hall Pub., USA.##21.	Khalasi Ahvazi, L., G. A. Heshmati, P. Zoofan and M. Akbarlou. 2016. Habitat factors impact on nutritional values of Gundelia tournefortii L. at phenological stages in the north east of Khozestan Province. PEC 4(8): 30-48. (In Farsi)##22.	Khodagholi, M., R. Saboohi, M. Bayat and J. Motamedi. 2020. Diet selection and palatability of plant species for Naiini sheep grazing in steppe rangelands of Meymeh, Isfahan. Journal of Range and Watershed Management 73(1): 65-74. (In Farsi)##23.	Krueger, W. C. 1972. Evaluating animal forage preference. Journal of Range Management 25: 471-475.##24.	Mesdaghi, M. 2016. Range managment in Iran. Astan Ghods Razavi press, Mashhad. (In Farsi)##25.	Mirdavudi, H. and A. Sanadgol. 2009. Study of preference value of range plants in key ranges of Anjedan’s rangelands of Markazi province. Iranian Journal of Range and Desert Research 16(2): 190-199. (In Farsi)##26.	Motamedi, J. and H. Solaly. 2018. The preference value of Makuyi sheep on the mountainous rangelands of Kelid Daghi in Jolfa. Iranian Journal of Animal Sciences 30(11): 3-16. (In Farsi)##27.	Moghadam, M. R. 2008. Rangeland and rangeland management. University of Tehran Press, Tehran. (In Farsi)##28.	Moghimi, J. 2005. Introduction of some important rangeland species for improvement of Iranian rangelands. Arvan Press, Tehran. (In Farsi)##29.	Nyamangara, M. E. and L. R. Ndlovu. 1995. Feeding behaviour, feed intake, chemical and botanical composition of the diets of indigenous goats raised on natural vegetation in a semi-arid region of Zimbabwe. The Journal of Agricultural Science 124(3): 455-461.##30.	Raufirad, V., A. Ebrahimi, H. Arzani and Z. Shojaei Asadeiye. 2014. Investigation on relationship between palatability and forage quality in some of rangeland plants, (case study: Karsanak rangelands of Chaharmahal-va-Bakhtiari Province). Iranian Journal of Range and Watershed Management 66(1): 111-120. (In Farsi)##31.	Roost, F. 2016. Comparison of preference value of several rangeland indicators in different phenological stages in rangelands around Sanandaj, Master of Science thesis. The University of Kordestan, Sanandaj, Iran. (In Farsi)##32.	Shahbandari, R., H. Arzani, N. Baghestani Meybodi and M. Zare Chahouki. 2017. Investigation of the quality of plant species parts in different phenological stages using NIRs (case study: rangelands of Nodooshan-Yazd). Iranian Journal of Range and Watershed Management 70(1): 139-149. (In Farsi)##33.	Shakeri Boroojeni, N., H. Bashari and M. Tarkesh. 2014. Identifing grazing indicator species using gradient analysis approach in Semi-Steppe rangelands of Feridan-Isfahan. Rangeland 8(2): 201-212. (In Farsi)##34.	Shirmardi, H., F. Beldaji, M. Mesdaghi and A. Chamani. 2004. Determination of nutritional value of six species of rangelands in the rangelands of Marouge Tape Plain. Iranian Journal of Agricultural Sciences and Natural Resources 10: 131-149. (In Farsi)##35.	Stoddart, L. A., A. D. Smith and T. W. Box. 1975. Range Management. McGrow-Hill, USA.##36.	Tatian, M., R. Tamartash and A. Mirjalili. 2016. Comparing nutritional values of the three rangeland species; Hordeum bulbosum, Trifolium repens and Prangos ferulacea in different phenological stages in the rangelands of Bagh Shadi, Yazd province. PEC 3(7): 59-72. (In Farsi)##37.	Vallentine, J. F. 2001. Grazing management, 2nd Edition. Academic Press, San Diego.##38.	Zamani, G., A. Ranjbar and M. Saeedfar. 2010. Comparative study of Astragalus effusus Bunge forage quality in three growth stage and management system. Iranian Journal of Forest and Range Protection Research 8(1): 1-9. (In Farsi)##39.	Zohdi, M. 2002. Determination and comparison of TDN in distinguishable organs of five forage species, MSc. thesis. University of Tehran, Tehran. (In Farsi)## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>انتخاب نواحی مناسب برای کاشت حرا Avicennia marina در منطقه ساحلی بوشهر با استفاده از روش بهترین- بدترین و تصمیم‌گیری چندمعیاره</TitleF>
		<TitleE>Suitable Site Selection for Avicennia marina Plantation in the Coastal Region of Bushehr, using Best-Worst Multi-Criteria Decision-Making Method</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>این مطالعه به&#8204;منظور شناسایی مناطق مستعد کاشت حرا در خور سلطانی در ساحل شهر بوشهر انجام شد. معیارهای مؤثر جهت کاشت و توسعه حرا در این مطالعه شامل ویژگی&#8204;های زمین (کاربری اراضی، شیب، ارتفاع، هدایت الکتریکی خاک، بافت خاک، و نوع خاک)، آب دریا (دامنه جزر و مد، موج، pH، هدایت الکتریکی، و شوری) و اقلیم (دما، رطوبت نسبی، بارش، حداقل و حداکثر دمای مطلق) است. با استفاده از یک شبکه آماربرداری سیستماتیک- تصادفی، نقاط نمونه&#172;گیری مشخص و 10 نمونه آب و خاک برداشت و متغیرهای فیزیکی و شیمیایی آنها اندازه&#172;گیری شد. نقشه&#172;های موضوعی معیارها تهیه و از سیستم اطلاعات جغرافیایی برای مدل&#8204;سازی و تحلیل فضایی و تلفیق لایه&#8204;ها استفاده شد. با استفاده از نظر کارشناسان و تحقیقات گذشته و با کمک روش دلفی، ارجحیت معیار تعیین شده و معیارها با روش بهترین- بدترین (Best-Worst method) وزن&#8204;دهی شدند. با روی&#172;هم&#8204;گذاری معیارهای وزن&#172;داده&#8204;شده با روش وزن&#8204;دهی افزودنی ساده (Weighted Linear Combination= WLC)، مکان&#8204;های مناسب کاشت و توسعه گونه حرا به طبقات نامناسب، نسبتاً مناسب و مناسب طبقه&#8204;بندی شد. نتایج نشان داد 24 درصد از مناطق (18/25 هکتار) در محدوده مناسب، 24/3 درصد (18/5 هکتار) در محدوده نسبتاً مناسب، و 51/8 درصد (39/4 هکتار) در طبقه نامناسب برای کاشت این گونه قرار دارد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>This study was conducted to identify suitable sites for planting Avicennia marina in Soltani Khore of the urban coast of Bushehr. The most effective criteria for Avicennia marina planting include land characteristics (i.e. land use, slope, elevation, soil electrical conductivity, soil texture, and soil type), seawater (i.e. tidal range, wave, acidity, electrical conductivity, and salinity), and climate (i.e. temperature, relative humidity, precipitation, absolute minimum and maximum temperatures) were considered. Ten soil and water samples were collected, using a systematic-random sampling network and their physicochemical variables were measured. The thematic maps of the criteria were prepared and the geographic information system was used to analyse and present spatial data. Using expert opinions and literature review, the priority of the criteria was determined by Delphi method and the criteria were weighted by the Best-Worst method (BWM). Based on the overlay of weighting criteria, using Weighted Linear Combination (WLC), suitable sites for planting and development of Avicennia marina were classified as suitable, relatively suitable and not suitable. The results showed that 24% (18.25 ha) of the total areas were suitable, 24.3% (18.5 ha) of the land was relatively suitable, and 51.8% (39.4 ha) was not suitable for planting and development of Avicennia marina species.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>15</FPAGE>
			<TPAGE>33</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/11/152020/03/1
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/12/11
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/22021/05/12
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/2/22
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>گلستانی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Golestani</FamilyE>
				<Organizations>
				<Organization>گروه منابع طبیعی، واحد بوشهر، دانشگاه آزاد اسلامی، بوشهر، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>golestanimohammad13@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فاضل</Name>
				<MidName></MidName>
				<Family>امیری</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Amiri</FamilyE>
				<Organizations>
				<Organization>دانشیار گروه منابع طبیعی و محیط زیست، واحد بوشهر، دانشگاه آزاد اسلامی، بوشهر، ایران،</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>famiri@iaubushehr.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Avicennia marina</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Site selection</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>GIS</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Best-Worst method (BWM)</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Multi-criteria evaluation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Soltani Khore</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Urban coastal zone</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مانگرو</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مکان‌یابی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سامانه اطلاعات جغرافیایی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>روش بهترین- بدترین</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ارزیابی چندمعیاره</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خور سلطانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>منطقه ساحلی شهری</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Akram, A., A. Alfarhan, E. Robinson and I. Aldjain. 2008. Pattern of survival and mortality of mangrove populations grown at Al-Jubail area (Saudi Arabia) of the Arabian Gulf. American Journal of Agricultural and Biological Science 3(3): 610-616.##2.	Amiri, F. and T. Tabatabaie. 2020. The influence of green spaces on land surface temperature and humidity of the surrounding environment in Bushehr city. Environmental Sciences 18(3): 134-160. (In Farsi) ##3.	Andon Petrosian, H., A. Danehkar, S. Ashrafi and J. Feghhi. 2013. Application of delphi method for prioritization of Mangrove afforestation site selection criteria (case study: Grey Mangroves on north part of Persian Gulf, Iran). Environment and Development Journal 4(7): 37-48. (In Farsi)##4.	Berger, U., V. H. Rivera-Monroy, T. W. Doyle, F. Dahdouh-Guebas, N. C. Duke, M. L. Fontalvo-Herazo, H. Hildenbrandt, N. Koedam, U. Mehlig, C. Piou and R. R. Twilley. 2008. Advances and limitations of individual-based models to analyze and predict dynamics of mangrove forests: A review. Aquatic Botany 89(2): 260-274. https://doi.org/10.1016/j.aquabot.2007.12.015.##5.	Bhalla, R., S. Ram and V. Srinivas. 2008. Studies on vulnerability and habitat restoration along the coromandel coast. Publication of UNDP/UNTRS &#38; FERAL, India.##6.	Brunelli, M. and J. Rezaei. 2019. A multiplicative best–worst method for multi-criteria decision making. Operations Research Letters 47(1): 12-15. doi:https://doi.org/10.1016/j.orl.2018.11.008.##7.	Dahdouh-Guebas, F. and N. Koedam. 2008. Long-term retrospection on mangrove development using transdisciplinary approaches: A review. Aquatic Botany 89(2): 80-92. https://doi.org/10.1016/j.aquabot.2008.03.012.##8.	Das, G. K. 2013. Characteristics of mangrove substrate sediments of sunderbans. Reason- A technical journal, Vol. XII: 7-18.##9.	Das, S. and A. S. Crépin. 2013. Mangroves can provide protection against wind damage during storms. Estuarine, Coastal and Shelf Science 134: 98-107. https://doi.org/10.1016/j.ecss.2013.09.021.##10.	Dehghani, M., P. Farshchi, A. Danekar, M. Karami and A. Aleshikh. 2010. Recreation value of hara biosphere reserve using willingness-to-pay method. International Journal of Environmental Research 4(2): 271-280. https://doi.org/ 10.22059/IJER.2010.19.##11.	Dehghani, M., M. Pourhashemi, N. Shabanian and Kh. Mirakhorlou. 2014. Identification of suitable sites for development of mangrove forests in Holor region, Qeshm Island. Forest Sustainable Development 1(2): 151-165. (In Farsi)##12.	Ellison, A. M. 2008. Mangrove ecology-applications in forestry and coastal zone management. Aquatic Botany 89(2): 77-89.##13.	Friess, D. A. 2017. Mangrove rehabilitation along urban coastlines: a singapore case study. Regional Studies in Marine Science 16: 279-289. https://doi.org/10.1016/j.rsma.2017.09.013.##14.	Gilman, E. and J. Ellison. 2007. Efficacy of alternative low-cost approaches to mangrove restoration, American Samoa. Estuaries and Coasts 30(4): 641-651. https://doi.org/10.1007/BF02841961.##15.	Jafarnia, Sh., J. Oladi and O. Karami. 2013. Application of GIS-AHP in land evaluation for mangrove forest development in Qeshm Island based on physical-chemical water and soil characteristics. Journal of RS and GIS for Natural Resources (Journal of Applied RS &#38; GIS Techniques in Natural Resource Science) 4(1): 79-91. (In Farsi)##16.	Joshi, H. and M. Ghose. 2003. Forest structure and species distribution along soil salinity and pH gradient in mangrove swamps of the Sundarbans. Tropical Ecology 44(2): 195-204.##17.	Kamali, B. and R. Hashim. 2011. Mangrove restoration without planting. Ecological Engineering 37(2): 387-391. https://doi.org/10.1016/j.ecoleng.2010.11.025.##18.	Kaur, L., M. S. Rishi, G. Singh and S. Nath Thakur. 2020. Groundwater potential assessment of an alluvial aquifer in yamuna sub-basin (Panipat region) using remote sensing and GIS techniques in conjunction with analytical hierarchy process (AHP) and catastrophe theory (CT). Ecological Indicators 110: 105850. https://doi.org/10.1016/j.ecolind.2019.105850.##19.	Leo, K. L., C. L. Gillies, J. A. Fitzsimons, L. Z. Hale and M. W. Beck. 2019. Coastal habitat squeeze: a review of adaptation solutions for saltmarsh, mangrove and beach habitats. Ocean &#38; Coastal Management 175: 180-190.##20.	Lewis, R. R. 2005. Ecological engineering for successful management and restoration of mangrove forests. Ecological Engineering 24(4): 403-418. https://doi.org/10.1016/j.ecoleng.2004.10.003.##21.	Li, W., H. El-Askary, M. A. Qurban, J. Li, K. P. ManiKandan and T. Piechota. 2019. Using multi-indices approach to quantify mangrove changes over the Western Arabian Gulf along Saudi Arabia coast. Ecological Indicators 102: 734-745. https://doi.org/10.1016/j.ecolind.2019.03.047.##22.	Nagelkerken, I., S. J. M. Blaber, S. Bouillon, P. Green, M. Haywood, L. G. Kirton, J. O. Meynecke, J. Pawlik, H. M. Penrose, A. Sasekumar and P. J. Somerfield. 2008. The habitat function of mangroves for terrestrial and marine fauna: a review. Aquatic Botany 89(2): 155-185. https://doi.org/10.1016/j.aquabot.2007.12.007.##23.	Nazim, K., M. Ahmed, M. U. Khan, N. Khan, M. Wahab and M. F. Siddiqui. 2010. An assessment of the use of Avicennia marina forsk vierh. to reclaim water logged and saline agricultural land. Pakistan Journal of Botany 42(4): 2423-2428.##24.	Omo-Irabor, O. O., S. B. Olobaniyi, J. Akunna, V. Venus, J. M. Maina and C. Paradzayi. 2011. Mangrove vulnerability modelling in parts of Western Niger Delta, Nigeria using satellite images, GIS techniques and Spatial Multi-Criteria Analysis (SMCA). Environmental Monitoring and Assessment 178(1): 39-51. doi:10.1007/s10661-010-1669-z.##25.	Rakotomavo, A. and F. Fromard. 2010. Dynamics of mangrove forests in the mangoky river delta, madagascar, under the influence of natural and human factors. Forest Ecology and Management 259(6): 1161-1169. https://doi.org/10.1016/j.foreco.2010.01.002.##26.	Rezaei, J. 2015. Best-worst multi-criteria decision-making method. Omega 53: 49-57. https://doi.org/10.1016/j.omega.2014.11.009.##27.	Rezaei, J. 2016. Best-worst multi-criteria decision-making method: some properties and a linear model. Omega 64: 126-130. https://doi.org/10.1016/j.omega.2015.12.001.##28.	Rokni, K. and T. A. Musa. 2019. Normalized difference vegetation change index: a technique for detecting vegetation changes using Landsat imagery. Catena 178: 59-63.##29.	Safiari, Sh. 2017. Mangrove forests in Iran. Journal of Iran Nature 2(2): 49-57. (In Farsi).##30.	Shahadat Hossain, M. S., C. K. Lin and M. Z. Hussain. 2003. Remote sensing and GIS applications for suitable mangrove afforestation area selection in the coastal zone of Bangladesh. Geocarto International 18(1): 61-65. https://doi.org/10.1080/10106040308542264.##31.	Sharma, S., R. A. MacKenzie, T. Tieng, K. Soben, N. Tulyasuwan, A. Resanond, G. Blate and C. M. Litton. 2020. The impacts of degradation, deforestation and restoration on mangrove ecosystem carbon stocks across Cambodia. Science of The Total Environment 706: 135416. https://doi.org/10.1016/j.scitotenv.2019.135416.##32.	Simard, M., L. Fatoyinbo, C. Smetanka, V. H. Rivera-Monroy, E. Castañeda-Moya, N. Thomas and T. Van der Stocken. 2019. Mangrove canopy height globally related to precipitation, temperature and cyclone frequency. Nature Geoscience 12(1): 40-45. https://doi.org/10.1038/s41561-018-0279-1.##33.	Singh, H. 2003. Vulnerability and adaptability of tidal forests in response to climate change in India. Indian Forester 129(6): 749-756.##34.	Tilahun, A. and B. Teferie. 2015. Accuracy assessment of land use land cover classification using Google Earth. American Journal of Environmental Protection 4(4): 193-198.##35.	Wang’ondu, V., J. G. Kairo, J. Kinyamario, F. Mwaura, J. Bosire, F. Dahdouh-Guebas and N. Koedam. 2010. Phenology of Avicennia marina (forsk.) vierh. in a disjunctly-zoned mangrove stand in Kenya. Western Indian Ocean Journal of Marine Science 9(2): 135-144.##36.	Zaldívar-Jiménez, M. A., J. A. Herrera-Silveira, C. Teutli-Hernández, F. A. Comín, J. L. Andrade, C. C. Molina and R. P. Ceballos. 2010. Conceptual framework for mangrove restoration in the Yucatán peninsula. Ecological Restoration 28(3): 333-342.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>عوامل اثرگذار بر ترس از خرس قهوه‌ای (Ursus arctos) در بین ساکنان
مناطق حفاظت‌شده استان البرز</TitleF>
		<TitleE>Factors Affecting Local People’s Fear of Brown Bears (Ursus Arctos) in Protected Areas of Alborz Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>ترس از گوشت&#172;خواران در جوامع محلی ساکن در زیستگاه گوشت&#172;خواران، حفاظت و مدیریت این جانوران را با چالش جدی روبرو کرده است. این رفتار می&#8204;تواند بر نگرش مردم درباره حیات&#172;وحش تأثیرگذار باشد و حفاظت و مدیریت این گوشت&#172;خواران را با مشکل روبرو کند. هدف از پژوهش حاضر، بررسی عوامل مؤثر بر ترس روستاییان از خرس قهوه&#8204;ای در منطقه حفاظت&#172;شده البرز مرکزی جنوبی و منطقه شکارممنوع طالقان در استان البرز است. به&#8204;منظور بررسی نقش برخی متغیرهای فردی و تجربی، با طراحی پرسشنامه&#8204;، اطلاعات لازم از 200 نفر از ساکنان 70 روستا در زیستگاه&#8204;های خرس قهوه&#8204;ای در فاصله زمستان 1397 تا تابستان 1398 جمع&#8204;آوری شد. تأثیر متغیرهای مستقل برداشت&#8204;شده بر اظهار ترس مصاحبه&#8204;شوندگان از حضور خرس، با استفاده از روش رگرسیون منطقی دوتایی مورد تجزیه و تحلیل قرار گرفت. بر اساس نتایج به&#8204;دست آمده، متغیرهای تجربه حمله خرس به باغ میوه پاسخگویان در یک سال گذشته، باور به نقش خرس در احیای مراتع و جنگل&#8204;ها، جنسیت بومیان مناطق مورد مطالعه، باور به این که خرس امنیت مردم را به خطر می&#8204;اندازد و همچنین نگرانی از سلامتی، تأثیر معناداری بر اظهار ترس ساکنان مناطق مورد مطالعه از خرس قهوه&#8204;ای داشت. طراحی و اجرای برنامه&#8204;های آموزشی و مشارکت مردمی برای افزایش آگاهی ساکنان درباره خرس قهوه&#8204;ای و درگیرساختن آنان در شناسایی راهکارهای همزیستی با خرس می&#8204;تواند در کاهش ترس مردم مؤثر باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Wildlife management and conservation is challenged by public perceptions and fear of carnivores in communities living in close proximity to wild habitats, where large carnivores occur. Fear of carnivores influences people&#39;s attitudes towards wild animals, further exacerbating the problems associated with effective conservation and management of wildlife. Here, we aimed to investigate the factors affecting rural attitudes towards brown bears in two protected areas (Southern-Central Alborz protected area and Taleghan prohibited hunting area) in Alborz province. To evaluate the effect of participant and experimental variables, we used a questionnaire survey. Data were collected from 200 randomly chosen residents from 70 villages across both study areas between winter of 2018 and summer of 2019. Binomial Logistic Regression was used to analyze the effect of independent variables on interviewees&#39; fear of coexistence with brown bears. Our results revealed that experiences of brown bear attacks on orchards, respondents&#8217; belief of bears&#8217; role in reforestation, gender, respondents&#8217; belief that bears jeopardize people&#8217;s safety, and respondents&#8217; concern for coexisting with brown bears play a significant role in shaping human fear towards this species. Development and implementation of educational programs to reduce local people&#8217;s fear of large carnivores and improving the sense of public participation in wildlife conservation and management programs, particularly in villages located in or adjacent to protected areas, are highly recommended.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>35</FPAGE>
			<TPAGE>49</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/11/152020/03/12020/10/29
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/8/8
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/22021/05/122021/05/12
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/2/22
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>هستی</Name>
				<MidName></MidName>
				<Family>رشنو</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rashnoo</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>hasti.rashnoo@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمد</Name>
				<MidName></MidName>
				<Family>کابلی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Kaboli</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mkaboli@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علیرضا</Name>
				<MidName></MidName>
				<Family>محمدی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohammadi</FamilyE>
				<Organizations>
				<Organization>دانشگاه جیرفت</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>armohammadi1989@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>دانیال</Name>
				<MidName></MidName>
				<Family>نیری</Family>
				<NameE>D.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Nayeri</FamilyE>
				<Organizations>
				<Organization>دانشگاه تهران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Danial.nayeri021@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جواد</Name>
				<MidName></MidName>
				<Family>سلیاری</Family>
				<NameE>J.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Selyari</FamilyE>
				<Organizations>
				<Organization>سازمان حفاظت محیط زیست ایران.</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>jselyari@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>بهنام</Name>
				<MidName></MidName>
				<Family>رحمانی</Family>
				<NameE>B.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Rahmani</FamilyE>
				<Organizations>
				<Organization>Uinversity of Tehran</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>rahmani.behnam@ut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Alborz province</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>protected areas</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>human-wildlife conflict</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>brown bear</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>fear of large carnivores</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>local people</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>wildlife damage to human resources</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استان البرز</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مناطق حفاظت‌شده</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تعارض انسان و حیات‌وحش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خرس قهوه‌ای</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ترس از حیات‌وحش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>روستاییان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خسارت حیات‌وحش.</KeyText>
			</KEYWORD>
		</KEYWORDS>

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Biological Conservation 177: 156-164.##6.	Behmanesh, M., M. Malekian., S. Fakhran Esfahani, M. Homami and M. Ahmadi. 2018. Frequency and severity of carnivorous damage to rural farmers in the east of Isfahan province. Animal Environment Quarterly 10(4): 35-44. (In Farsi) ##7.	Bhatia, S., S. M. Redpath, K. Suryawanshi and C. Mishra. 2017. The relationship between religion and attitudes toward large carnivores in Northern India? Human Dimensions of Wildlife 22(1): 30-42.##8.	Blekesaune, A. and K. Rønningen. 2010. Bears and fears: cultural capital, geography and attitudes towards large carnivores in Norway. Norsk Geografisk Tidsskrift-Norwegian Journal of Geography 64(4): 185-198.##9.	Bojarska, K. and N. Selva. 2012. Spatial patterns in brown bear Ursus arctos diet: the role of geographical and environmental factors. Mammal Review 42(2): 120-143.##10.	Bruskotter J. T., A. Singh, D. C. Fulton and K. Slagle. 2015. 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Deputy of Statistics and Information; Alborz Province Management and Planning Organization. 2017. Statistical yearbook of Alborz province. Center for Scientific Documents and Publications, Tehran, Iran. (In Farsi) ##18.	Dickman, A., S. Marchini and M. Manfredo. 2013. The human dimension in addressing conflict with large carnivores. Key topics in conservation biology 2(1): 110-126.##19.	Farhadinia, M., E. Moghanaki and B. Ekrami. 1398. Guide to managing the conflict between humans and large carnivores in Iran. Andisheh Lantern Publications, Tehran. (In Farsi)##20.	Flykt, A., M. Johansson, J. Karlsson, S. Lindeberg and O. V. Lipp. 2013. Fear of wolves and bears: physiological responses and negative associations in a Swedish sample. Human Dimensions of Wildlife 18(6): 416-434.##21.	Frank, J., M. Johansson and A. Flykt. 2015. Public attitude towards the implementation of management actions aimed at reducing human fear of brown bears and wolves. Wildlife Biology 21(3): 122-130.##22.	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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی همبستگی بین خدمت بوم‌شناختی گرده‌افشانی و سنجه‌های الگوی سیمای سرزمین (منطقه مورد مطالعه: استان قزوین)</TitleF>
		<TitleE>Evaluating the Correlation Between Pollination Ecosystem Service and Landscape Pattern metrics (Case Study: Qazvin Province)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>گرده&#8204;افشانی یک خدمت بوم&#8204;شناختی با ارزش اقتصادی غیرقابل انکار است که با رفاه انسان و سلامت بوم&#8204;شناختی سیمای &#8204;سرزمین مرتبط است. این مطالعه با هدف ارزیابی همبستگی بین پیچیدگی سیمای &#8204;سرزمین و خدمت گرده&#8204;افشانی (زنبور) در مقیاس سیمای &#8204;سرزمین استان قزوین انجام شده است. در این مطالعه، سنجه&#8204;های الگوی سیمای &#8204;سرزمین (تعداد لکه، غنای لکه، تراکم حاشیه و تنوع شانون) به عنوان شاخصی برای ارزیابی پیچیدگی سیمای سرزمین، با الگوریتم مدل&#172;ساز در نرم&#8204;افزار ArcGIS و خدمت گرده&#8204;افشانی با مدل InVEST استخراج شد. همبستگی بین خدمت گرده&#8204;&#8204;افشانی و پیچیدگی سیمای سرزمین در محیط SPSS محاسبه شد. نتایج همبستگی بین خدمت گرده&#8204;افشانی و سنجه&#8204;های الگوی سیمای &#8204;سرزمین نشان داد همبستگی بین گرده&#8204;افشانی و تنوع شانون با رگرسیون خطی، مناسب&#8204;ترین نتیجه را در پی داشته و دارای رابطه معنی&#8204;دار در سطح 0/01 است (**0/420). همبستگی دیگر سنجه&#8204;های الگوی سیمای&#8204;سرزمین با گرده&#8204;افشانی، با رگرسیون درجه 2 مناسب تشخیص داده شد. همبستگی تعداد لکه (**0/171) و غنای لکه (**0/352) در سطح 0/01 معنی&#8204;دار بوده و همبستگی تراکم حاشیه معنی&#8204;دار نبود (0/002). نتایج مطالعه نشان داد که در تعداد و غنای لکه کمتر، همبستگی مثبت و در تعداد و غنای لکه بیشتر، همبستگی منفی وجود دارد که نشان&#172;دهنده اثر تکه&#8204;تکه&#8204;شدگی بر ارائه خدمت گرده&#8204;افشانی است. نتایج این مطالعه می&#8204;تواند در برنامه&#8204;ریزی سیستم&#8204;های کشاورزی و مدیریت تنوع زیستی به&#172;منظور حفظ فرایندهای بوم&#8204;شناختی کاربرد داشته باشد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Pollination is an ecological service with high economic values related to human and ecological wellbeing. This study aims to evaluate the correlation between landscape complexity and pollination service (bee) in Qazvin province at the landscape scale. Landscape pattern metrics (Number of Patches (NP), Patch Richness (PR), Edge Density (ED), and Shannon Index (H)), as a proxy of landscape complexity, were calculated by the model builder in the ArcGIS and pollination service was generated by InVEST. The correlation between landscape complexity and pollination service was evaluated by SPSS software. Results of the correlation between landscape metrics and pollination service, using Linear regression, showed that H has the highest and the most significant relationship with pollination at the 0.01 level (0.420**). Correlation between other metrics and pollination was found to better explauned by Quadratic regression, showing a significant correlation with NP (0.171**) and PR (0.352**) at the 0.01 level and a non-significant relationship with ED (0.002). It was concluded from our results that in the low NP and PR, correlation is high and positive, and in the high NP and PR, correlation is negative, indicating the effect of fragmentation on pollination service. The results of this study can be used in agricultural system planning and biodiversity management to preserve the ecological processes.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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

		<RECEIVE_DATE>
			2020/11/152020/03/12020/10/292021/01/9
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/10/20
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/22021/05/122021/05/122021/05/23
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/3/2
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>آصف</Name>
				<MidName></MidName>
				<Family>درویشی</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Darvishi</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهید بهشتی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Asefdarvishi1980@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مریم</Name>
				<MidName></MidName>
				<Family>یوسفی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Yousefi</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهید بهشتی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Yousefi.myb@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نغمه</Name>
				<MidName></MidName>
				<Family>مبرقعی دینان</Family>
				<NameE>N.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mobarghaee Dinan</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهید بهشتی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>n_mobarghei@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Ecosystem Services</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Pollination</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>Agricultural Production</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Qazvin Province</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>گرده‌افشانی</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>تولیدات کشاورزی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>استان قزوین</KeyText>
			</KEYWORD>
		</KEYWORDS>

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Journal of applied ecology 44(1): 50-59.##33.	Ollerton, J., R. Winfree and S. Tarrant. 2011. How many flowering plants are pollinated by animals? Oikos 120: 321-326.##34.	Ricketts, T. H., J. Regetz, I. Steffan-Dewenter, S. A. Cunningham, C. Kremen, A. Bogdanski, B. Gemmill-Herren, S. S. Greenleaf, A. M. Klein, M. M. Mayfield, L. A. Morandin, A. Ochieng', S. G. Potts and B. F. Viana. 2008. Landscape effects on crop pollination services: are there general patterns? Ecology Letters 11(5): 499-515.##35.	Schulp, C. J. E., S. Lautenbach and P. H. Verburg. 2014. Quantifying and mapping ecosystem services: demand and supply of pollination in the European Union. Ecological Indicators 36: 131-141.##36.	Sobhani, P., H. Goshtasb, B. Nezami and A. Jahani. 2018. Ecological capability evaluation of no-hunting areas for a higher level of protection by using Multiple Criteria Decision Making method (case study: Alvand No-Hunting Area). Environmental Researches 8(16): 29-42. (In Farsi)##37.	Tscheulin, T., L. Neokosmidis, T. Petanidou and J. Settele. 2011. Influence of landscape context on the abundance and diversity of bees in Mediterranean olive groves. Bulletin of Entomological Research 101(5): 557.##38.	Vanbergen, A. J. and T. I. P. Initiative. 2013. Threats to an ecosystem service: pressures on pollinators. Frontiers in Ecology and the Environment 11(5): 251-259.##39.	Wood, S., K. Sebastian and S. J. Scherr. 2000. Pilot analysis of global ecosystems: agroecosystems. International Food Policy Research Institute and World Resources Institute, Washington, DC.##40.	Wu, J. 2013. Landscape ecology. pp. 179-200, In: Leemans R. (ed.), Ecological systems. Springer, New York, NY.##41.	Yousefi, M., A. Darvishi, R. Padró, S. Barghjelveh, N. Mobarghei Dinan and J. Marull. 2020. An energy-landscape integrated analysis to evaluate agroecological scarcity. Science of The Total Environment 139998. ##42.	Yousefi, M., A. Darvishi, E. Tello, S. Barghjelveh, N. Mobarghei Dinan and J. Marull. 2021. Comparison of two biophysical indicators under different landscape complexity. Ecological Indicators 124: 107439.##43.	Yousefi, M., S. Barghjelveh, A. Darvishi and N. Mobarghei Dinan. 2021. Energy return on investment, a new approach to ecological sustainability and its correlation with landscape heterogenity (case study: Qazvin Province). Agroecology 13 (1). (In Farsi)##44.	Zulian, G., J. Maes and M. L. Paracchini. 2013. Linking land cover data and crop yields for mapping and assessment of pollination services in Europe. Land 2(3): 472-492.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی روند تغییرات بوم‌شناختی تالاب شادگان با استفاده از تصاویر سنجنده مودیس 
(از سال 2003 تا 2017)</TitleF>
		<TitleE>Evaluating the Trend of Ecological Changes in Shadegan Wetland Using MODIS Imagery (2003-2017)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>امروزه خطر نابودی و تخریب تالاب&#172;ها به یکی از مهم&#8204;ترین بحران&#8204;های محیط&#172;زیستی در جهان تبدیل شده است. از این&#172;رو پایش پیوسته و طولانی&#172;مدت روند تغییرات بوم&#172;شناختی تالاب&#8204;ها می&#8204;تواند نقش کلیدی در حفاظت و مدیریت اصولی آنها داشته باشد. در مطالعه حاضر روند تغییرات ماهانه برخی شاخص&#8204;های بوم&#172;&#172;شناختی محیط آبی تالاب شادگان شامل WST، NDVI، MVWR، VWR، LSWI، MNDWI و غلظت کروفیل-a طی سال&#8204;های 2003 تا 2017 با استفاده از تصاویر ماهواره&#8204;ای مودیس مورد ارزیابی قرار گرفت. به&#8204;منظور تحلیل روند و بزرگی شیب روند به&#8204;ترتیب از آزمون&#8204;های من-&#172;کندال و شیب سن استفاده شد. نتایج پژوهش نشان داد حجم آب موجود در تالاب در طی دوره مطالعه دارای روند افزایشی معنادار بوده است، درحالی&#172;که پوشش گیاهی تالاب در این دوره روند کاهشی و معناداری داشته است (p&#60;0/05). همچنین نتایج نشان داد که تاریخ احتمالی شروع تغییر روند برای چهار شاخص NDVI، MVWR، MNDWI و LSWI اکتبر 2012 است که تقریباً هم&#172;زمان با توسعه برخی صنایع پرورش ماهی در بالادست این تالاب است. علاوه بر این در بازه زمانی مطالعه، بین شاخص&#8204;های پوشش گیاهی با شاخص&#8204;های آبی، همبستگی قوی معکوس (به&#8204;طور میانگین به&#172;مقدار حدود 0/86-) مشاهده شد. به&#8204;طور خلاصه نتایج پژوهش حاضر شواهدی از یک توالی معکوس و شرایط بحرانی را در تالاب شادگان نشان داد. تلفیق تکنیک&#8204;های سنجش از دور و برخی روش&#8204;های آماری مورد استفاده در این مطالعه و در نهایت، تهیه سری زمانی کامل و پیوسته از شاخص&#8204;های مدنظر، می&#8204;تواند برای شناخت بهتر پویایی بوم&#172;سازگان تالاب شادگان، و ارزیابی، مدل&#172;سازی و پیش&#8204;بینی تغییرات وضعیت بوم&#172;شناختی این تالاب مورد استفاده قرار گیرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Nowadays, the risk of degradation of wetlands is one of the main environmental challenges in the world, so continuous and long-term monitoring of ecological changes in wetlands can play a key role in their protection and proper management. In the present study, the trend of monthly changes in some of the most important ecological indicators of the aquatic environment of Shadegan wetland including WST, NDVI, MVWR, VWR, LSWI, MNDWI and Chlorophyll-a concentration (during 2003-2017) was evaluated using MODIS satellite imagery. The Mann-Kendall and Sen&#8217;s slope tests were used to analyze the trend and its magnitude, respectively. Results showed a significant increasing trend in the volume of water in Shadegan wetland, while the vegetation of the wetland had a significant decreasing trend during the study period (p &#60;0.05). Also, the change in the monthly trend of NDVI, MVWR, MNDWI and LSWI time series was observed around October 2012, which approximately coincided with the development of aquacultural facilities in the northern part of this wetland. In addition, a strong inverse correlation (about -0.86) was observed between vegetation and water indices. Results further provided evidence of an inverse sequence and critical conditions in Shadegan wetland. Integrating remote sensing techniques and statistical methods in this study (to provide continuous time series of ecological indicators) can help to better understand the dynamics of wetland ecosystems (at different temporal and spatial scales). This approach is also applicable in evaluation, modeling and prediction of ecological changes in Shadegan wetland.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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

		<RECEIVE_DATE>
			2020/11/152020/03/12020/10/292021/01/92021/01/6
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/10/17
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/22021/05/122021/05/122021/05/232021/06/12
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/3/22
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>کیان</Name>
				<MidName></MidName>
				<Family>حاجیان</Family>
				<NameE>K.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hajian</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>hajian_knwork@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>امید</Name>
				<MidName></MidName>
				<Family>بیرقدار کشکولی</Family>
				<NameE>O.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Beyraghdar Kashkooli</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>omid.beyraghdar@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>نصرالله</Name>
				<MidName></MidName>
				<Family>محبوبی صوفیانی</Family>
				<NameE>N.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mahboobi Soofiani</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>soofiani@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سعید</Name>
				<MidName></MidName>
				<Family>پورمنافی</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Pourmanafi</FamilyE>
				<Organizations>
				<Organization>دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>spourmanafi@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Shadegan Wetland</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ecological changes</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>MODIS imagery</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Chlorophyll</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تالاب شادگان</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تغییرات اکولوژیک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سنجنده مودیس</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کلروفیل</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Adam, E., O. Mutanga and D. Rugege. 2010. Multispectral and hyperspectral remote sensing for identification and mapping of wetland vegetation: a review. Wetlands Ecology and Management 18(3): 281-296.##2.	Alibakhshi, S., T. A. Groen, M. Rautiainen and B. Naimi. 2017. Remotely-sensed early warning signals of a critical transition in a wetland ecosystem. Remote Sensing 9(4): 352-371.##3.	Arsanjani, T. J., R. Javidan, M. J. Nazemosadat, J. J. Arsanjani and E. Vaz. 2015. Spatiotemporal monitoring of Bakhtegan Lake's areal fluctuations and an exploration of its future status by applying a cellular automata model. Computers &#38; Geosciences 78: 37-43.##4.	Asghari poudeh, Z., O. Ghadirian Baharanchi, S. Nematallahi, S. Fakheran and S. Pourmanafi. 2019. Monitoring and prediction of land use/cover changes in Shadegan International Wetland. Iranian Journal of Applied Ecology 8(3): 63-76. (In Farsi)##5.	Bayat, R., S. Jafari, B. Ghermezcheshmeh and A. M. Charkhabi. 2016. Studying the effect of dust on vegetation changes (case study: Shadegan wetland, Khuzestan). Remote Sensing and Geographic Information System in Natural Resources 7(2): 17-32. (In Farsi)##6.	Environmental Protection Agency of Iran. 2010. Comprehensive management plan of Shadegan Wetland. Conservation of Iranian Wetlands Project, UNDP/GEF, Tehran.##7.	Guo, M., J. Li, C. Sheng, J. Xu and L. Wu. 2017. A review of wetland remote sensing. Sensors 17(4): 777.##8.	Jafari Azar, A., T. M. Sabzeqbaee and S. Dashti. 2017. Application of multi-criteria decision-making methods in environmental risk assessment (case study: the international wetland of Shadegan, Khur e Omayyeh and Khur e Mousa Estuary). Geography and Environmental Hazards 24: 97-119. (In Farsi)##9.	Khaliq M. N. and T. B. Ouarda. 2007. On the critical values of the standard normal homogeneity test (SNHT).  International Journal of Climatology 27: 681-687.##10.	Libiseller, C. and A. Grimvall. 2002. Performance of partial Mann–Kendall tests for trend detection in the presence of covariates. Environmetrics 13(1): 71-84.##11.	Lou, J., X. Li, R. Ma, F. Li, H. Duan and W. Hu. 2016. Applying remote sensing techniques to monitoring seasonal and interannual changes of aquatic vegetative in Taihu Lake, China. Ecological Indicators 60: 73-81.##12.	Qureshi, S., S. K. Alavipanah,  M. Konyushkova, N. Mijani, S. Fathololomi,  M. K. Firozjaei and  A. A. Kakroodi. 2020. A Remotely sensed assessment of surface ecological change over the Gomishan Wetland, Iran. Remote Sensing 12(18): 2989.##13.	Rahimi Baloochi, L. and B. Malek Mohammdi. 2012. Methodology for assessing the vulnerability of surface water resources (case study: Jarahi Basin). 6th Conference and Exhibition on Environmental Engineering. Tehran, Iran. (In Farsi)##14.	 Reis, V., V. Hermoso, S. K. Hamilton, D. Ward, E. Fluet-Chouinard, B. Lehner and S. Linke. 2017. A global assessment of inland wetland conservation status. Bioscience 67(6): 523-533.##15.	Rodriguez, Y. C., A. ElAnjoumi, J. D. Gomez, D. R. Perez and E. Rico. 2014. Using Landsat image time series to study a small water body in Northern Spain. Environmental Monitoring and Assessment 186(6): 3511-3522.##16.	Sadeghi Rad, A., S. K. Jafari and B. Allah Gani. 2017. Investigation of vegetation status of International Shadegan Wetland with NDVI index using MODIS sensor during 2000 to 2015. In: 12th Symposium on Advances in Science and Technology. Mashhad, Iran. pp. 69-79. (In Farsi)##17.	Sen, P. K. 1968. Estimates of the regression coefficient based on Kendall’s tau. Journal of the American Statistical Association 63: 1379-1389.##18.	Xu, H. 2006. Modification of normalised difference water index (NDWI) to enhance open water features in remotely sensed imagery. International Journal of Remote Sensing 27(14): 3025-3033.##19.	Yuan, L. and L. Zhang. 2006. Identification of the spectral characteristics of submerged plant Vallisneria spiralis. Acta Ecologica Sinica 26(4): 1005-1010.##20.	Yu, K. and C. Hu. 2015. Changes in vegetative coverage of the Hongze Lake national wetland nature reserve: a decade-long assessment using MODIS medium-resolution data. Journal of Applied Remote Sensing 7(1): 073589.##21.	Zar, J. H. 1972. Significance testing of the Spearman rank correlation coefficient. Journal of the American Statistical Association 67(339): 578-580.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>تأثیر ارتفاع از سطح دریا و خصوصیات خاک بر تنوع آلفا و بتای مراتع پلور مازندران</TitleF>
		<TitleE>Effects of Altitude and Soil Properties on Alpha and Beta Diversity in  Plour Rangelands of Mazandaran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تنوع&#172;زیستی یکی از مسائل مهم بوم&#8204;شناختی است که پایه و اساس عملکرد اکوسیستم است. بنابراین حفظ تنوع&#172;زیستی برای رفاه انسان لازم و ضروری است. هدف از این پژوهش، بررسی روند تغییرات تنوع آلفا و بتا و مؤلفه&#8206;های تنوع بتا در طول گرادیان ارتفاع در 5 طبقه ارتفاعی و همچنین تأثیر خصوصیات فیزیکی و شیمیایی خاک بر تغییرات شاخص&#8206;های مذکور بود. در هر طبقه 20 نمونه خاک و در کل 100 نمونه از منطقه برداشت شده و ارتباط بین خصوصیات فیزیکی و شیمیایی با شاخص&#8204;های تنوع مورد بررسی قرار گرفت. تعداد گونه&#8204;ها در 100 پلات برداشت شد و شاخص&#8204;های تنوع آلفا و بتا در دو سطح پلات و ترانسکت در نرم&#8204;افزار R محاسبه شد. بر اساس نتایج، کمترین میزان تنوع آلفای پلات (1/03 &#177; 12/47) و ترانسکت (1/06 &#177; 24/15) مربوط به کلاس ارتفاعی بیش از 3200 متر بود درحالی&#172;که کمترین مقدار تنوع بتای پلات 780 &#177; 11) و ترانسکت (0/44 &#177; 18) در کلاس ارتفاعی کمتر از 2600 متر مشاهده شد. در همه کلاس&#8206;های ارتفاعی، بیش از 90 درصد از تغییرات تنوع بتا به&#8204;واسطه مؤلفه روگشت گونه&#8207;ای اتفاق افتاده و مؤلفه الگوی آشیانه&#8207;ای سهم بسیار ناچیزی از تنوع بتا را توجیه کرد. مدل کلی (همه عوامل محیطی) تنها 11 درصد از تغییرات تنوع آلفا و 30 درصد از تغییرات تنوع بتا را توجیه نمود. این نتیجه بیانگر پیچیدگی بالای محیط و جوامع گیاهی است و به&#172;روشنی نشان می&#8207;دهد که با استفاده از برخی متغیرهای محیطی نمی&#8207;توان کل تغییرات ترکیب گیاهان را آشکار کرد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Biodiversity is one of the important aspects of natursal systems which supports ecosystem functions. Therefore, the preservation of biodiversity is necessary for human well-being. The curreny study aimed to investigate changes of alpha and beta diversity and its components along the elevation gradient of five classes and to evaluate the effects of physical and chemical characteristics of soil on these diversity indices. In each elevation class, 20 soil samples and a total of 100 samples were taken and the relationship between physical and chemical characteristics of soil with diversity indices was examined. The number of species was recorded at 100 plots and the alpha and beta diversity indices were calculated at two spatial scales (i.e., plot and transect) using R software. Based on the results, the lowest amount of alpha diversity across plots (12.47 &#177; 1.03) and transects (24.15 &#177; 1.06) were observed at the elevation class of &#62; 3200 m, while, the lowest amount of beta diversity in plots (11 &#177; 0.78) and transects (18 &#177; 0.44) were observed in class of &#60; 2600 m. In all altitude classes, more than 90% of the variation in beta diversity was explained by the species turnover component and the nested pattern component was responsible for a very small part of beta diversity. Environmental factors were explanined only 11% of the changes in alpha diversity and 30% of the beta diversity. This result indicates the high complexity of the environment and plant communities and clearly shows that using a few environmental variables cannot reveal all the changes in plant composition.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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

		<RECEIVE_DATE>
			2020/11/152020/03/12020/10/292021/01/92021/01/62020/11/7
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/8/17
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2021/05/22021/05/122021/05/122021/05/232021/06/122021/06/20
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1400/3/30
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>زینب</Name>
				<MidName></MidName>
				<Family>جعفریان</Family>
				<NameE>Z.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jafarian</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>z.jafarian@sanru.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رضا</Name>
				<MidName></MidName>
				<Family>امیدی پور</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Omidipour</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهرکرد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>romidipor@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>لیلا</Name>
				<MidName></MidName>
				<Family>زندی</Family>
				<NameE>L.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Zandi</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی ساری</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>zandileila257@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Spatial diversity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Conservation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Species turnover</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Nested pattern</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>حفاظت</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>روگشت گونه‌ای</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>الگوی آشیانه‌ ای</KeyText>
			</KEYWORD>
		</KEYWORDS>

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

	</ARTICLE>

</ARTICLES>

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