<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1402</YEAR>
<VOL>12</VOL>
<NO>3</NO>
<MOSALSAL>45</MOSALSAL>
<PAGE_NO>95</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>ارزیابی کارآمدی مناطق حفاظت شده در حفاظت از زیستگاه‌های کبک دری خزری 
(Tetraogallus caspius)، به عنوان یک گونه تخصصی مناطق کوهستانی مرتفع در ایران</TitleF>
		<TitleE>Evaluating the Effectiveness of Pretected  Areas in Preserving Habitats of Caspian Snowcock (Tetraogallus caspius), 
 as a High-Altitude Specialist Species in Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>گونه&#8204;های تخصصی ساکن مناطق مرتفع کوهستانی، در مقایسه با گونه&#8204;های ساکن مناطق کم&#8204;&#8204;ارتفاع، با تهدیدهای بیشتری به واسطه تخریب یا تکه&#8204;تکه&#8204;شدن زیستگاه و تغییرات اقلیمی مواجه هستند. کبک دری خزری، از گونه&#8204;های دارای آشیان بوم&#8204;شناختی تخصصی و شاخص مناطق کوهستانی مرتفع است. علیرغم حساسیت بالای این گونه به تغییرات زیستگاهی و نقش آن به عنوان یک گونه چتر و یا پرچم در مناطق کوهستانی، اطلاعات اندکی در زمینه بوم&#8204;شناسی این گونه وجود دارد. در پژوهش حاضر، با استفاده از 262 داده&#8204; حضور و 10 متغیر محیطی و انسانی و در چهارچوب یک رویکرد تلفیقی حاصل از پنج الگوریتم مدلسازی، پراکنش جغرافیایی این پرنده در ایران پیش&#8204;بینی شد. بر اساس مدل تلفیقی، در حدود 96527/4 کیلـومتر مربع (حدود 5/8 درصد) از گستره کشور به&#8204;عنوان زیستگاه مطلوب کبک دری شناسایی شـد. متغیرهای ناهمواری سطح زمین (30/02 درصد)، میانگین دمای سالیانه (29/61 درصد)، ارتفاع (18/57 درصد)، و شاخص هم&#8204;دمایی (14/14 درصد) بیشترین مشارکت را در مدل&#8204;سازی داشتند. به ترتیب، حدود 16/04 و 23/13 درصد از گستره زیستگاه&#8204;های مطلوب با مناطق شکار ممنوع و مناطق حفاظت &#8204;شده هم&#8204;پوشی داشت. پیشنهاد می&#8204;&#8204;شود اقدامات حفاظتی کارآمد، با تمرکز بر تهدیدهای احتمالی ناشی از فعالیت&#8204;های انسانی از جمله توسعه زیرساخت&#8204;های گردشگری، احداث جاده&#8204;ها، چرای بی&#8204;رویه و شکار غیرقانونی، انجام شود.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Specialized species living in high mountain areas face more threats compared to species living in low altitudes, primarily due to habitat destruction or fragmentation and climate change.The Caspian snowcock is a &#160;species with a specialized ecological niche and serves as an indicator of mountain ecosystems. Despite the high sensitivity of this species to habitat changes and its role as an umbrella or flagship species in mountainous areas, there is a scarcity of data on the ecology of this species. In the current study, we predicted the geographical range of this bird using 262 presence localities and 10 environmental and anthropogenic variables within an ensemble framework, resulting from five modeling algorithms. Based on the ensemble model, about 96527.4 km2 (5.8%) of the country was identified as a suitable habitat for the Caspian snowcock. Potential habitats of the species appeared to be strongly influenced by topographical roughness (30.02), average annual temperature (29.61), altitude (18.57), and isothermality (14.14). About 16.04% and 23.13% of the predicted suitable range overlapped with no-hunting&#160; and protected areas. It is suggested that effective conservation measures should be taken by focusing on the possible threats caused by human activities, including the development of tourism infrastructure, road networks, overgrazing, and poaching.
&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

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

		<RECEIVE_DATE>
			2023/09/9
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/6/18
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/11
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/9/20
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>مرضیه</Name>
				<MidName></MidName>
				<Family>مرادی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moradi</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهرکرد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mmarzieh529@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>محمدرضا</Name>
				<MidName></MidName>
				<Family>اشرف زاده</Family>
				<NameE>M. R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ashrafzadeh</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهرکرد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mrashrafzadeh@sku.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>علی اصغر</Name>
				<MidName></MidName>
				<Family>نقی پور</Family>
				<NameE>A. A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Naghipour</FamilyE>
				<Organizations>
				<Organization>دانشگاه شهرکرد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>aa_naghipour@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Snowcock</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Species distribution model</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ecological niche</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Ensemble modeling</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Protected areas</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کبک دری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدل‌ پراکنش گونه‌ای</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آشیان بوم شناختی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رویکرد مدلسازی تلفیقی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مناطق حفاظت شده</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آشیان بوم‌شناختی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رویکرد مدلسازی تلفیقی</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Allouche, O., A. Tsoar and R. Kadmon. 2006. Assessing the accuracy of species distribution models: prevalence, kappa and the true skill statistic (TSS). Journal of Applied Ecology 43(6):1223-1232.##2.	Amini Tehrani, N., B. Naimi and M. Jaboyedoff. 2020. Toward community predictions: Multi‐scale modelling of mountain breeding birds' habitat suitability, landscape preferences, and environmental drivers. Ecology and Evolution 10(12): 5544-5557. ##3.	An, B., L. Zhang., Y. Wang and S. Song. 2020. Comparative phylogeography of two sister species of snowcock: impacts of species-specific altitude preference and life history. Avian Research 11: 1-12. ##4.	Araújo, M. B. and M. New. 2007. Ensemble forecasting of species distributions. Trends in Ecology and Evolution 22(1): 42-47.##5.	Arlettaz, R., P. Patthey., M. Baltic., T. Leu., M. Schaub., R. Palme and S. Jenni-Eiermann. 2007. Spreading free-riding snow sports represent a novel serious threat for wildlife. Proceedings of the Royal Society B: Biological Sciences 274(1614): 1219-1224. ##6.	Ashrafzadeh, M. R., N. Habibzadeh and S. Ashrafi. 2018. Effects of climatic change on the geographical distribution of Caspian snowcock (Tetraogallus caspius Gmelin, 1784) in Chaharmahal and Bakhtiari province, Iran. Iranian Journal of Applied Ecology 7(3): 39-50. (In Persian)  ##7.	Ashrafzadeh, M. R., A. A. Naghipour., M. Haidarian., S. Kusza and D. S. Pilliod. 2019. Effects of climate change on habitat and connectivity for populations of a vulnerable, endemic salamander in Iran. Global Ecology and Conservation 19: p.e00637. ##8.	Ashrafzadeh, M. R. and A. R. Nazarian. 2017. Habitat suitability modelling for the Caspian Snowcock (Tetraogallus caspius), as a typical high-montane species. Journal of Natural Environment 70(4): 745-756. (In Persian) ##9.	Babaeian, I., R. Modirian., M. Karimian and M. Zarghami. 2015. Simulation of climate change in Iran during 2071-2100 using PRECIS regional climate modelling system. Desert 20(2): 123-134.##10.	Bagaria, P., A. Thapa., L. K. Sharma., B. D. Joshi., H. Singh., C. M. Sharma., J. Sarma., M. Thakur and K. Chandra. 2021. Distribution modelling and climate change risk assessment strategy for rare Himalayan Galliformes species using archetypal data abundant cohorts for adaptation planning. Climate Risk Management 31: 100264. ##11.	Barbet‐Massin, M., F. Jiguet, C. H. Albert and W. Thuiller. 2012. Selecting pseudo‐absences for species distribution models: How, where and how many?. Methods in Ecology and Evolution 3(2): 327-338. ##12.	Bellis, J. M. 2018. Conserving temperate montane birds under climate change: an assessment of potential management options. PhD thesis. Liverpool John Moores University. Liverpool, UK. ##13.	Bird Life International. 2016. Bird species distribution maps of the world. Version 6.0.##14.	Bosso, L., L. Ancillotto., S. Smeraldo., S. D’Arco., A. Migliozzi., P. Conti and D. Russo. 2018. Loss of potential bat habitat following a severe wildfire: a model-based rapid assessment. International Journal of Wildland Fire 27(11): 756-769.##15.	Brambilla, M., P. Pedrini., A. Rolando and D. E. Chamberlain. 2016. Climate change will increase the potential conflict between skiing and high elevation bird species in the Alps. Journal of Biogeography 43(11): 2299-2309. ##16.	Carvalho, J., L. Martins., J. P. Silva., J. Santos., R. T. Torres and C. Fonseca. 2012. Habitat suitability model for red deer (Cervus elaphus Linnaeus, 1758): spatial multi-criteria analysis with GIS application. Galemys 24(1): 47-56.##17.	Chamberlain, D. E., M. Negro., E. Caprio and A. Rolando. 2013. Assessing the sensitivity of alpine birds to potential future changes in habitat and climate to inform management strategies. Biological Conservation 167: 127-135. ##18.	Cheng, L., S. Lek., S. Lek-Ang and Z. Li. 2012. Predicting fish assemblages and diversity in shallow lakes in the Yangtze River basin. Limnologica 42(2): 127-136. ##19.	Elith, J. H., C. Graham., P. R. Anderson., M. Dudík., S. Ferrier., A. Guisan., J. R. Hijmans., F. Huettmann., J. Leathwick., A. Lehmann and J. Li. 2006. Novel methods improve prediction of species’ distributions from occurrence data. Ecography 29(2): 129-151. ##20.	Elith, J. and C. H. Graham. 2009. Do they? How do they? Why do they differ? On finding reasons for differing performances of species distribution models. Ecography 32(1): 66-77. ##21.	Franklin, J. 2010. Mapping Species Distributions: Spatial Inference and Prediction. Cambridge University Press.##22.	Fuller, R. A., and P.J. Garson. 2000. Pheasants: status survey and conservation action plan 2000-2004. IUCN Publications Services Unit, Cambridge, UK.##23.	Gavashelishvili, A. and Z. Javakhishvili. 2010. Combining radio-telemetry and random observations to model the habitat of near threatened Caucasian grouse Tetrao Mlokosiewiczi. Oryx 44(4): 491-500. ##24.	Goodenough, A. E. and A. G. Hart. 2013. Correlates of vulnerability to climate-induced distribution changes in European avifauna: habitat, migration and endemism. Climatic Change 118: 659-669. ##25.	Grainger, M. J., P. J. Garson., S. J. Browne., P. J. McGowan, and T. Savini. 2018. Conservation status of phasianidae in Southeast Asia. Biological Conservation 220: 60-66.##26.	Guisan, A., W. Thuiller and N. E. Zimmermann. 2017. Habitat Suitability and Distribution Models. With Applications in R. Cambridge University Press, UK.##27.	Guisan, A., R. Tingley., J. B. Baumgartner., I. Naujokaitis Lewis., P. R. Sutcliffe., A. I. Tulloch., T.J. Regan., L. Brotons., E. McDonald‐Madden., C. Mantyka‐Pringle and T. G. Martin. 2013. Predicting species distributions for conservation decisions. Ecology Letters 16(12): 1424-1435.##28.	Habibzadeh, N., A., Ghoddousi., B. Bleyhl and T. Kuemmerle. 2021. Rear‐edge populations are important for understanding climate change risk and adaptation potential of threatened species. Conservation Science and Practice 3(5): e375. ##29.	Habibzadeh, N. and Ludwig, T. 2019. Ensemble of small models for estimating potential abundance of Caucasian grouse (Lyrurus mlokosiewiczi) in Iran. Ornis Fennica 96(2): 77-89.##30.	Hickling, R., D. B. Roy., J. K. Hill., R. Fox. and C. D. Thomas. 2006. The distributions of a wide range of taxonomic groups are expanding polewards. Global Change Biology, 12(3): 450-455. ##31.	Hof, A. R. and A. M. Allen. 2019. An uncertain future for the endemic Galliformes of the Caucasus. Science of the Total Environment 651: 725-735. ##32.	Hu, H., Y. Wei., W. Wang and C. Wang. 2021. The Influence of climate change on three dominant alpine species under different scenarios on the Qinghai–Tibetan Plateau. Diversity 13(12): 682. ##33.	Jameel, M. A., M. S. Nadeem., S. Aslam., W. Ullah., D. Ahmad., M. N. Awan., W. Masroor., T. Mahmood., R. Ullah., M. Z. Anjum and K. Ali. 2022. Impact of human imposed pressure on pheasants of western Himalayas, Pakistan: Implication for monitoring and conservation. Diversity 14(9): 752.##34.	Kapos, V., J. Rhind., M. Edwards., M. F. Price and C. Ravilious. 2000. Developing a map of the world's mountain forests. pp. 4-19. In: M.F. Price and N. Butt (ed.), Forests in sustainable mountain development: a state of knowledge report for 2000. Task Force on Forests in Sustainable Mountain Development. Wallingford UK: Cabi Publishing.##35.	Khosravi, R., Wan, H. Y., Sadeghi, M. R., and Cushman, S. A. 2022. Identifying human–brown bear conflict hotspots for prioritizing critical habitat and corridor conservation in southwestern Iran. Animal Conservation 26(1): 31-45.##36.	La Sorte, F. A. and F. R., Thompson. 2007. Poleward shifts in winter ranges of North American birds. Ecology 88(7): 1803-1812. ##37.	LeDee, O. E., S. D. Handler., C. L. Hoving., C. W. Swanston and B. Zuckerberg. 2021. Preparing wildlife for climate change: How far have we come?. The Journal of Wildlife Management 85(1): 7-16.##38.	Li, R. 2019. Protecting rare and endangered species under climate change on the Qinghai Plateau, China. Ecology and Evolution 9(1): 427-36.##39.	Li, X. T. and X. Y. Lu. 1992. Status and ecology of the Snow Partridge (Lerwa lerwa callipygia) in southwestern China. In First International Symposium on Partridges, Quails and Francolins. Gibier Faune Sauvage 9: 617-623.##40.	Lin, C.T. and C. A. Chiu. 2018. The Relic Trochodendron aralioides Siebold &#38; Zucc.(Trochodendraceae) in Taiwan: Ensemble distribution modeling and climate change impacts. Forests 10(1): 7.##41.	Linshan, L., Z. Zhilong, Z. Yili and W. Xue. 2017. Using maxent model to predict suitable habitat changes for key protected species in Koshi Basin, Central Himalayas. Journal of Resources and Ecology 8(1): 77-87. ##42.	Luo, G., C. Yang., H. Zhou., M. Seitz., Y. Wu and J. Ran. 2019. Habitat use and diel activity pattern of the Tibetan Snowcock (Tetraogallus tibetanus): a case study using camera traps for surveying high-elevation bird species. Avian Research 10(1): 1-9. ##43.	Marmion, M., M. Parviainen., M. Luoto., R. K. Heikkinen and W. Thuiller. 2009. Evaluation of consensus methods in predictive species distribution modelling. Diversity and Distributions 15(1): 59-69. ##44.	McGowan, P. J. K. 1994. Caspian Snowcock (Tetraogallus caspius). In: del Hoyo, J., A. Elliott, J. Sargatal, D.A. Christie and E. Juana, (ed.), Handbook of the Birds of the World Alive. Lynx Edicions, Barcelona.##45.	McGowan, P. J., Y. Y. Zhang and Z. W. Zhang. 2009. Galliformes–barometers of the state of applied ecology and wildlife conservation in China. Journal of Applied Ecology 46(3): 524-526. ##46.	Møller, A. P., W. Fiedler and P. Berthold, 2010. Effects of Climate Change on Birds. Oxford University Press, Oxford, UK. ##47.	Pearson, R. G., W. Thuiller, M. B. Araújo., E. Martinez‐Meyer., L. Brotons., C. McClean., L. Miles., P. Segurado., T. P. Dawson and D. C. Lees. 2006. Model‐based uncertainty in species range prediction. Journal of Biogeography 33(10): 1704-1711.##48.	Peterson, A. T., J. Soberón., R. G. Pearson., R. P. Anderson., E. Martínez- Meyer., M. Nakamura and M. B. Araújo. 2011. Ecological niches and geographic distributions. Princeton, NJ: Princeton University Press.##49.	Porter, R. and S. Aspinall. 2013. Birds of the Middle East. Bloomsbury Publishing. ##50.	Purvis, A., J. L. Gittleman, G. Cowlishaw and G. M. Mace. 2000. Predicting extinction risk in declining species. Proceedings of the Royal Society of London. Series B: Biological Sciences, 267(1456): 1947-1952. ##51.	Ranner, A., A.V. Davygora., B. Hallman., A. Anselin., F. Zino., V. Galushin and V. N. Moseikin. 1994. Birds in Europe. Their conservation status. Royal Society for the Protection of Birds. BirdLife Conservation Series.  Orenburg State Teacher Training University, Orenburg Oblast, Russia. ##52.	Rodríguez-Castañeda, G., A. R. Hof., R. Jansson and L. E. Harding. 2012. Predicting the fate of biodiversity using species’ distribution models: enhancing model comparability and repeatability. Plos One 7(9): 1-10##53.	Rowland, M. M., M. J. Wisdom., L. H. Suring and C. W. Meinke. 2006. Greater sage-grouse as an umbrella species for sagebrush-associated vertebrates. Biological Conservation 129(3): 323-335. ##54.	Sato, C. F., J. T. Wood and D.B. Lindenmayer. 2013. The effects of winter recreation on alpine and subalpine fauna: a systematic review and meta-analysis. PloS One, 8(5): e64282.##55.	Scridel, D., M. Brambilla., K. Martin., A. Lehikoinen., A. Iemma., A. Matteo., S. Jähnig., E. Caprio., G. Bogliani., P. Pedrini and A. Rolando. 2018. A review and meta‐analysis of the effects of climate change on Holarctic mountain and upland bird populations. IBIS 160(3): 489-515. ##56.	Segurado, P. and Araujo, M. B. 2004. An evaluation of methods for modelling species distributions. Journal of Biogeography 31(10): 1555-1568. ##57.	Senay, S. D., S. P. Worner, and T. Ikeda. 2013. Novel three-step pseudo-absence selection technique for improved species distribution modelling. PloS One 8(8): e71218. ##58.	Shepard, D. B., A. R. Kuhns, M. J. Dreslik and C.A. Phillips. 2008. Roads as barriers to animal movement in fragmented landscapes. Animal Conservation 11(4): 288-296.##59.	Sheykhi Ilanloo, S., A. Khani., A. Kafash., N. Valizadegan., S. Ashrafi., F. Loercher., E. Ebrahimi and M., Yousefi. 2021. Applying opportunistic observations to model current and future suitability of the Kopet Dagh Mountains for a Near Threatened avian scavenger. Avian Biology Research 14(1): 18-26. ##60.	Siegel, R. B., P. Pyle., J. H. Thome., A. J. Holguin., C.A. Howell., S. Stock and M. W.Tingley. 2014. Vulnerability of birds to climate change in California's Sierra Nevada. Avian Conservation and Ecology 9(1): 7##61.	Thuiller, W., D., Georges, R., Engler, F., Breiner, M.D. Georges, and C.W., Thuiller, 2016. Package ‘biomod2’. Species distribution modeling within an ensemble forecasting framework. https://cran.r-project.org/package=biomod2.##62.	Venter, O., E. W. Sanderson., A. Magrach., J. R. Allan., J. Beher., K. R. Jones., H. P. Possingham., W. F. Laurance., P. Wood., B. M. Fekete and M.A. Levy. 2016. Sixteen years of change in the global terrestrial human footprint and implications for biodiversity conservation. Nature Communications 7(1): 12558.##63.	Wang, W., G. Ren., Y. He and J. Zhu. 2008. Habitat degradation and conservation status assessment of Gallinaceous birds in the Trans-Himalayas, China. The Journal of Wildlife Management 72(6): 1335-1341. ##64.	Wang, B., Y. Xu and J. Ran. 2017. Predicting suitable habitat of the Chinese monal (Lophophorus lhuysii) using ecological niche modeling in the Qionglai Mountains, China. PeerJ 5: e3477.##65.	Yao, H., G. Davison., N. Wang., C. Ding and Y. Wang. 2017. Post-breeding habitat association and occurrence of the Snow Partridge (Lerwa lerwa) on the Qinghai-Tibetan Plateau, west central China. Avian Research 8(1): 1-14.##66.	Yao, H., P., Wang., G. Davison., Y. Wang., P. J. McGowan., N. Wang and J. Xu. 2021. How do Snow Partridge (Lerwa lerwa) and Tibetan snowcock (Tetraogallus tibetanus) coexist in sympatry under high-elevation conditions on the Qinghai–Tibetan Plateau?. Ecology and Evolution 11(24): 18331-18341.##67.	Yıldızbaş, M., 2022. Yüksek Rakım Türlerinden Urkeklik (Tetraogallus caspius Gmelin, 1784), Dağ Horozu (Lyrurus mlokosiewiczi Taczanowski, 1875) ve Kafkas Urkekliği (Tetraogallus caucasicus Pallas, 1811)’nin İklim Değişimine Verdiği Cevapların Ekolojik Niş Modeli İle İncelenmesi. MSc thesis. Hacettepe Üniversitesi, Turkey.##68.	Yousefi, M., A. Kafash., N. Valizadegan., S. S. Ilanloo., M. Rajabizadeh., S. Malekoutikhah., S. S. H. Yousefkhani and S. Ashrafi. 2019. Climate change is a major problem for biodiversity conservation: A systematic review of recent studies in Iran. Contemporary Problems of Ecology 12: 394-403. ##69.	Zambrano, J., C.X. Garzon-Lopez., L. Yeager., C. Fortunel., N. J. Cordeiro and N. G. Beckman. 2019. The effects of habitat loss and fragmentation on plant functional traits and functional diversity: what do we know so far?. Oecologia 191: 505-518.##70.	Zheng, G. M. 2016. Chinese Pheasant. Beijing Science Press, Beijing, China.##71.	Zheng, G. M., Z. W. Zhang, P. Ding C.Q. Ding, X. Lu and Y.Y. Zhang. 2002. A Checklist on the Classification and Distribution of the Birds of the World. Science Press. Beijing, China.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی ویژگی‌های رویشی و صفات فیزیولوژیکی اکوتیپ‌های مختلف بالنگوی شهری(Lallemantia iberica Fischer & C.A. Meyer) در منطقه آذربایجان شرقی</TitleF>
		<TitleE>Evaluation of the Vegetative Characteristics and Physiological Traits of Different Ecotypes of Dragon's Head (Lallemantia Iberica Fischer & C.A. Meyer) in East Azerbaijan Region</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>ارزیابی، شناسایی و حفاظت از اکوتیپ&#8204;های بومی گیاهان دارویی به&#8204;عنوان میراث بشری، یک ضرورت است. لذا، جمع&#8204;آوری گیاهان دارویی زراعی و ارزیابی اکولوژیکی اکوتیپ&#8204;های بومی آن&#8204;ها و معرفی اکوتیپ&#8204;های سازگار برای کشاورزان، اهمیت زیادی دارد. در همین راستا، به&#8204; منظور ارزیابی صفات زراعی 49 اکوتیپ بالنگوی شهری (قَرَه زَرَک) جمع &#8204;آوری&#8204; شده از مناطق مختلف کشور، پژوهشی در قالب طرح بلوک&#8204;های کامل تصادفی با 3 تکرار و طی سال&#8204;های 95 و 96 در مزرعه تحقیقاتی دانشکده کشاورزی دانشگاه تبریز اجرا گردید. بیشترین ارتفاع بوته مربوط به اکوتیپ شماره 6 (توده محلی کلوانق 5) با میانگین 41/13 سانتی&#8204;متر، بیشترین تعداد برگ در ساقه اصلی با میانگین 30/14 برگ در اکوتیپ شماره 23 (توده محلی تبریز 4)، بیشترین شاخص کلروفیل برگ مربوط به اکوتیپ شماره 49 (توده بومی روستای نظیرلو و درویش بقال) با میانگین 36/04 و بالاترین شاخص سطح برگ مربوط به اکوتیپ شماره 20 (توده بومی محلی کلوانق 11) با میانگین cm2 &#160;2/89 بود. بیشترین عملکرد دانه تک بوته مربوط به اکوتیپ شماره 25 (توده محلی روستای تازه کند 1 هریس) با میانگین 1/05 گرم بود. نتایج نشان داد که اکوتیپ&#8204;های شماره 7 (کلوانق 6) و 14 (تبریز 3) با بالاترین عملکرد بیولوژیکی به&#8204;منظور تأمین علوفه می&#8204;تواند مورد توجه قرار بگیرد.&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Evaluation, identification, and conservation of native ecotypes of medicinal plants as human heritage are essential. Therefore, collecting and evaluating native ecotypes, as well as introducing adaptive ecotypes, are important for farmers. In order to evaluate the agricultural characteristics of 49 ecotypes of the dragon&#39;s head collected from different regions of the country, a randomized complete block design with three replications was applied at the research farm of the Faculty of Agriculture at Tabriz University. The tallest plant was associated with the ecotype number 6 (Kolvanagh 5), with an average of 41.13 cm. The ecotype number 23 exhibited the highest number of leaves on the main stem, with an average of 30.14 leaves. The highest chlorophyll index was associated with ecotype number 49 (Nazirlo and Darwish Bakal villages), averaging 36.04. The highest leaf area index was associated with ecotype No. 20, averaging 2.89 cm2. The highest seed yield of a single plant was associated with ecotype number 25 (the local population of Taze Kand 1 Haris village), averaging 1.05 g. The findings indicate that ecotypes No. 7 (Kolvanagh 6) and 14 (Tabriz 3), which exhibited the highest biological performance, could be used for fodder production.
&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>17</FPAGE>
			<TPAGE>34</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2023/09/92023/09/2
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/6/11
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/112024/01/29
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/11/9
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>جلیل</Name>
				<MidName></MidName>
				<Family>شفق کلوانق</Family>
				<NameE>Jalil</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Shafagh- kolvanagh</FamilyE>
				<Organizations>
				<Organization>دانشگاه تبریز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>shafagh.jalil@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مینا</Name>
				<MidName></MidName>
				<Family>امانی</Family>
				<NameE>Mina</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Amani</FamilyE>
				<Organizations>
				<Organization>دانشگاه تبریز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>MINA76AMANI@YAHOO.COM</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>پیوند</Name>
				<MidName></MidName>
				<Family>صمیمی فر</Family>
				<NameE>P.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Samimifar</FamilyE>
				<Organizations>
				<Organization>دانشگاه تبریز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>samimifarpeyvand@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>عادل</Name>
				<MidName></MidName>
				<Family>دباغ محمدی نسب</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Dabbagh-Mohammadi-Nasab</FamilyE>
				<Organizations>
				<Organization>دانشگاه تبریز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>adeldabb@tabrizu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>یعقوب</Name>
				<MidName></MidName>
				<Family>راعی</Family>
				<NameE>Y.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Raee</FamilyE>
				<Organizations>
				<Organization>دانشگاه تبریز</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>yaegoob@tabrizu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Biological yield</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>Ecotypes</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Grain yield</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Leaf area index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اکوتیپ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص سطح برگ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص کلروفیل</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عملکرد بیولوژیکی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عملکرد دانه</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Abdoli, S. 2017. Comparison of yield and some qualitative and quantitative characteres of##common ecotypes of Lallemantia (Lallemantia iberica Fisch. et Mey). MSc thesis. Tabriz University. Tabriz, Iran. (In Persian)##2.	Agboola, A. A. and A. A. Fayami. 1972. Fixation and excretion of nitrogen by tropical legumes. Journal of Agronomy 64: 409-412. (In Persian)##3.	Akbarpour, A., B. Kavoosi, M. Hosseinifarahi, S. Tahmasebi and S. Gholipour. 2021. Evaluation of yield and phytochemical content of different Iranian garlic (Allium sativum L.) ecotypes. International Journal of Horticultural Science and Technology 8(4): 385-400. (In Persian)##4.	Fakhar, F., A. Biabani, M. Zarei and A. N. Moghadam. 2019. Effects of cultivar and planting spacing on yield and yield components of garlic (Allium sativum L.). Italian Journal of Agronomy 14(2): 108-113. (In Persian)##5.	Gholizadeh-Khajeh, B. 2017. Evaluation of agronomic characteristics and performance of 49 landraces Lallemantia (Lallemantia iberica Fisch. et Mey) collected from different regions of Iran. MSc thesis. Tabriz University. Tabriz, Iran. (In Persian)##6.	Jiang, Y. and N. Huang. 2001. Drought and heat stress injury to two cool season furfgrasses in relation to antioxidant metabolism and lipid peroxidation. Crop Science 41: 436-442.##7.	Moslemi, E., M. M. Akbarian, S. Z. Ravari, M. R. Yavarzadeh and N. Modafeh-Behzadi. 2023. Investigation of the effect of drought stress on yield and yield components of cumin (Cuminum cyminum L.) ecotypes in climatic conditions of Kerman Province. Eco-phytochemical Journal of Medicinal Plants 10(4): 107-119. (In Persian)##8.	Nezamivand Chegini, R., F. Benakashani, I. Alahdadi and E. Soltani. 2021. Quantification of salinity stress and drought effects on fourteen ecotypes of black caraway (Nigella sativa L.) medicinal plant. Environmental Stresses in Crop Sciences 14(1): 211-220. (In Persian)##9.	Rashidzadeh, H., F. S. Mosavi, T. Shafiee, S. M. Adyani, G. Eghlima, M. Sanikhani and A. Ramazani. 2023. Anti-plasmodial effects of different ecotypes of Glycyrrhiza glabra traditionally used for malaria in Iran. Revista Brasileira de Farmacognosia 33(2): 310-315. (In Persian)##10.	Shafagh-Kolvanagh, J., H. Dehghanian, A. D. Mohammadi-Nassab, M. Moghaddam, Y. Raei, S. Z. Salmasi and B. Gholizadeh-Khajeh. 2022. Machine learning-assisted analysis for agronomic dataset of 49 Balangu (Lallemantia iberica L.) ecotypes from different regions of Iran. Scientific Reports 12(1): 19237.##11.	Shahbazi, S., K. Alizadeh and V. Fathirezaie. 2012. Study on planting possibility of Dragon's head (Lallemantia iberica F. &#38; C. M.) landraces in cold rainfed conditions. Iranian Dryland Agronomy Journal 1(2): 82-95. (In Persian)##12.	Shaltouki, M., V. Nazeri, M. Shokrpour, L. Tabrizi and F. Aghaei. 2021. Phenotypic and genotypic assessment of some Iranian Ziziphora clinopodioides Lam. Ecotypes. Journal of Agricultural Science and Technology 23(3): 645-660. (In Persian)##13.	Sirus Mehr, A. R., M. R. Shakiba, H. Alyari, M. Tourchi and A. Dabbagh Mohammadi Nasab. 2008. Effect of drought stress and density on yield and some morphological characteristics of autumn safflower cultivars. Asian Journal of Agronomy and Horticulture 78: 80-87. (In Persian)##14.	Tetio-Kagho, F. and F. P. Gardner. 1988. Responses of maize to plant population density, Ӏ. Canopy development, light relationships, and vegetative growth. Agronomy Journal 80: 830-935.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی تغییرات مکانی و زمانی تولید خالص اولیه در اکوسیستم‌های مرتعی ایران و ارتباط آن با خشکسالی</TitleF>
		<TitleE>Evaluation of Spatial and Temporal Changes in Net Primary Production in Iran's Rangeland Ecosystems in Relation to Drought</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تغییرات مکانی و زمانی تولید خالص اولیه (Net Primary Production, NPP) نسبت به خشکسالی از معیارهای اساسی تعیین کننده وضعیت اکوسیستم&#8204;های مرتعی است. پژوهش حاضر با هدف بررسی تغییرات NPP&#160; و ارتباط آن با خشکسالی انجام گرفت. سری زمانی ماهانه داده&#8204;های NPP برای کاربری&#8204;های مرتع کشور از حاصل جمع تولیدات فتوسنتز خالص (PSN) هشت روزه سنجنده مودیس (MOD17A2H) با مقیاس مکانی 500 متر طی دوره&#8204;ی زمانی 2000 تا 2022 تهیه شد. همچنین داده&#8204;های بارش ماهانه 165 ایستگاه&#8204; سینوپتیک برای محاسبه شاخص بارش استاندارد و پایش خشکسالی&#8204;ها طی این دوره&#160; از سازمان هواشناسی&#160; کشور اخذ گردید. نتایج نشان داد که بیشترین مقادیر تولید خالص اولیه با متوسط بیش از gC.m-2.month-1 50، طی فصل بهار و اوایل تابستان در مناطق مرطوب اتفاق می&#8204;افتد. یافته&#8204;های این پژوهش نشان داد که NPP در اکوسیستم&#8204;های مرتعی ایران رو به افزایش است و بطور متوسط تولید خالص اولیه کل اکوسیستم&#8204;های مرتعی کشور حدود gC.m-2.yr-1 13&#177; 112/6 است. به عبارتی حدود 76 میلیون تن کربن در سال توسط گیاهان موجود در اکوسیستم&#8204;های مرتعی کشور ترسیب می&#8204;شود. روند تغییرات سری ماهانه NPP به دلیل تاثیرپذیری ازخاصیت فصلی معنادار نشد ولی تغییرات سالانه NPP در تمام مناطق روند افزایشی معناداری را نشان داد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>The present study was conducted to investigate NPP changes and its relationship with drought. The monthly time series of NPP for the country&#39;s rangelands was prepared from the sum of net photosynthesis production (PSN) of the eight-day MODIS sensor (MOD17A2H) with a spatial scale of 500 m for 2000 to 2022.The monthly rainfall data of 165 synoptic stations were obtained from the National Meteorological Organization to calculate the Standard Precipitation Index (SPI) and monitor droughts in this period. Box plots of precipitation and NPP were prepared and showed that the highest values of NPP with an average of more than 50 gC.m-2month-1 occur during spring and early summer in humid areas. Results showed that NPP is increasing in Iran&#39;s rangeland ecosystems, and on average, the NPP of all rangeland ecosystems in the country is about 112.6 &#177; 13 gC.m-2.year-1 &#160;,in other words, about 76 million tons of carbon per year. It is absorbed by the plants in the rangeland ecosystems of the country. The trend of changes in the monthly series of NPP was not significant due to the influence of seasonal characteristics, but the annual changes of NPP showed a significant trend of increase in all regions.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>35</FPAGE>
			<TPAGE>52</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2023/09/92023/09/22023/08/25
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/6/3
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/112024/01/292024/01/29
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/11/9
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>زهرا</Name>
				<MidName></MidName>
				<Family>سنایی</Family>
				<NameE>Z.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sanaee</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی مرتع و آبخیزداری، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>sanaeezahra@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>رضا</Name>
				<MidName></MidName>
				<Family>مدرس</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Modares</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی مرتع و آبخیزداری، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>modarres2005@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>پوریا</Name>
				<MidName></MidName>
				<Family>محیط اصفهانی</Family>
				<NameE>P.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mohit Esfahani</FamilyE>
				<Organizations>
				<Organization>گروه مهندسی مرتع و آبخیزداری، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان، اصفهان، ایران</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>poriamohit.72@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>NPP</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>SPI</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>trend analysis test</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>monthly precipitation</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>MODIS sensor</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تولید خالص اولیه</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص بارش استاندارد</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آزمون تحلیل روند</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بارش ماهانه</KeyText>
			</KEYWORD>

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

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Acharya, B. S., Rasmussen and J. Eriksen. 2012. Grassland carbon sequestration and emissions following cultivation in a mixed crop rotation. Agriculture, ecosystems and environment 153 (24): 33–39.##2.	Araghi-Shahri, S. M., S. Soltani1., M. Tarkesh and S. Pourmanafi. 2020. Investigating the effects of teleconnection indices on net primary production in the north of Iran’s Alborz Mountains. Journal of applied ecology 9(3): 1-16. (In Persian).##3.	Bazame, H. C., D. Althoff, R. Filgueiras, M. L. Calijuri and J. C. D. Oliveira. 2019. Modeling the net primary productivity: A study case in the Brazilian territory. Journal of the Indian Society of Remote Sensing 47: 1727-1735. ##4.	Bastos, A., S.W. Running, C. Gouveia and R. M. Trigo. 2013. The global NPP dependence on ENSO: La Niña and the extraordinary year of 2011. Journal of geophysical research: Biogeosciences 118: 1247–1255. ##5.	Ciais, P., M. Reichstein, N. Viovy, A. Granier, J. Og´ee and V. Allard. 2005. Europe-wide reduction in primary productivity caused by the heat and drought in 2003. Nature (London) 437(7058): 529–533.##6.	Fernández-Martínez, M., J. Sardans, F. Chevallier, P. Ciais, M. Obersteiner, S. Vicca, J. G. Canadell, A. Bastos, P. Friedlingstein, S. Sitch and S.L. Piao. 2019. Global trends in carbon sinks and their relationships with CO2 and temperature. Nature climate change 9(1): 73-79.##7.	Guisan, A., J. R. T. C. Edwards and T. Hastie. 2002. Generalized linear and generalized additive models in studies of species distributions: setting the scene. Ecological modelling 157(2-3): 89-100.##8.	Hadian, F., R. Jafari, H. Bashari, M. Tarkesh and K. D. Clarke. 2019. Estimation of spatial and temporal changes in net primary production based on Carnegie Ames Stanford Approach (CASA) model in semi-arid rangelands of Semirom County, Iran. Journal of arid land 11(4): 477-494. ##9.	Huang, Q., F. Zhang, Q. Zhang, H. Ou and Y. Jin. 2020. Quantitative assessment of the impact of human activities on terrestrial net primary productivity in the Yangtze River delta. Sustainability 12(4): 1697.##10.	Jafari, F., R. Jafari and H. Bashari. 2023. Comparing actual and potential productions of rangeland ecosystems of Kohgiluyeh and Boyer-Ahmad Province in different rangeland conditions. Journal of applied ecology 11(4): 1-14. (In Persian).##11.	Karandish, F. and S. S. Mousavi. 2018. Climate change uncertainty and risk assessment in Iran during twenty-first century: evapotranspiration and green water deficit analysis. Theoretical and applied climatology 131(1): 777-791.##12.	Kemp, D.R., H. Guodong, H. Xiangyang, D.L. Michalk, H. Fujiang, W. Jianping and Z. Yingjun. 2013. Innovative grassland management systems for environmental and livelihood benefits. Proceedings of the national academy of sciences 110(21): 8369-8374.##13.	Khatibi, R. and M. Saberi. 2020. Bio-climatic classification of Iran by multivariate statistical methods. SN Applied Sciences 2(10): 1-30.##14.	Lei, T., J. Feng, J. Lv, J. Wang, H. Song, W. Song and X. Gao. 2020. Net primary productivity loss under different drought levels in different grassland ecosystems. Journal of environmental management 274: 111144.##15.	Li, P., C. Peng, M. Wang, W. Li, P. Zhao, K. Wang, Y. Yang, and Q. Zhu. 2017. Quantification of the response of global terrestrial net primary production to multifactor global change. Ecological indicators 76: 245-255.##16.	Lu, Q., Z. Gao, J. Ning, X. Bi and Q. Wang. 2015. Impact of progressive urbanization and changing cropping systems on soil erosion and net primary production. Ecological engineering 75: 187-194.##17.	McKee T. B., N. J. Doesken, J. Kleist. 1995. Drought monitoring with multiple time scales. In: Proceedings of 9th conference on Applied Climatology. Boston, Massachusetts, 15-20 January, pp. 233–236.##18.	Mgalula, M. E., O. V. Wasonga, C. Hülsebusch, U. Richter and O. Hensel. 2021. Greenhouse gas emissions and carbon sink potential in Eastern Africa rangeland ecosystems: A review. Pastoralism 11(1): 1-17.##19.	Modarres, R. and V. D. P. R. da Silva. 2007. Rainfall trends in arid and semi-arid regions of Iran. Journal of arid environments 70(2): 344-355.##20.	Patel, N. R., V. K. Dadhwal, S. K. Saha, A. Garg and N. Sharma. 2010. Evaluation of MODIS data potential to infer water stress for wheat NPP estimation. Tropical Ecology 51(1): 93-105.##21.	Richardson, A. D., T. Andy Black, P. Ciais, N. Delbart, M. A. Friedl, N. Gobron, D.Y. Hollinger, W.L. Kutsch, B. Longdoz, S. Luyssaert and M. Migliavacca. 2010. Influence of spring and autumn phenological transitions on forest ecosystem productivity. Philosophical Transactions of the Royal Society B: Biological Sciences 365(1555): 3227-3246.##22.	Saki,M., S. Soltani Koupaei., M. Taekesh Esfahani and R. Jafari. 2018. Spatial and temporal changes of net primary production (NPP) and their relationship with climatic factors from 2000 to 2014 in Isfahan Province. Journal of applied ecology 7(1): 27-40. (In Persian).##23.	Saydzade, F., S. Soltani and R. Modarres. 2022. Prediction of net primary production changes in different phytogeographical regions of Iran from 2000 to 2016, using time series models. Journal of applied ecology. 11(2): 19-35. (In Persian).##24.	Sen, P. K. 1968. Estimates of the regression coefficient based on Kendall's Tau. Journal of the American statistical association 63(324): 1379–1389.##25.	Wood, S. 2006. Generalized Additive Models: An Introduction with R. CRC Press, University of Bristol, UK.##26.	Yu, T., R. Sun, Z. Xiao, Q. Zhang, G. Liu, T. Cui and J. Wang. 2018. Estimation of global vegetation productivity from global land surface satellite data. Remote sensing 10(2): 327-347.##27.	Zhao, M. and S. W. Running. 2010. Drought-induced reduction in global terrestrial net primary production from 2000 through 2009. Science 329(5994): 940–943.##28.	Zhao, J., S. Huang, Q. Huang, H. Wang and G. Leng. 2018. Detecting the dominant cause of streamflow decline in the Loess Plateau of China based on the latest Budyko Equation. Water 10(9): 1-19.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی ویژگی‌های جدید میکرواکولوژیک تالاب درگه‌سنگی در استان آذربایجان غربی</TitleF>
		<TitleE>Investigating the New Micro-Ecological Characteristics of Darga-Sangi Wetland in West Azarbaijan Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تالاب&#8204;ها به عنوان منابع آبی شکننده دائماً تحت تاثیر تغییرات اقلیمی و فعالیت&#8204;های انسانی می&#8204;باشند. اخیراً دخالت&#8204;های انسانی و کاهش آب&#8204;های سطحی در حوزه آبریز دریاچه ارومیه موجب تغییر میکروفلور و پارامترهای فیزیکوشیمیایی تالاب&#8204;ها شده است که نیازمند مطالعه است. در این تحقیق ابتدا تنوع ریزجلبک&#8204;های تالاب درگه سنگی بررسی شد. تحقیق نشان داد جمعیت فیتوپلانکتون&#8204;ها شامل Chlorophyta (2 رده، 10 خانواده و 22 جنس)، Cyanobacteriota (1 رده، 3 خانواده و 4 جنس)، Streptophyta (1 رده، 2 خانواده و 2 جنس)، Ochrophyta (2 رده، 2 خانواده و 2 جنس) و Bacillariophyta (4 رده، 6 خانواده و 10 جنس) می&#8204;باشند. همچنین، مقدار pH، میزان اکسیژن مورد نیاز زیستی (Biochemical Oxygen Demand) و اکسیژن مورد نیاز شیمیایی (Chemical Oxygen Demand) بررسی شد. بیشترین مقدار BOD5 آب تالاب درگه&#8204;سنگی مربوط به فصل تابستان بین 78 تا 98 میلی&#8204;گرم در لیتر و بیشترین مقدار COD مربوط به فصل تابستان و بین 159 تا 198 میلی&#8204;گرم در لیتر برآورد شد. نتایج نشان داد که ورود میزان بالایی از مواد آلی و معدنی به تالاب بر غنی&#8204;شدن تالاب و شکوفایی ریزجلبک&#8204;ها تاثیرگذاشته است که از دیدگاه اکولوژیک نگران کننده است. بار باکتریایی این تالاب آن را در وضعیت نامناسبی قرار می&#8204;دهد که می&#8204;تواند برای گونه&#8204;هایبومی و مهاجر خطرناک باشد.&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Wetlands, as fragile water sources, are constantly affected by climate change and human activities. Recently, human intervention and the reduction of surface water in the catchment area of Lake Urmia have altered the microflora and physicochemical parameters of the wetlands, which need to be investigated. Results showed that phytoplankton populations of Darga-Sangi wetland consisted of Chlorophyta (2 classes, 10 families, and 22 genera), Cyanobacteriata (1 classes, 3 families, and 4 genera), Streptophyta (1 classes, 2 families, and 2 genera), Ochrophyta (2 classes, 2 families, and 2 genera), and Basillariophyta (4 orders, 6 families, and 10 genera ). In addition, pH value, Biological Oxygen Demand (BOD), and Chemical Oxygen Demand (COD) were investigated. The highest amount of BOD5 of Darga-Sangi wetland was estimated to be between 78 and 98 mg/l, while the highest amount of COD was 159 and 198 mg/l during the summer season. The results indicate that the high influx of organic and mineral substances into the wetland has affected its enrichment which resulted in blooming of microalgae and hence, rising ecological concerns. The bacterial load in this wetland puts it in an unfavorable condition, which can be dangerous for native and migratory organisms.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>53</FPAGE>
			<TPAGE>66</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2023/09/92023/09/22023/08/252023/11/5
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/8/14
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/112024/01/292024/01/292024/01/29
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/11/9
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>رامین</Name>
				<MidName></MidName>
				<Family>مناف فر</Family>
				<NameE>R.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Manaffar</FamilyE>
				<Organizations>
				<Organization>دانشگاه ارومیه</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>r.manaffar@urmia.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سکینه</Name>
				<MidName></MidName>
				<Family>مرادخانی</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moradkhani</FamilyE>
				<Organizations>
				<Organization>دانشگاه پیام نور</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>s.moradkhani@pnu.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>هدیه</Name>
				<MidName></MidName>
				<Family>یزدانی</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Yazdani</FamilyE>
				<Organizations>
				<Organization>دانشگاه ارومیه</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>h_yazdani97@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Phytoplankton</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Micro-algae</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Genetic diversity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Enrichment</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Water pollution</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>فیتوپلانکتون</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ریزجلبک</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>غنی‌شدن</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آلودگی آب</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Abdel-Raouf, N., A. A., Al-Homaidan and I. Ibraheem. 2012. Microalgae and wastewater treatment. Saudi Journal of Biological Sciences 19: 257-275.##2.	Becker, E. W. 1994. Microalgae: biotechnology and microbiology. Cambridge University Press. Landen.##3.	Carrier, G., J. Berthelier,  A. Maupetit, E. Nicolau, M. Marbouty, N. Schreiber, A. Charrier, C. Carcopino, L. Leroi and B. Saint-Jean. 2023. Genetic and phenotypic intra-species diversity of alga Tisochrysis lutea reveals original genetic structure and domestication potential. European Journal of Phycology 59: 1-18.##4.	Bellinger, E. G. and D. C., Sigee. 2010. Fresh water algae: identification and use as bioindicators. John wiley and Sons Ltd, 271. ##5.	Cheraghpoor, J., S. Afsharzadeh, M. Sharifi, R. Ramezannejad Ghadi and M. Masoudi. 2013. Phytoplankton diversity assessment of Gandoman wetland, west of Iran. The Iranian Journal of Botany 19: 61-153. ##6.	Dugan, P. 1993. Wetlands in danger: a world conservation atlas. Oxford University Press. New York.##7.	Eimanifar, A and Mohebbi, F. 2007. Urmia Lake (northwest Iran): A brief review. Aquatic Biosystems 3: 30-38. ##8.	Gorbani, S. Manaffar, R., A. Taei and R. Malek Zade. 2013. Molcular diversity studing in Dunaliella genus in some site of Urmia Lake. Journal of Plant Biology 77: 89-98. (In Persian) ##9.	Gaonkar, C. C. and L. Campbell. 2023. Metabarcoding reveals high genetic diversity of harmful algae in the coastal waters of Texas, Gulf of Mexico. Harmful Algae 121: 102368.##10.	Gopal, B. and M. Chauhan. 2001. South Asian wetlands and their biodiversity: the role of monsoons. Biodiversity in Wetlands: International Journal of Ecology and Environmental Sciences 23: 305–313.##11.	Gharibkhany, M., M., Tatina, Z. Ramezanpur and F. Chobian. 2015. Studying the diversity, density and abundance of phytoplanktons of Esteel lagoon in Astara. Iranian Scientific Fisheries Journal 3: 41-54. (In Persian)##12.	Gholami, Z., M. S. Mortazavi and A. Karbassi. 2019. Environmental risk assessment of harmful algal blooms case study: Persian Gulf and Oman Sea located at Hormozgan province, Iran. Human and Ecological Risk Assessment: An International Journal 25: 271-296. ##13.	Karthick, P., K. N., Murthy, C. Ramesh, S. Narayana and R. Mohanraju. 2022. Molecular authentication of green algae Caulerpa (Caulerpales, Chlorophyta) based on ITS and tuf A genes from Andaman Islands, India. Indian Journal of Experimental Biology 58:109-114. ##14.	Keddy, P. A. 2010. Wetland ecology: principles and conservation. Cambridge University Press. Cambridge.##15.	Khalili Morcheh Khorti, F., M.  Soltani, H.Rajabi Islami and S. A. Mousavi. 2015. Impact of fish cage rainbow trout Oncorhynchus mykiss on the bacterial flora of Karon dam, Journal of Animal Environment 7:175-182. (In Persian)##16.	Lapointe, B. E., R. A. Brewton, L. E. Wilking, and L. W. Herren. 2023. Fertilizer restrictions are not sufficient to mitigate nutrient pollution and harmful algal blooms in the Indian River Lagoon, Florida. Marine Pollution Bulletin 193: 115041.##17.	Machado, K. B., , L. M.,  BiniA. S. Melo, A. T. Andrade, M. F. Almeida, P. Carvalho, F. B. Teresa, F. D. Roque, J. C. Bortolini, A. A. Padial and L. C. Vieira. 2023. Functional and taxonomic diversities are better early indicators of eutrophication than composition of freshwater phytoplankton. Hydrobiology 850: 1393-1411.##18.	Manaffar, R and S. Ghorbani. 2015. Algae bloom in northwest Urmia Lake (Bari station). Cellular and Molecular Research (Iranian Journal of Biology) 28: 115-123. (In Persian)##19.	Mitchell, S. A. 2013. The status of wetlands, threats and the predicted effect of global climate change: the situation in Sub-Saharan Africa. Aquatic Sciences 75: 95-112.##20.	Mitsch, W. J. and J. G. Gosselink. 2000. Wetlands. Third Edition. John Wiley and Sons, New York, USA.##21.	Musavi, M. S. 2010. Study of the effects of salmon farms production on water quality of the Dohezar Tonekabon river based on coarse fauna of basti invertebrates. MSc. Thesis. Azad University, Science and Research Branch, Tehran, Iran. (In Persian) ##22.	Polle, J. E. W., D.Tran and A. Ben-Amotz. 2009. History, distribution, and habitats of algae of the genus Dunaliella Teodoresco (Chlorophyceae). In Ben-Amotz, A., Polle, J. E. W. and Subba Rao, D. V. (Eds.) The Alga Dunaliella: Biodiversity, Physiology, Genomics and Biotechnology. Science Publishers, Enfield. 1-14.##23.	Naeem, S., D. R. Hahn and G. Schuurman. 2000. Producer–decomposer co-dependency influences biodiversity effects. Nature 403: 762-764.##24.	Nejat khah M. P., M. Mahdavi and M. Frozad. 2009. Plankton sutding and water quality monitoring of BandAli Khan lagoon. Journal of Environmental Science and Technology 1: 149-162. (In Persian)##25.	Prescott, G. W. 1962. Algae of western great lakes area. W. M. C. Brown compony publishing, Iowa, USA. 933.##26.	Ramberg, L., P., Hancock, M. Lindholm, T. Meyer, S. Ringrose, J. Silva, J. Van As and C. Vanderpost. 2006. Species diversity of the Okavango Delta, Botswana. Aquatic Sciences 68: 310–337.##27.	Ramezan Zade, H. 2003. Studying on epiphytic algae of Amir Kelayeh pond and Comparing of algal communities on different substrates. MSc. Thesis, Faculty of science, The University of Tehran, Iran. (In Persian)##28.	Reynolds, C. S. 1984. The ecology of freshwater phytoplankton. Cambridge University Press, Cambridge. UK.##29.	Sakhaei, N., B. Doostshenas and P. Mobed. 2017. Determining the Bahmanshir river health and biodiversity using Nygaard-Palmer and Saprobic indices. Iranian Scientific Fisheries Journal 26: 163-176. (In Persian)##30.	Shadrin, N., D. Balycheva and E. Anufriieva. 2021. Microphytobenthos in the hypersaline water bodies, the case of Bay Sivash (Crimea): Is salinity the main determinant of species composition?. Water 13: 1542.##31.	Singh, Y., A., Gulati, D. P. Singh and J. I. S. Khattar. 2018. Cyanobacterial community structure in hot water springs of Indian north-western Himalayas: a morphological, molecular and ecological approach. Algal Research 29:179-192.##32.	Tiffany, L. H. and M. E. G. Britton. 1971. The algae of Illinois. Hanfer publishing company, New York, USA, 407.##33.	Verdelho Vieira, V., J. P., Cadoret, F. G. Acien and J. Benemann. 2022. Clarification of most relevant concepts related to the microalgae production sector. Processes 10: 1-11.##34.	White, T. J., T., Bruns, S. Lee and J. Taylor. 1990. Amplification and direct sequencing of eukaryotic ribosomal RNA genes for phylogenetic analyses. PP. 315-322. In: Innis, M. A, Gelfand, D. H., Sninsky, J. J. and White, T. J. (eds.), PCR Protocols, Academic Press, Waltham.##35.	Yoshida, K. O. H., T., Iwanaga, A. Yoshitake, T. Mine, M. Omura and K. Kimura. 2023. Species-specific monitoring of skeletonema blooms in the coastal waters of Ariake sound, Japan. Marine Ecology Progress Series 12: 31-46.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>اثرات لاشبرگ‌های ترکیبی بلوط ایرانی، داغداغان و بنه بر نرخ تجزیه و پویایی عناصر غذایی
در جنگل‌های زاگرس (مطالعه موردی: استان ایلام)</TitleF>
		<TitleE>Effects of Mixed Leaf Litters of Iranian Oak, Tree of Heaven, and Wild Pistachio on Decomposition and Dynamics of Nutrients in Zagros Forests (Case Study: Ilam Province)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تجزیه لاشبرگ نقش کلیدی در چرخه عناصر غذایی بوم&#8204;سازگان&#8204;های جنگلی بازی می&#8204;کند، با این حال هنوز درک جامعی در مورد اثرات لاشبرگ&#8204;های ترکیبی بر نرخ تجزیه وجود ندارد. در مطالعه حاضر پویایی عناصر غذایی و نرخ تجزیه لاشبرگ&#8204;های بلوط ایرانی&#160;
(Quercus brantii Lindl.)، داغداغان (Celtis australis L.) و بنه (Pistacia atlantica Desf) در حالت&#8204;های خالص و ترکیبی بررسی شد. در این پژوهش تعداد 81 کیسه لاشبرگ تک&#8204;جیبه و دوجیبه در منطقه مورد بررسی نصب و طی 180 روز با فواصل زمانی 30، 60 و 180 روز مورد انکوباسیون قرار گرفتند. براساس نتایج، در پایان دوره انکوباسیون، تجزیه لاشبرگ بلوط در ترکیب با لاشبرگ داغداغان، لاشبرگ داغداغان در ترکیب با لاشبرگ بنه و لاشبرگ بنه در ترکیب با لاشبرگ بلوط مثبت و از نوع هم&#8204;افزایی بود. همچنین در پایان دوره بررسی، غلظت نیتروژن در لاشبرگ بلوط ترکیبی با داغداغان بیشتر از حالت خالص آن بود، اما غلظت فسفر در حالت&#8204;های خالص و ترکیبی اختلاف معنی&#8204;داری نشان نداد. غلظت پتاسیم فقط در لاشبرگ بنه ترکیبی با بلوط بیشتر از حالت خالص آن بود. به&#8204;طور کلی، یافته&#8204;های این پژوهش نشان&#8204;دهنده اثرات غیرافزایشی مثبت لاشبرگ&#8204;های ترکیبی بر نرخ تجزیه بود، ولی در خصوص پویایی عناصر غذایی، این اثرات فقط در مورد نیتروژن مثبت گزارش شد.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Leaf litter decomposition plays a key role in the nutrient cycle of forest ecosystems. However, there is not a comprehensive understanding of the non-additive decomposition effects in leaf litter mixing experiments. In this study, the dynamics of nutrients and the rate of decomposition of Iranian oak (Quercus brantii), tree of heaven (Celtis caucasica), and wild pistachio (Pistacia atlantica) were investigated in both pure and mixed stands. For this purpose, 81 single- and double-litter bags were placed in the study area and incubated for 180 days. According to the results, at the end of the incubation period, the decomposition of oak litters in combination with tree of heaven, tree of heaven in combination with wild pistachio, and wild pistachio in combination with oak showed positive results. Based on the results, the nitrogen concentration in oak mixed with tree of heaven was higher than in its pure state. But the concentration of phosphorus in its pure and combined states did not show any significant differences. In general, the findings showed the positive non-additive effects of litter on its decomposition rate. Regarding the dynamics of nutrients, these effects were considered positive only for nitrogen.&#160;</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>67</FPAGE>
			<TPAGE>79</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2023/09/92023/09/22023/08/252023/11/52023/10/4
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/7/12
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/112024/01/292024/01/292024/01/292024/02/6
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/11/17
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>ساناز</Name>
				<MidName></MidName>
				<Family>رمضانی</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ramezani</FamilyE>
				<Organizations>
				<Organization>دانشگاه ملایر</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>sanaz.ramezanii73@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>فرهاد</Name>
				<MidName></MidName>
				<Family>قاسمی آقباش</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghasemi Aghbash</FamilyE>
				<Organizations>
				<Organization>دانشگاه ملایر</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>ghasemifa@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Leaf litter quality</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>non-additive effects</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Iranian oak</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>litterbag</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Zagros forests</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>اثرات غیرافزایشی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بلوط ایرانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کیسه لاشبرگ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>جنگل‌های زاگرس</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Aerts, R. 2006. The freezer defrosting: global warming and litter decomposition rates in cold biomes. Journal of Ecology 94(4): 713-724.##2.	Barbe, L, C. Mony., V. Jung., M. Santonja., I. Bartish and A. Prinzing. 2018. Functionally or phylogenetically distinct neighbors turn antagonism among decomposing litter species into synergy. Journal of Ecology 106: 1401-1414.##3.	Berg, B., and C. McClaugherty. 2014. Plant litter: Decomposition, Humus Formation, Carbon Sequestration, third edition. Springer Verlag, Berlin, Heidelberg, 315P.##4.	Berg, B., B. Erhagen., M.B. Johansson., M. Nilsson., J. Stendahl and F. Trum. 2015. Manganese in the litter fall-forest floor continuum of boreal and temperate pine and spruce forest ecosystems – a review. Forest Ecology and Management 358: 248-260. ##5.	Berger, T and P. Berger. 2014. Does mixing of beech (Fagus sylvatica) and spruce (Picea abies) litter hasten decomposition? Plant Soil 377: 217-234.##6.	Beyranvand, M and F. Ghasemi Aghbash. 2020. Non-additive effects of European black pine (Pinus nigra Arnold) and tree of heaven (Ailanthus altissima Mill.) mixed leaflitters on decomposition and nutrient dynamics of leaflitters. Forest and Wood Products 73(3): 305-315. (In Persian).##7.	Bohara, M., R. Kailash., P. Yadav., W. Dong., J. Cao and CH. Hu. 2019. Nutrient and isotopic dynamics of litter decomposition from different land uses in naturally restoring Taihang mountain, North China. Sustainability 11: 1-19.##8.	Boyero, L., J. Pé rez., N. Ló pez-Rojo., A.M. Tonin., F. Correa-Araneda and R.G. Pearson. 2021. Latitude dictates plant diversity effects on instream decomposition. Science Advances 7(13): eabe7860. ##9.	Bradford, M.A., B. Berg., D.S. Maynard., W.R. Wieder and S.A. Wood. 2016. Understanding the dominant controls on litter decomposition. Journal of Ecology 104: 229-238.##10.	  Bremner, J. M and C.S. Mulvaney. 1982. Nitrogen-Total. pp. 595-624, In: Methods of soil analysis. Part 2. Chemical and microbiological properties, Page, A.L., Miller, R.H. and Keeney, D.R. (ed.), American Society of Agronomy, Soil Science Society of America, Madison, Wisconsin.##11.	Cassart, B., A.A. Basia., M. Jonard and Q. Ponette. 2020. Average leaf litter quality drives the decomposition of single-species, mixed-species and transplanted leaf litters for two contrasting tropical forest types in the Congo Basin (DRC). Annals of Forest Science 77:1-20.##12.	Cisse, M., S. Traore and B.A.  Bationo. 2021. Decomposition and nutrient release from the mixed leaf litter of three agroforestry species in the Sudanian zone of West Africa. SN Applied Sciences 3:273. ##13.	De Long, J. R., E. Dorrepaal., P. Kardol., M.C. Nilsson., L.M. Teuber and D.A. Wardle. 2016. Understory plant functional groups and litter species identity are stronger drivers of litter decomposition than warming along a boreal forest post-fire successional gradient. Soil Biology and Biochemistry 98: 159-170. ##14.	Gao, J., F. Kang and H. Han. 2016. Effect of litter quality on leaf-litter decomposition in the context of home-field advantage and non-additive effects in temperate forests in China. Polish Journal of Environmental Studies 25(5): 1911-1920.##15.	Gartner, T. B and Z. G. Cardon. 2004. Decomposition dynamics in mixed-species leaf litter. Oikos 104: 230-246.##16.	Ghasemi Aghbash, F and M. Beyranvand. 2021. Effect of litter quality and Home-Field advantage on leaf-litter decomposition of Tree of heaven and European black pine leaf-litters. Iranian Journal of Forest 13 (3): 319-332. (In Persian).##17.	Ghasemi Aghbash, F., V. Hosseini and M. Poureza. 2016. Nutrient dynamics and early decomposition rates of Picea abies needles in combination with Fagus orientalis leaf litter in an exogenous ecosystem. Annals of Forest Research 59(1): 21-32.##18.	Gnankambary, Z., J. Bayala., A. Malmer., G. Nyberg and V. Hien. 2008. Decomposition and nutrient release from mixed plant litters of contrasting quality in an agroforestry parkland in the south-Sudanese zone of West Africa. Nutrient Cycling in Agroecosystems 82: 1-13.##19.	He, W., Z. Ma., J. Pei., M. Teng., L. Zeng., Z. Yan., Z. Huang., Z. Zhou., P. Wang and X. Luo. 2019. Leaf litter decomposition in the Three Gorges Reservoir, China. Forests 10: 360.##20.	Hoorens, B., M. Stroetenga and R. Aerts. 2010. Litter mixture interactions at the level of plant functional types are additive. Ecosystems 13: 90-98.##21.	Issac, R.A and W.C. Johnson. 1975. Collaborative study of wet and dry techniques for the elemental analysis of plant tissue by atomic absorption spectrometer. Journal of the Association of Official Agricultural Chemists. 58(3): 427-631.##22.	Leroy, F., S. Gogo., A. Buttler., L. Bragazza and F. Laggoun-Défarge. 2018. Litter decomposition in peatlands is promoted by mixed plants. Journal of Soils and Sediments 18: 739-749.##23.	Li, SH., Y. Tong and Zh. Wang. 2017. Species and genetic diversity affect leaf litter decomposition in subtropical broadleaved forest in southern Chin. Journal of Plant Ecology 10(1): 232-241.##24.	Liao, S., X.  Ni., W. Yang., H. Li., B. Wang., C. Fu., Z. Xu., B. Tan and F. Wu. 2016. Water, rather than temperature,##dominantly impacts how soil fauna affect dissolved carbon and nitrogen release from fresh litter during early litter decomposition. Forests 7: 249.##25.	Liu, J., X. Liu., Q. Song., Z. Compson., C.J. LeRoy., F. Luan., H. Wang., Y. Hu and Q. Yang. 2020. Synergistic effects: a common theme in mixed-species litter decomposition. New Phytologist 227(3): 757-765.##26.	Mao, B., T. Cui., T. Su., Q. Xu., F. Lu., H. Su., J. Zhang and SH. Xiao. 2022. Mixed-litter effects of fresh leaf semi-decomposed litter and fine root on soil enzyme activity and microbial community in an evergreen broadleaf karst forest in southwest China. Frontiers in Plant Science 13: 1-15.##27.	Montané, F., J.  Romanya., P. Rovira and P. Casals. 2013. Mixtures with grass litter may hasten shrub litter decomposition after shrub encroachment into mountain grasslands. Plant and Soil 368: 459-469.##28.	Nelson, D.W and L.E. Sommers. 1996. Total Carbon, Organic Carbon, and Organic Matter. pp. 961-1010, In: Sparks, D.L. (ed.), Methods of Soil Analysis, SSSA Book Series No. 5, Madison.##29.	Olsen, S.R and L. dean. 1965. Phosphorus. pp. 1044-1047, In: Black, C.A. (ed), methods of soil Analysis, American Society of Agronomic, Maddison.##30.	Tiunov. A.V. 2009. Particle size alters litter diversity effects on decomposition. Soil Biology and Biochemistry 41: 176-178.##31.	Versini, A., J. P. Laclau., L. Mareschal., C. Plassard., L.A. Diamesso., J. Ranger and B. Zeller. 2016. Nitrogen dynamics within and between decomposing leaves, bark and branches in Eucalyptus planted forests. Soil Biology and Biochemistry 101: 55-64.##32.	Wardle, D.A., K.I. Bonner and G.M. Barker. 1997. Biodiversity and plant litter: experimental evidence which does not support the view that enhanced species richness improves ecosystem function. Oikos 79: 247–258.##33.	Zeng, L., W. He., M. Teng., X. Luo., ZH. Yan., ZH. Huang., ZH. Zhou., P. Wang and W. Xiao. 2018. Effects of mixed leaf litter from predominant afforestation tree species on decomposition rates in the Three Gorges Reservoir, China. Science of the Total Environment 639: 679-686.##34.	Zhao, W., R.S.P.V. Logtestijn., J.R.V. Hal., M. Dong and J.H.C. Cornelissen. 2019. Non-additive effects of leaf and twig mixtures from different tree species on experimental litter-bed flammability. Plant and Soil 436: 311-324.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی بیلان انرژی و اثرات زیست‌محیطی تولید بادام با استفاده از شبکه‌های عصبی مصنوعی (مطالعه موردی:شهرستان لنجان، استان اصفهان)</TitleF>
		<TitleE>Evaluating the Energy Balance and Environmental Effects of Almond Production Using Artificial Neural Networks (Case Study: Lenjan County, Isfahan Province)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>این پژوهش با هدف بررسی بیلان انرژی و پتانسیل گرمایش جهانی تولید بادام به&#8204;صورت کشت سنتی و مکانیزه در شهرستان لنجان در استان اصفهان انجام گرفت. اطلاعات مربوط به مصرف نهاده&#8204;ها و ستانده&#8204;ها با استفاده از ۱۷۵ پرسش&#8204;نامه در کشت سنتی و 171 پرسش&#8204;نامه در کشت مکانیزه جمع&#8204;آوری گردید. انرژی معادل نهاده&#8204;ها و ستانده&#8204;ها و پتانسیل گرمایش جهانی با استفاده از ضرایب هم&#8204;ارز نهاده&#8204;ها محاسبه شد. نتایج نشان داد کل انرژی مصرفی در کشت سنتی و مکانیزه به ترتیب 14108/53 و 13767/39 مگاژول در هکتار، کارایی انرژی 0/19 و 0/24 و بهره&#8204;وری انرژی 0/1 و 0/12 کیلوگرم بر مگاژول بود. از لحاظ آماری اختلاف معنی&#8204;دار بین شاخص شدت انرژی و انرژی مصرفی در دو روش سنتی و مکانیزه مشاهد شد (P&#8804; 0.05) ولی بین شاخص شدت انرژی در این دو روش اختلاف معنی&#8204;دار مشاهده نشد. بر اساس تحلیل اقتصادی نسبت سود به هزینه در کشت سنتی و مکانیزه برابر با 3/27 و 4/2 بود. مقدار پتانسیل گرمایش جهانی حاصل از کشت سنتی 533/23 ودر کشت مکانیزه 672/3 کیلوگرم معادل&#8204;دی اکسیدکربن در هکتار محاسبه شد و بیشترین میزان آلایندگی زیست محیطی در کشت سنتی و مکانیزه مربوط به &#160;سوخت دیزل به ترتیب با 64/46 و 83/83 درصد بود.&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>This research was conducted to investigate the energy balance and global warming potential of almond production through by traditional and mechanized cultivation in Lenjan county, Isfahan province. Information related to the consumption of inputs and outputs was collected using 175 and 177 questionnaires in traditional and mechanized cultivation, respectively. Equivalent energy of inputs and outputs, as well as global warming potential, were calculated using coefficients of equivalent inputs. The results showed that the total energy consumption in traditional and mechanized cultivation is 14108.53 and 13767.39 MJ ha -1, energy efficiency is 0.19 and 0.24, and energy efficiency is 0.10 and 0.12 kg/MJ, respectively. Statistically, a significant difference was observed between the energy intensity index and energy consumption in both methods (P&#8804; 0.05). However no significant difference was observed between the energy intensity index in these two methods. Based on the economic analysis, the profit-to-cost ratio in traditional and mechanized cultivation was 3.27 and 4.2, respectively. The global warming potential from traditional and mechanized cultivation was 533.23 and 672.3 kg equivalent of carbon dioxide per hectare. The highest levels of environmental pollution in traditional and mechanized farming were associated with diesel fuel, accounting for 64.46% and 83.83%, respectively.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>81</FPAGE>
			<TPAGE>95</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2023/09/92023/09/22023/08/252023/11/52023/10/42023/09/29
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1402/7/7
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2023/12/112024/01/292024/01/292024/01/292024/02/62024/02/22
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1402/12/3
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>امیر</Name>
				<MidName></MidName>
				<Family>عزیزپناه</Family>
				<NameE>A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Azizpanah</FamilyE>
				<Organizations>
				<Organization>دانشگاه ایلام</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>a.azizpanah@ilam.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهناز</Name>
				<MidName></MidName>
				<Family>هادی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hadi</FamilyE>
				<Organizations>
				<Organization>دانشگاه ایلام</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mimhadi0034@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>قاسمی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ghasemi</FamilyE>
				<Organizations>
				<Organization>دانشگاه ایلام</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>ghasemymahdi@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Crop yield</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>net income</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>global warming</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>artificial neural network</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>almonds</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>عملکرد محصول</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>درآمد خالص</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گرمایش جهانی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شبکه عصبی مصنوعی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بادام</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Aghkhani, M. H., S. Ahmadipour, H. Soltanali and A. Rohani. 2018. Greenhouse gas emission, energy use and cost analysis of citrus production: Case Study of Mazandaran Province. Journal of Energy Policy and Planning Research 4 (3):181-229.##2.	Agrawal, J. D and M. C. Deo. 2004. Wave parameter estimation using neural networks. Marine Structures 17(7):536–550.##3.	Anonymous. 2018. Iran planning and budget organization, isfahan province management and planning organization. Isfahan Province Statistical Yearbook. (In Persian).##4.	Asgharipour, M.R and F. Salehi. 2015. Energy use on wheat production: A comparative analysis of irrigated and dry-land wheat production systems in Kermanshah. Journal of Agricultural Ecological 5(1): 1-11. (In Persian).##5.	Azizpanah, A and R. Fathi. 2021. Analysis of energy structure and greenhouse gas emissions of walnut orchards; a case study in ilam region. Iranian Journal of Applied Ecology 10 (2) :33-50.##6.	Azizpanah, A., M. Pourmusi and M. Taki. 2023. Eco-environmental and sustainability evaluation of cucumber and sunflower productions in Iran, Total Environment Research Themes 6:1-8.##7.	Azizpanah, A and H. R. Shirkhani. 2023. Energy analysis and global warming potential in wheat production systems in south of ilam. Iranian Journal of Applied Ecology 12 (1):87-102.##8.	Babaeian, M., M. Kheirkhah, M. Ghorbanzadeh and M. jafarian. 2021. Environmental hazards and energy flow in rapeseed agroecosystem Case study: North Khorasan. Journal of Agricultural Sciences and Sustainable Production 31(4): 325-339.##9.	 Beigi, M., M. Torki-Harchegani and D. Ghanbarian. 2015. Energy use efficiency and economical analysis of almond production: A Case Study in Chaharmahal-Va-Bakhtiari Province, Iran. Energy Efficiency 9(3):745–754. ##10.	Čolić, S. D., I. V. Bakić, D. Č. D. Zagorac, M. M. Natić, A. T. Smailagić, M. V. Pergal and M. M. Akšić, F. 2021. Chemical fingerprint and kernel quality assessment in different grafting combinations of almond under stress condition. Scientia Horticulturae 275: 109705.##11.	Charles, R., O. Jolliet, G. Gaillardand and D. Pellet. 2006. Environmental analysis of intensity level in wheat crop production using life cycle assessment. Agriculture, Ecosystems and Environment 113(1-4): 216-225.##12.	FAO. 2019. FAOSTAT.2021 (Melons, Other (Inc.Cantaloupes). Retrieved (http://www.fao.org/faostat/en/#data/QCL).##13.	Firmani, P., R. Bucci, F. Marini and A. Biancolillo. 2019. Authentication of avola almonds by near infrared (NIR) spectroscopy and chemometrics. Journal of Food Composition and Analysis 82: 103235.##14.	Fulton, J., M. Norton and F.  Shilling. 2019. Water-indexed benefits and impacts of California almonds. Ecological indicators 96: 711-717.##15.	Ghorbani, R., F. Mondani, S. Amirmoradi, H. Feizi, S. Khorramdel, M. Teimouri and H. Aghel. 2011. A case study of energy use and economical analysis of irrigated and dryland wheat production systems. Applied Energy 88(1): 283-288.##16.	 Heidari, M. D., M. Omid, and A. Akram. 2011. Energy efficiency and econometric analysis of broiler production farms. Energy 36(11): 6536-6541.##17.	 Kaab, A., M. Sharifi, H. Mobli, A. Nabavi-Pelesaraei and K. W. Chau. 2019. Combined life cycle assessment and artificial intelligence for prediction of output energy and environmental impacts of sugarcane production. Science of the Total Environment 664: 1005-1019.##18.	Kaul, M., R. L. Hill and C. Walthall. 2005. Artificial neural networks for corn and soybean yield prediction. Agricultural Systems 85(1): 1-18.##19.	Kitani, O., T. Jungbluth, R. M., Peart and A. Ramdani. 1999. CIGR Handbook of agricultural engineering. Energy and biomass engineering 5: 330. ##20.	Khoshnevisan, B., S. Rafiee, M. Omid, and H. Mousazadeh. 2013. Applying data envelopment analysis approach to improve energy efficiency and reduce GHG emission of wheat production. Energy 58: 588-593.##21.	Khoshnevisan, B., S. Rafiee, M. Omid, M. Yousefi and M. Movahedi. 2013. Modeling of energy consumption and GHG emissions in wheat production in Esfahan province of Iran using artificial neural networks. Energy 52: 333-338.##22.	Khodaei Joghan, A., M. Taki and H. Matoorian, 2022. Evaluating energy productivity, greenhouse gas emission, global warming potential and sustainability index of wheat and rapeseed agroecosystems in khorramshahr. Journal of Agricultural Science and Sustainable Production 32(1): 309-324.##23.	Mirhaji, H., M. Khojastehpour and M. H. Abbaspour-Fard. 2013. Environmental impact study of wheat productionin in marvdasht area of iran. Journal of Natural Environment 66(2): 223-232.##24.	Mohammadi, A. and M. Omid. 2010. Economical analysis and relation between energy inputs and yield of greenhouse cucumber production in Iran. Applied Energy 87(1): 191-196.##25.	Mohammadi, A., S. Rafiee, S. S. Mohtasebi and H. Rafiee. 2010. Energy inputs–yield relationship and cost analysis of kiwifruit production in Iran. Renewable Energy 35(5): 1071-1075.##26.	Moosavi, A. A and A. Sepaskhah. 2012. Artificial neural networks for predicting unsaturated soil hydraulic characteristics at different applied tensions. Archives of Agronomy and Soil Science 58(2): 125-153. ##27.	Nabavi-Pelesaraei, A., R. Abdi, and S. Rafiee. 2013. Energy use pattern and sensitivity analysis of energy inputs and economical models for peanut production in Iran. International Journal of Agriculture and Crop Sciences 5(19): 2193.##28.	 Nahashon, S. N., N. Adefope, A. Amenyenu and D. Wright. 2006. Effect of varying metabolizable energy and crude protein concentrations in diets of pearl gray guinea fowl pullets 1. Growth performance. Poultry science 85(10): 1847-1854.##29.	Olatunji, B. T., D.E. Ibiyeye and A.O. Onifade.  2020. Development and performance evaluation of a simple multi- nozzle mobile compression pump (MMPC) sprayer. Journal of Multidisciplinary Engineering Science and Technology (7(12):13099–13102.##30.	 Piri, Z., A. Azizpanah, K. kheiralipour and A. Maraseli. 2021. Modeling of energy consumption trend and economic indicators of broiler production (Case Study: Diwandarreh City). Journal of Animal Environment 13(4): 129-136.##31.	 Pishgar-Komleh, S.H., M. Ghahderijani, and P. Sefeedpari. 2012. Energy consumption and CO2 emissions analysis of potato production Based on different farm size levels in iran. Journal of Cleaner Production 33:183–191.##32.	Pishgar-Komleh, S.H., M. Omidm, and M.D. Heidari. 2013. On the study of energy use and GHG (Greenhouse Gas) emissions in greenhouse cucumber production in yazd province. Energy 59:63–71. ##33.	Rahman, M. M., and B. K. Bala. 2010. Modelling of jute production using artificial neural networks. Biosystems Engineering 105: 350-356.##34.	Sáez-Martínez, F. J., G. Lefebvre, J. J. Hernández and J. H. Clark. 2016. Drivers of sustainable cleaner production and sustainable energy options. Journal of cleaner production 138: 1-7.##35.	Sharifi, M., S. Soodmand-Moghaddamand, and A. Akram. 2022. Investigating the energy consumption and environmental pollutants of pumpkin production (Case Study: Boroujerd County). Iranian Journal of Biosystems Engineering 52(1), 27-36.##36.	Shabani, A., A.G. Keramat, A.R. Sepaskhah, and A.A. Kamgar-Haghighi. 2017. Using the artificial neural network to estimate leaf area. Scientia Horticulturae 216:103–10. ##37.	Shahhoseini, H. R. and H. Kazemi. 2021. Economic analysis and evaluating the sustainability of potato production based on greenhouse gas emissions (Case Study: Golestan Province). Journal of Agricultural Science and Sustainable Production 31(3): 295-311.##38.	 Singh, A. B. Ganapathysubramanian, A.K. Singh and S. Sarkar. 2016. Machine learning for high-throughput stress phenotyping in plants. Trends in plant science 21(2): 110-124.‌##39.	Taheri-Rad, A., M. Khojastehpour, A. Rohani, S. Khoramdelm, and A.Nikkhah. 2017. Energy flow modeling and predicting the yield of iranian paddy cultivars using artificial neural networks. Energy 135:405–412. ##40.	Vafabakhsh, J. and A. Mohammadzadeh. 2019. Energy flow and GHG emissions in major field and horticultural crop production systems (Case study: Sharif Abad Plain). Journal of Agroecology 11(2): 365-382.##41.	Unakıtan, G. and B. Aydın. 2018. A comparison of energy use efficiency and economic analysis of wheat and sunflower production in Turkey: A case study in Thrace Region. Energy 149 : 279–285.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

</ARTICLES>

</JOURNAL>
</XML>
