<?xml version="1.0" encoding="utf-8"?>
<XML>
<JOURNAL>
<YEAR>1399</YEAR>
<VOL>9</VOL>
<NO>3</NO>
<MOSALSAL>33</MOSALSAL>
<PAGE_NO>97</PAGE_NO>


<ARTICLES>

	<ARTICLE> 
		<TitleF>بررسی تأثیر شاخص‌های پیوند از دور بر تولید خالص اولیه (NPP) در دامنه شمالی البرز</TitleF>
		<TitleE>Investigating the Effects of Teleconnection Indices on Net Primary Production in the North of Iran’s Alborz Mountains</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>یکی از موضوعات اصلی تحقیقات علمی در زمینه اثر تغییر اقلیم جهانی، بررسی تغییرات چرخه کربن در مراتع است و تولید خالص اولیه (NPP) مؤلفه&#8204;ای مهم در این چرخه از نظر ذخیره کربن و شاخصی کلیدی برای ارزیابی کارکرد اکوسیستم است. در این تحقیق رابطه تولید خالص اولیه با نوسانات اقیانوسی اتمسفری به&#172;صورت ماهانه و فصلی در فاصله سال&#8204;های 2016-2000 در دامنه شمالی رشته کوه البرز مورد بررسی قرار گرفت. به این منظور برای مدل&#172;سازی رابطه تولید ناخالص اولیه با شاخص&#8204;های اقیانوسی اتمسفری، میزان NPP با استفاده از محصولات سنجنده مودیس استخراج شد. برای بررسی روابط هم&#172;زمان و غیرهم&#172;زمان در سری&#8204;های مختلف زمانی از رگرسیون چندمتغیره و برای بررسی روند تغییرات تولید خالص اولیه در فصل&#8204;های مختلف در طول دوره آماری مورد مطالعه از آزمون من کندال استفاده شد. نتایج نشان داد که میانگین بیشترین میزان تولید خالص اولیه در فصول بهار و تابستان به&#172;ترتیب به&#172;میزان 2/06 و 1/30 و کمترین مقدار در فصول پاییز و زمستان به&#172;ترتیب برابر با 0/68 و 0/55 گرم کربن در متر مربع در روز بود. روند معنی&#8204;دار تغییرات NPP در فصول پاییز و زمستان مشاهده شد. به&#172;طور کلی نتایج نشان داد که NPP تحت تأثیر عوامل اقلیمی به&#172;ویژه بارش بوده و شاخص&#8204;های مربوط به انسو (النینو نوسان جنوبی) از عوامل مؤثر بر بارش و در نتیجه تولید خالص اولیه در منطقه شمال کشور است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>One of the main scientific topics on the effects of global climate change is to assess changes in the carbon cycle in rangelands. Net Primary Production (NPP) is an important component of this cycle, in terms of carbon storage, and a key indicator for assessing the ecosystem function. This research aimed to investigate the correlation between NPP and ocean-atmospheric oscillations, monthly and seasonally, from 2000 to 2016 in the north of Iran&#8217;s Alborz Mountains. Net Primary Production of terrestrial vegetation was extracted from MODIS data and used in a model along with ocean-atmospheric oscillations. Multivariate regression analysis was used to investigate the simultaneous and lagged status in different timescales. Mann-Kendal test was used for trend analysis in different seasons over the studied period. Results showed that the highest NPP values were 2.06 and 1.30 g C m-2 d-1 in spring and summer and the lowest were 0.68 and 0.55 g C m-2 d-1 in autumn and winter, respectively. The trend of NPP variations was significantly different in autumn and winter. Overall, it was showed that NPP was affected by climatic variables, especially precipitation, and variables &#160;related to ENSO indicator are the main factors affecting precipitation, thereby affecting NPP in the north of Iran.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>1</FPAGE>
			<TPAGE>16</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/3
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/11/14
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/08/23
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/6/2
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>سید مرتضی</Name>
				<MidName></MidName>
				<Family>عراقی شهری</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Araghi Shahri</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>m.araghi@na.iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سعید</Name>
				<MidName></MidName>
				<Family>سلطانی</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Soltani</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>ssoltani@cc.iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مصطفی</Name>
				<MidName></MidName>
				<Family>ترکش</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Tarkesh</FamilyE>
				<Organizations>
				<Organization>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>m_tarkesh@cc.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>دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>spourmanafi@cc.iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Ocean-Atmospheric Oscillations</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Multivariate Regression</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ENSO</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Trend Analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Mann-Kendal</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Remote Sensing</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>نوسانات اقیانوسی اتمسفری</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>رگرسیون چندمتغیره</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>انسو</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آنالیز روند</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>من-کندال</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سنجش از دور</KeyText>
			</KEYWORD>
		</KEYWORDS>

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

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی آواهای زیستی در پارک‌های‌ شهر اصفهان با استفاده از شاخص‌های اکوستیک</TitleF>
		<TitleE>Evaluation of Biophonies in Isfahan Parks, Using Acoustic Indices</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تجزیه و تحلیل آوای منظر به&#172;ویژه آواهای زیستی با استفاده از شاخص&#8204;های اکوستیک اطلاعات بوم&#172;شناختی ارزشمندی را به منظور ارزیابی تنوع زیستی، بررسی الگوهای رفتاری گونه&#8204;ها و ارزیابی آلودگی&#8204;های صوتی در اختیار پژوهشگران قرار می&#172;دهد. در این پژوهش، به منظور تجزیه و تحلیل آواهای زیستی و انسانی در شش پارک شهری اصفهان در فصل بهار از شش شاخص اکوستیک شامل: شاخص پیچیدگی اکوستیک، شاخص تنوع اکوستیک، شاخص یکنواختی اکوستیک، شاخص زیستی اکوستیک، شاخص اختلاف نرمال&#172;شده آوای منظر و شاخص بی&#8204;نظمی استفاده شد که با استفاده از بسته آماری Seewave ارزش این شاخص&#172;ها در محیط نرم&#172;افزار R محاسبه شد. پس از اندازه&#8204;گیری مقادیر این شش شاخص در پارک&#8204;های شهر اصفهان، میزان همبستگی بین آنها مشخص شده و برای تعیین معنی&#8204;دار بودن تفاوت بین شاخص&#172;های اکوستیک بین جفت پارک&#172;ها از آزمون توکی در نرم&#172;افزار R استفاده شد. با توجه به نتایج آزمون ANOVA و آزمون تکمیلی توکی بیشترین مقدار شاخص&#172;&#172;های زیستی اکوستیک، اختلاف نرمال&#172;شده آوای منظر، پیچیدگی اکوستیک، تنوع اکوستیک، یکنواختی اکوستیک و بی&#172;نظمی اکوستیک مربوط به پارک صفه با مقادیر 51/63 ، 0/99، 2267، 1/46، 0/89 و 0/82 و کمترین مقدار این شاخص&#172;ها به&#172;ترتیب متعلق به پارک&#172;های محمودآباد با مقادیر 16/56 و 0/49-، ایثارگران با مقدار 1787 و باغ غدیر با مقادیر 0/05، 0/67 و 0/41 است. همچنین بیشترین اختلاف معنی&#172;دار شاخص زیستی اکوستیک و شاخص اختلاف نرمال&#172;شده آوای منظر بین پارک&#8204;های صفه و محمودآباد محاسبه شد که بیانگر تأثیرگذاری عواملی مانند میزان اثر حاشیه و تنوع زیستی پرندگان بر ارزش شاخص&#172;ها است. با توجه به نتایج پژوهش می&#8204;توان گفت شاخص&#8204;های اکوستیک زیستی و اختلاف نرمال&#172;شده آوای منظر معیارهای مناسبی برای ارزیابی فعالیت&#172;های انسانی و زیستی در فضاهای سبز شهری هستند.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Soundscape analysis, using acoustic indices, provides researchers with valuable ecological information to assess biodiversity, species behavior, and noise pollution. In this study,&#160; to analyze biophonies and anthrophony in six urban parks in&#160; Isfahan city in spring, six acoustic indices, including Acoustic complexity index (ACI), Acoustic Diversity Index (ADI), Acoustic Evenness Index (AEI), and Bioacoustic Index (BI), Normalized Difference Soundscape Index (NDSI) and Entropy Index (H) were used and quantified using&#160; Seewave Package in R software. In the next step, using ANOVA test, we evaluated the significance of difference between values of the indices among the six parks. We also calculated the degree of correlation between pairs of the indices among and within the parks using Tukey test. According to the results of ANOVA and Tukey tests, the highest values of BI, NDSI, ACI, ADI, AEI and H indices were obtained for Sofeh Park with values of 51.63, 0.99, 2267, 1.46, 0.89 and 0.82, respectively and the lowest values of the these indices were also calculated for Mahmoud-Abad (16.56 and - 0.49), Isargaran (1787) and Bagh-Ghadir (0.05, 0.67 and 0.41) Parks. Among the indices, the most significant difference was calculated for the two indices of ADI and NDSI and between the Sofeh and Mahmoud-Abad Parks, indicating the effect of factors such as edge effect and birds diversity on these indices. Based on the results, it can be concluded that NDSI and BI indices are suitable tools for evaluating ecosystem quality and can be used in green space management and urban biodiversity assessment.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>17</FPAGE>
			<TPAGE>32</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/32020/01/14
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/10/24
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/08/232020/08/31
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/6/10
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>میلاد</Name>
				<MidName></MidName>
				<Family>لطیفی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Latifi</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>milad.latifi6@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهرداد</Name>
				<MidName></MidName>
				<Family>رعنایی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Ranaie</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mehrdadranaee137166@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>سیما</Name>
				<MidName></MidName>
				<Family>فاخران</Family>
				<NameE>S.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Fakheran</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده منابع طبیعی، دانشگاه صنعتی اصفهان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>Fakheran@iut.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مینو</Name>
				<MidName></MidName>
				<Family>مشتاقی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Moshtaghie</FamilyE>
				<Organizations>
				<Organization>گروه محیط زیست، دانشکده کشاورزی و منابع طبیعی، دانشگاه آزاد اسلامی واحد اصفهان (خوراسگان)</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>m_moshtaghie@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Soundscape</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Bioacoustic Index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Seewave Package</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Birds diversity</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Sofeh Park</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>آوای منظر</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص‌ زیستی اکوستیک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>بسته Seewave</KeyText>
			</KEYWORD>

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

			<KEYWORD>
				<KeyText>پارک صفه</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Boelman, N. T., G. P. Asner, P. J. Hart and R. E. Martin. 2007. Multi‐trophic invasion  resistance in Hawaii: bioacoustics, field surveys, and airborne remote sensing. Ecological Applications 17(8): 2137-2144.##2.	Brumm, H. 2004. The impact of environmental noise on song amplitude in a territorial bird. Journal of Animal Ecology 73(3): 434-440.##3.	Duarte, M. H. L., R. S. Sousa-Lima, R. J. Young, A. Farina, M. Vasconcelos, M. Rodrigues and N. Pieretti. 2015. The impact of noise from open-cast mining on Atlantic forest biophony. Biological Conservation 191:623-631.##4.	Fairbrass, A. J., P. Rennett, C. Williams, H. Titheridge and K. E. Jones. 2017. Biases of acoustic indices measuring biodiversity in urban areas. Journal of Ecological Indicators 83:167-177.##5.	Farina, A. 2014. Soundscape ecology (principles, patterns, methods and applications). Springer, Pesaro-Urbino, Italy.##6.	Farina, A. and S. H. Gage. 2017. Ecoacoustics: the ecological role of sounds. John Wiley and Sons., New Jersey, USA.##7.	Gasc, A., S. Pavoine, L. Lellouch, P. Grandcolas and J. Sueur. 2015. Acoustic indices for biodiversity assessments: analyses of bias based on simulated bird assemblages and recommendations for field surveys. Journal of Biological Conservation 191: 306-312.##8.	Ghodsi, F. and M. Amiri. 2017. Development and management of parks and green spaces for the conservation of birds in urban areas. Human &#38; Environment 15(3): 81-89. (In Farsi)##9.	Harris, S. A., N. T. Shears and C. A. Radford. 2016. Ecoacoustic indices as proxies for biodiversity on temperate reefs. Methods in Ecology and Evolution 7(6): 713-724.##10.	Hemami, M. and A. Z. Amirani. 2011. Influence if urban park size and shape on bird species richness: case study of Isfahan City. Journal of Environmental Studies 37(59): 55-62. (In Farsi)##11.	Hellström, B., M. E. Nilsson, Ö. Axelsson and P. Lundén. 2014. Acoustic design artifacts and methods for urban soundscapes: a case study on the qualitative dimensions of sounds. Journal of Architectural and Planning Research 31(1): 57-71. ##12.	Kasten, E. P., S. H. Gage, J. Fox and W. Joo. 2012. The remote environmental assessment laboratory's acoustic library: an archive for studying soundscape ecology. Journal of Ecological Informatics 12: 50-67.##13.	Katorani, S. 2019. Evaluation of noise pollution caused by urban traffic and its effect on the level of anxiety of citizens in Sanandaj city. Journal of Urban Studies 8(32): 117-127. (In Farsi)##14.	Khademolhoseini, A., S. Ghaedrahmati and Z. Jamshidi. 2016. Assessment of sustainability in urban green space in 15 districts of Isfahan. Human Geography Research 48(4): 751-763. (In Farsi)##15.	Khanaposhtani, M. G., A. Gasc, D. Francomano, L. J. Villanueva-Rivera, J. Jung, M. J. Mossman and B. C. Pijanowski. 2019. Effects of highways on bird distribution and soundscape diversity around Aldo Leopold’s shack in Baraboo, Wisconsin, USA. Journal of Landscape and Urban Planning 192: 103666.##16.	Khoroushi, N. and M. Moshtaghie. 2017. Investigation of false voices in mountain park of Soffe (urban park) in Isfahan. Journal of Environmental Science Studies 2(1): 69-74. (In Farsi)##17.	Krause, B. and A. Farina. 2016. Using ecoacoustic methods to survey the impacts of climate change on biodiversity. Journal of Biological Conservation 195: 245-254.##18.	Liddle, M. 1997. Recreation ecology: the ecological impact of outdoor recreation and ecotourism. Chapman &#38; Hall,  Melbourne, Australia.‌##19.	Liu, J., J. Kang and H. Behm. 2014. Birdsong as an element of the urban sound environment: a case study concerning the area of Warnemünde in Germany. Acta Acustica united with Acustica 100(3): 458-466.##20.	McLaren, J. 2012. Monitoring techniques for temperate bird diversity: uncovering relationships between soundscape analysis and point counts. University of Notre Dame, Environmental Research Center, Land O'Lakes, WI.##21.	Merchan, C. I., L. Diaz-Balteiro and M. Soliño. 2014. Noise pollution in national parks: soundscape and economic valuation. Journal of Landscape and Urban Planning 123:1-9.##22.	Mohammadi, J., J. Mohammadi and R. Shaykh Baygloo. 2010. Analysis of climatic parameters of wind and rainfall considering on urban design (case study: Isfahan). Geography and Environmental Planning 21(3): 61-82. (In Farsi)##23.	Moharramnejad, N. and M. Safaripour. 2009. The impact of urban development on noise pollution in district one of Tehran and presenting management strategies to improve conditions. Journal of Environmental Science and Technology 10(4): 43-70. (In Farsi)##24.	Moshtaghie, M. and M. Kaboli, 2015. Finding the best location for installing wildlife signs using kernel density estimation in Khojir National Park. International Journal of Environmental Health Engineering 4(3): 1-6.##25.	Nasiri, P. and F. Farhang. 2003. Dependence of traffic noise pollution on increasing the height and distance from the edge of Sheikh Fadlallah Highway in Tehran. Journal of Environmental Science and Technology 5(3): 75-86. (In Farsi)##26.	Nemeth, E., N. Pieretti, S. A. Zollinger, N. Geberzahn, J. Partecke, A. C. Miranda and H. Brumm. 2013. Bird song and anthropogenic noise: vocal constraints may explain why birds sing higher-frequency songs in cities. Proceedings of the Royal Society B: Biological Sciences 280(1754): 20122798.##27.	Ortega, C. P. 2012. Effects of noise pollution on birds: a brief review of our knowledge. Journal of Ornithological Monographs 74(1): 6-22.##28.	Pieretti, N., A. Farina and D. Morri. 2011. A new methodology to infer the singing activity of an avian community: The Acoustic Complexity Index (ACI). Journal of Ecological Indicators 11(3): 868-873.##29.	Rahimi, M. 2015 .Analysis of variability in soundscape and landscape metrics along an urban-natural gradient in the central part of Isfahan Province. Isfahan University of Technology, Isfahan, Iran. (In Farsi)##30.	Rahimi, M. and S. Fakheran. 2013. Analysis of variability in soundscapes along an urban–natural area. In: Proceedings of 1st International Conference of IALE. Esfahan, Iran. (In Farsi)##31.	Razzaghian, F., M. Rahnama, M. Tavangar and H. Aghajani. 2013. Ecological analysis of urban parks (case study: Mashhad). Journal of Environmental Studies 38(4): 155-168. (In Farsi)##32.	Robbins, C. S. 1981. Effect of time of day on bird activity. Studies in Avian Biology 6(3): 275-286.##33.	Sueur, J., A. Farina, A. Gasc, N. Pieretti and S. Pavoine. 2014. Acoustic indices for biodiversity assessment and landscape investigation. Acta Acustica united with Acustica 100(4): 772-781.##34.	Sueur, J., S. Pavoine, O. Hamerlynck and S. Duvail. 2008. Rapid acoustic survey for biodiversity appraisal. PloS ONE 3(12): e4065. ##35.	Summers, P. D., G. M. Cunnington and L. Fahrig. 2011. Are the negative effects of roads on breeding birds caused by traffic noise?. Journal of Applied Ecology 48(6): 1527-1534.##36.	Tashakor, S., M. Hemami, B. Riazi and R. Jafari. 2013. Impacts of green space parameters on bird species richness of city parks: case study of Isfahan city. Journal of Environmental Science and Technology 15(1): 137-151. (In Farsi)##37.	Villanueva-Rivera, L. J., B. C. Pijanowski, J. Doucette and B. Pekin. 2011. A primer of acoustic analysis for landscape ecologists. Journal of Landscape ecology 26(9): 1233-1246.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>بررسی عوامل مؤثر بر حضور و تعارض خدنگ بزرگ (Herpestes edwardsii) در یک محیط شهری در استان خوزستان</TitleF>
		<TitleE>Factors influencing the occurrence and conflict of the Indian grey mongoose (Herpestes edwardsii) in an urban area in Khuzestan Province, Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>تعارض انسان و حیات وحش به دلیل اشغال زیستگاه&#8204;های حیات&#8204;وحش توسط انسان و کاهش طعمه وحشی رو به افزایش است. در این مطالعه، عوامل مؤثر بر حضور خدنگ بزرگ به عنوان یک گونه سازگار با محیط انسانی و دارای تعارض با انسان و عوامل مؤثر بر کاهش خسارت به ماکیان ساکنان یک محدوده مسکونی 73 هکتاری در شهر ملاثانی استان خوزستان بررسی شد. به این منظور از روش&#8204;های تحلیل شبکه اجتماعی و دسته&#8204;&#8206;بندی بیز ساده همراه با تکمیل و تحلیل 150 پرسشنامه استفاده شد. نتایج نشان داد که 42/7 درصد از مصاحبه&#8204;شوندگان، حمله خدنگ به ماکیان را در طول سال&#8204;های 1389 تا 1398 تجربه کرده&#8204;اند. نتایج تحلیل شبکه اجتماعی نشان داد که کاهش طعمه این گونه در زیستگاه&#8204;های اطراف و وجود منابع غذایی انسانی در منطقه مورد مطالعه، به&#173;ترتیب مهم&#173;ترین عوامل حضور و تعارض خدنگ بزرگ با انسان از نظر مصاحبه&#8204;شوندگان بودند. نتایج دسته&#8204;بندی بیز ساده نیز نشان داد نگهداری ماکیان در محفظه&#8204;های مناسب و کنترل و مدیریت زباله&#8204;های خانگی، کاهش خسارت در برابر حملات خدنگ بزرگ را در پی دارد. اتخاذ رویکردهایی به&#8204;منظور کاهش تعارض این گونه با انسان همراه با ترویج نقش آن در کنترل جمعیت مارها و جوندگان می&#8204;تواند خدنگ بزرگ را به گوشت&#173;خواری محبوب نزد جوامع محلی تبدیل کند.

&#160;</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Human-wildlife conflict is on the rise due to human occupation of wildlife habitats and declining wild prey. In this study, we assessed factors influencing the presence of the Indian grey mongoose (IGM), as a species compatible with the human environment and in conflict with humans, and factors affecting poultry depredation by IGM in a residential area of 73 ha in Mollasani city, Khuzestan Province. Social network analysis and Na&#239;ve Bayes classification were used along with completion and analysis of 150 questionnaires. The results showed that 42.7% of the interviewees had experienced IGM predatory attacks on poultry during 2010-2019. Results of the social network analysis showed that the interviewees perceived depletion of wild prey in adjacent habitats and presence of anthropogenic food waste in the study area as main factors influencing the presence of the IGM, leading to conflict with the residents. Results of the Na&#239;ve Bayes classification revealed that protection of poultry in suitable enclosures and management of human waste will decrease poultry depredation by the IGM. Adopting approaches to reduce conflict with humans, while promoting the species&#8217; role in controlling snake and rodent populations, can increase local acceptance of this carnivore.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>33</FPAGE>
			<TPAGE>48</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/32020/01/142020/04/17
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/1/29
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/08/232020/08/312020/10/3
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/7/12
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>کامران</Name>
				<MidName></MidName>
				<Family>الماسیه</Family>
				<NameE>K.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Almasieh</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی خوزستان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>almasieh@asnrukh.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مسلم</Name>
				<MidName></MidName>
				<Family>سواری</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Savari</FamilyE>
				<Organizations>
				<Organization>دانشگاه علوم کشاورزی و منابع طبیعی خوزستان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>savari@asnrukh.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>علیرضا</Name>
				<MidName></MidName>
				<Family>محمدی</Family>
				<NameE>A. R.</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>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Human-wildlife conflict</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Social network analysis</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Indian grey mongoose</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Small carnivores</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تعارض انسان و حیات وحش</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تحلیل شبکه اجتماعی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>خدنگ بزرگ</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>گوشت‌خواران کوچک</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Almasieh, A. 2019. Assessment of carnivores in Agricultural Sciences and Natural Resources University of Khuzestan. In: Proceedings of the First National Conference of Agriculture and Environment of Iran. Mollasani, Iran, pp. 1-12. (In Farsi) ##2.	Amador-alcalá, S., E. J. Naranjo and G. Jimenez-ferrer. 2013. Wildlife predation on livestock and poultry: implications for predator conservation in the rainforest of south-east Mexico. Oryx 47(2): 243-250.##3.	Anthony, M. L., B. A. Knuth and T. B. Lauber. 2004. Gender and citizen participation in wildlife management decision making. Society and Natural Resources 17(5): 395-411.##4.	Bastani, S. and M. Raissi. 2012. Social network analysis as a method: using whole network approach for studying FOSS communities. Journal of Iranian Social Studies 5(2): 31-57. (In Farsi)##5.	Behdarvand, N. and M. Kaboli. 2015. Characteristics of gray wolf attacks on human in an altered landscape in the west of Iran. Human Dimensions of Wildlife 20(2): 112-122.##6.	Behmanesh, M., M. Malekian, M. R. Hemami and S. Fakheran. 2018. Patterns and determinants of human-carnivore conflicts in Central Iran: realities and perceptions behind the conflict. Human Dimensions of Wildlife 24(1): 14-30. ##7.	Blair, R. B. 2001. Birds and butterflies along urban gradients in two ecoregions of the United States: is urbanization creating a homogeneous fauna? pp. 33-56, In: J. L. Lockwood and M. L. McKinney (eds.), Biotic homogenization. Academic Press, Cambridge.##8.	Darvish A., M. Ghorbani, S. Fakheran and A. Soffianian. 2014. Network analysis and key actors toward wildlife management (case study: habitat of caucasian black grouse, Arasbaran Biosphere Reserve). Iranian Journal of Applied Ecology 3(9): 29-41. (In Farsi)##9.	Dickman, A. J. 2010. Complexities of conflict: the importance of considering social factors for effectively resolving human–wildlife conflict. Animal Conservation 13: 458-466.##10.	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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>ارزیابی و مقایسه ذخایر کربن ‌آلی و نیتروژن خاک مراتع و مزارع گندم مجاور در موقعیت‌های مختلف شیب دامنه (مطالعه موردی: مراتع کوهستانی کرمانشاه)</TitleF>
		<TitleE>Soil Organic Carbon Stocks and Nitrogen Content Comparison in Different Slope Positions in Native Grasslands and Adjacent Cultivated Soils (Case Study: Kermanshah Mountain Rangelands, Iran)</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>افزایش گازهای گلخانه&#8204;ای اتمسفر به&#8204;ویژه دی&#8204;اکسیدکربن در اثر مصرف سوخت&#8204;های فسیلی موجب افزایش دمای کره زمین شده &#8204;است. توقف این روند فقط با کاهش مصرف این سوخت&#8204;ها و یا ذخیره کربن &#8204;آلی در خاک امکان&#8204;پذیر است. پوشش گیاهی کره زمین شامل جنگلها، مراتع و اراضی کشاورزی با جذب و ذخیره کربن نقش مؤثری در کاهش گازهای گلخانه&#8204;ای دارد. این مطالعه به&#172;منظور بررسی تأثیر میزان شیب و موقعیت دامنه و نیز کاربری اراضی بر میزان ذخایر کربن&#8204; آلی در یک منطقه کوهستانی واقع در ارتفاعات زاگرس میانی در کرمانشاه انجام شد. نتایج بیانگر تأثیر معنی&#8204;دار شیب و کاربری زمین بر مقدار زیست&#8204;توده، میزان ذخایر کربن&#8204; آلی و نیتروژن خاک است. مقایسه شیب&#8204;های مختلف مرتعی نشان داد که موقعیت پای&#172;&#8204;دامنه با کمترین شیب (20 تا 30 درصد) بیشترین میزان ذخیره کربن &#8204;آلی، درصد نیتروژن خاک و زیست&#8204;توده فوقانی را داشت. حضور درختان پراکنده در مرتع در موقعیت شانه&#172;دامنه موجب افزایش توانایی این موقعیت در ذخیره&#8204;سازی کربن &#8204;آلی خاک در مقایسه با دامنه مشابه بدون درختان شده که احتمالاً در اثر افزوده&#8204;شدن هوموس و یا مراقبت تاج آنها از گونه&#8204;های علفی زیراشکوب درختان است. مقایسه گندمزار با مرتع مجاور با شیب یکسان بیانگر افزایش معنی&#8204;دار (0/05&#62;P) میزان کربن &#8204;آلی و درصد نیتروژن کل در خاک مرتع است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Global warming has been largely driven by increasing atmospheric GHG (Green House Gasses), particularly carbon dioxide caused by fossil fuels burning. The current trend can not be stopped except by reducing fossil fuel consumption or storing organic carbon in soil or earth&#39;s biological systems such as forests, rangelands and agricultural systems. This study was conducted to determine the effect of slope position as well as land use effect on organic carbon storage and nitrogen content in a mountainous area in the middle of Zagros chain mountain ranges in Kermanshah. The results showed that slope position has significant effect on aboveground biomass, SOC (Soil Organic Carbon) and Soil Nitrogen Content (SNC). Comparison of different rangeland slopes showed that the lowest slope position (20-30%) had the highest amount of SOC, SNC and aboveground biomass. The presence of scattered trees in the shoulder position added significant amount of soil organic carbon and total nitrogen content to the soil beneath the trees, resulting from the input of tree litter and positive effect of trees canopy on herbaceous layer. Comparison of natural rangeland in all slope positions and adjacent cropland showed higher amount of SOC and SNC in grasslands. Comparison of croplands and adjacent rangelands with the same slope shows a significant increase in organic carbon content (P&#62;0.05) and soil nitrogen percentage in the rangelands. This situation is also seen in other rangeland slope classes.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>49</FPAGE>
			<TPAGE>61</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/32020/01/142020/04/172020/02/1
		</RECEIVE_DATE>

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

		<ACCEPT_DATE>
			2020/08/232020/08/312020/10/32020/10/7
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/7/16
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>حیدر</Name>
				<MidName></MidName>
				<Family>میرزایی</Family>
				<NameE>H.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mirzaei</FamilyE>
				<Organizations>
				<Organization>دانشگاه رازی</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mirzaei.hd@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>soil organic carbon</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>natural grasslands</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>croplands</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>climate change</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>slope position</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>کربن آلی خاک</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مراتع طبیعی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>اراضی کشاورزی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>تغییرات اقلیمی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>موقعیت شیب دامنه</KeyText>
			</KEYWORD>
		</KEYWORDS>

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Vertical distribution of soil organic carbon density in relation to land use cover, altitude and slope aspect in the Eastern Himalayas. Land 3(4): 1-19.##46.	Tumwesigye, W., J. Wasige and G. Thomas. 2015. Effect of land use change and slope position on soil organic carbon in Kitabi Watershed Rwanda. Journal of Scientific and Innovative Research 4(5): 213-217. ##47.	Van Eerd, L., K. Congreves, A. Hayes, A. Verhallen and D. Hooker. 2014. Long-term tillage and crop rotation effects on soil quality, organic carbon, and total nitrogen. Canadian Journal of Soil Science 94: 303-315.##48.	Xiaofei, M., Z. Chengyi, Y. Wei and Z. Xiaoning. 2019. Influences of 1.5 °C and 2.0 °C global warming scenarios on water use efficiency dynamics in the sandy areas of northern China. Science of The Total Environment 664: 161-174.##49.	Xin, H. Z., J. Z. Wan, G. S. Yi and T. S. Hui. 2014. Slope aspect and slope position have effects on plant diversity and spatial distribution in the hilly region of Mount Taihang, North China. Journal of Food, Agriculture &#38; Environment 12(1): 391-397.##50.	Yu, G., H. Fang, L. Gao and W. Zhang. 2006. Soil organic carbon budget and fertility variation of black soils in Northeast China. Journal of Ecological Research 21: 855-867. ##51.	Yu, G., C. Hui, W. Wei and B. Hong. 2015. Effects of slope position, aspect and cropping system on soil nutrient variability in hilly areas. Journal of Soil Research 53: 338-348.##52.	Zau, M., Q. Feng, M. Zhang, W. Liu, Y. Qin and R. Deo. 2019. Effects of topography on soil organic carbon stocks in grasslands of a semiarid alpine region, northwestern China. Journal of Soils and Sediments 19(4): 1640-1650.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>شناسایی، فراوانی و پراکنش بزرگ‌بی‌مهرگان کف‌زی و ارزیابی زیستی رودخانه قلعه‌رودخان (استان گیلان)</TitleF>
		<TitleE>Identification, Distribution and Abundance of Macroinvertebrates and Biomonitoring of the Ghale Rudkhan River, Guilan Province</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>استفاده از جمعیت بی&#172;مهرگان کف&#172;زی از مناسب&#172;ترین ابزارها برای تعیین سلامت و یکپارچگی زیستی رودخانه&#172;ها و تأثیر فعالیت&#172;های انسانی بر کیفیت آنها است. با توجه به اهمیت رودخانه قلعه&#172;رودخان از نظر گردشگری و رشد جمعیت در حاشیه آن، از شاخص&#172;های زیستی برای ارزیابی وضعیت رودخانه استفاده شد. نمونه&#172;برداری با استفاده از سوربر سمپلر (چشمه 300 میکرون و مساحت 900 سانتی&#172;متر مربع) در 5 ایستگاه با 3 تکرار از اردیبهشت تا آذر 1396 انجام شد. نمونه&#172;ها در اتانول 96 درصد فیکس و به آزمایشگاه انتقال داده شده و شناسایی شدند. فراوانی کل، شاخص EPT، غنای EPT، درصد EPT و نسبت EPT/Chiro محاسبه شد. تعداد 5134 نمونه از 35 جنس، 30 خانواده، 10 راسته، 4 رده و 3 شاخه شناسایی شد. بالاترین غنای EPT در ایستگاه 4 در اردیبهشت&#172;ماه (607 عدد بر مترمربع) و پایین&#172;ترین آن در ایستگاه 5 در مهرماه (7 عدد بر مترمربع) مشاهده شد. حضور گونه&#172;های حساس به آلودگی از جمله Epeorus sp.، Rithrogena sp.، Rhyacophila sp.، Isopela sp.، Gomphus sp.، Cordulegaster sp.، Coenagrion sp.، Oligoneuriella sp.، Heptagenia sp و .Philorus sp نشانگر کیفیت مطلوب آب رودخانه است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Benthic macroinvertebrate-based indices are suitable tools for assessment of stream health and human impacts on its biological integrity. Since Ghale Rudkhan River is an attractive tourist destination and its surrounding population is growing, its water quality was examined usning biological indicators. Macroinvertebrate samples were taken monthly by a Surber sampler (mesh = 300 &#181; and area = 900 cm2) at five stations from May to December 2017. Samples were preserved in ethanol 96% and transported to laboratory for analysis. Total abundance, EPT index, EPT richness and percentage,EPT/CHIR ratios were determined. In total 5134 macroinvertebrates that belong to 35 genera, 30 families, 10 orders, 4 classes and 3 phyla were identified. The highest EPT richness was observed at the station no. 4 in May (607 ind.m-1) and the lowest was at the station no. 5 in October (7 ind.m-1). The presence of pollution sensitive species such as Epeorus sp. Rithrogena sp., Rhyacophila sp., Isopela sp., Gomphus sp., Cordulegaster sp., Coenagrion sp., Oligoneuriella sp., Heptagenia sp., Philorus sp. in Ghale Rudkhan River indicated the optimal quality of the river water.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>63</FPAGE>
			<TPAGE>76</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/32020/01/142020/04/172020/02/12019/12/2
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1398/9/11
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/08/232020/08/312020/10/32020/10/72020/10/21
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/7/30
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>فرشته</Name>
				<MidName></MidName>
				<Family>حاجی آقایی قاضی محله</Family>
				<NameE>F.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Hajiaghaei Ghaazi Mahalleh</FamilyE>
				<Organizations>
				<Organization>دانشگاه گیلان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>ereshte.hj@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>جاوید</Name>
				<MidName></MidName>
				<Family>ایمانپور نمین</Family>
				<NameE>J.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Imanpour Namin</FamilyE>
				<Organizations>
				<Organization>دانشگاه گیلان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>javidiman@gmail.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مسعود</Name>
				<MidName></MidName>
				<Family>ستاری</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Sattari</FamilyE>
				<Organizations>
				<Organization>دانشگاه گیلان</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>msattari647@gmail.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Biomonitoring</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Macroinvertebrates</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Surber sampler</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>EPT Index</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ارزیابی زیستی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>ماکروبنتوز</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>سوربر سمپلر</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>شاخص EPT</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Arifi, K., S. Elblidi, A. Serghini, L. Tahri, A. Yahyaoui and M. Fekhaoui. 2018. Taxonomic diversity of benthic macroinvertebrates and bio-evaluation of water quality of Grou River (Morocco) through the use of the standardized global biological index (IBGN). Journal of Materials and Environmental Science 9(4): 1343-1356.##2.	Behmer, D. J. and C. P. Hawkins. 1986. Effects of overhead canopy on macroinvertebrate production in a Utah stream. Freshwater Biology 16: 283-300.##3.	Chi, S. H., S. Li, S. H. Chen, M. Chen, J. Zheng and J. Hu. 2017. Temporal variations in macroinvertebrate communities from the tributaries in the Three Gorges Reservoir Catchment, China. Revista Chilena de Historia Natural 90: 1-11. ##4.	Cooper, Ch. M. and S. S. Knight. 1991. Water quality cycles in two hill land streams subject to natural, municipal, and non-point agricultural stresses in the Yazoo Basin of Mississipi, USA (1985-1987). Internationale Vereinigung für Theoretische und Angewandte Limnologie: Verhandlungen 24: 1654-1663.##5.	Dodds, W. K., J. S. Perkin and J. E. Gerken. 2013. Human impact on freshwater ecosystem services: a global perspective. Environmental Science and Technology 47(16): 9061-9068.##6.	Dudlley, T. L., S. D. Coopera and N. hemphill. 1986. Effects of macroalgae on a stream invertebrate community. Journal of the North American Benthological Society 5: 93-106.##7.	Durán, J., A. Rodríguez, J. L. Morse and P. M. Groffman. 2013. Winter climate change effects on soil C and N cycles in urban grasslands. Global Change Biology 19: 2826-2837.##8.	Ehlinger, T. J., C. D. Sandgren and L. S. Dethorne. 2003. Monitoring of stream habitat and aquatic biotic integrity lincoln Creec Milwaukee Country, Wisconsin. Department of Biological Sciences, University of Wisconsin, Milwaukee, USA.##9.	Feminella, J. W. 1999. Biotic indicators of water quality the Alabama watershed demonstration project. Aubum University, Auburn, Alabama, USA.##10.	Fierroa, P., I. Arismendic, M. Robert, D. Hughesc, C. Valdovinosa, A. Alfonso Jara-Floresa. 2018. Benthic macroinvertebrate multimetric index for Chilean Mediterranean streams. Ecological Indicators 91: 13-23.##11.	Fries, L. T. and D. E. Bowles. 2002. Water quality and macroinvertebrate community structure associated with a sportfish hatchery. North American Journal of Aquaculture 64(4): 257-266.##12.	Gerth, W., J. Li and R.Giannico. 2017. Agricultural land use and macroinvertebrate assemblages in lowland temporary streams of the Willamette Valley, Oregon, USA. Agriculture, Ecosystems and Environment 236: 154-165.##13.	Gowen, R. J. 1992. Aquaculture and the environment. In: Aquaculture and the environment: reviews of the International Conference Aquaculture Europe. Dublin, Ireland. European Aquaculture Society Special Publication, 16, pp. 23-48.##14.	 Imanpour Namin, J., P. Spurny. 2004. Effects of unfavorable environmental factors on prosperity of Ichthyocenoses of the middle course of the Becva River. PhD Thesis, Mendel University, Brno, Czech Republic.##15.	Kerans, G. L. and J. R. Karr. 1994. A benthic index of biotic integrity of rivers of Tennessee Valley. Journal of Applied Ecology 4: 768-785.##16.	Li, L., B. Zheng and L. Liu. 2010. Biomonitoring and bioindicators used for river ecosystems: definitions, approaches and trends. Procedia Environmental Sciences 2: 1510-1524.##17.	Loch, D. D., J. L. West and D. G. Perlmutter. 1999. The effect of trout farm effluent on the taxa richness of benthic macroinvertebrates. Aquaculture 147: 37-55.##18.	Ludwig, J. and J. F. Reynolds. 1988. Statistical ecology: a primer on methods and computing. A Niley-Interscience Publication, New York, USA.##19.	Lydy, M. J., C. G. Crawfor and J. W. Frey. 2000. A comparison of selected diversity, similary and biotic indices for detecting changes in benthic-invertebrate community structure and stream quality. Archives of Environmental Contomination and Toxicology 39: 469-479.##20.	Meybeck, M., D. V. Chapman and R. Helmer. 1989. Global freshwater quality: a first assessment. Blackwell Reference, Published on behalf of the World Health Organization and the United Nations Environmental Programme, Oxford.##21.	 Min, C., T. Y. Chiu, M. Chou and K. Hwa. 2018. Seasonal patterns of stream macroinvertebrate communities inresponse to anthropogenic stressors in monsoonal. Taiwan Journal of Asia-Pacific Entomology 21(1): 423-429.##22.	Ministry of Defence and Armed Forces Logistics. 2003. Geographical catalogue of rivers of Iran, Caspian Sea basins. National Geographic Organization Publication, Tehran.##23.	Morin, A. 1988. Effect of microhabitat features, seston quality, and periphyton on abundance of overwintering black fly larvae in Southern Quebec. Journal of Limnology and Oceanography 33(3): 431-446.##24.	Navis, N. and W. N. Gillies. 2001. A comparison of a professional method and a volunteer method for assessing stream health, including discussion of an improved volunteer method. United States Environmental Protection Agency Publication, West Virginia, USA.##25.	NCDEHNR (North Carolina Department of Environment, Health, and Natural Resources). 1997. Standard operating procedures for biological monitoring. Environmental Sciences Branch, Biological Assessment Group, Division of Water, Water Quality Section.##26.	Patric, K. R. and C. W. Reimer. 1995. The diatoms of the United States, Exclusive of Alaska and Hawaii, 1st edition. Academy of Natural Sciences Publications, Philadelphia, USA.##27.	Pennak, R. W. 1953. Freshwater invertebrates of United States. The Ronald Press Company, New York.##28.	Plafkin, J. L., M. T. Barbour, K. D. Porter, S. K. Gross and R. M. Hughes. 1989. Rapid bioassessment protocols for use in streams and rivers: benthic macroinvertebrates and fish. U.S. Environmental Protection Agency, Office of Water Regulations and Standards, Washington, D. C.##29.	Quigley, M. 1986. Invertebrates of streams and rivers. Edward Arnolds Publication, Northampton, UK.##30.	Quinn, J. M. and C. W. Hickey. 1990. Characterisation and classification of benthic invertebrate communities in 88 New Zealand rivers in relation to environmental factors. New Zealand Journal of Marine and Freshwater Research 24(3): 387-409.##31.	Resh, W. H. and M. T. Barbour. 1995. Design and implementation of rapid assessment approaches for water resource monitoring using benthic macroinvertebrates. Australian Journal of Ecology 20: 101-135.##32.	Rosenberg, D. M. and V. H. Resh. 1993. Freshwater biomonitoring and benthic macroinvertebrates. Chapman and Hall, New York.##33.	Roy, A. H., A. D. Rosemond, M. J. Paul, D. S. Leigh and J. B. Wallace. 2003. Stream macroinvertebrate response to catchment urbanization (Georgia, USA). Freshwater Biology 48: 329-346.##34.	Stephens, W. W. and J. L. Farris. 2004. Instream community assessment of aquaculture effluents. Aquaculture 112: 149-162.##35.	Taylor, B. R. and R. C. Baily. 1997. Technical evaluation on methods for benthic invertebrate’s data analysis and interpretation. Canada Center for Mineral and Energy Technology, Ottawa, Ontario.##36.	Towns, R. 1981. Effects of artificial shading on periphyton and invertebrates in a New Zealand stream. New Zealand Journal of Marine and Freshwater Research  15: 185-192.##37.	Voelker, D. C. and D. E. Renn. 2000. Benthic invertebrates and quality of streambed sediments in the White River and selected tributaries in and near Indianapolis, Indiana. USGS Science for a Changing World, Virginia, USA.##38.	Washington, H. G. 2003. Diversity, biotic, similarity indices, a review with special relevance to aquatic ecosystems. Water Research 18: 653-694.##39.	Wright, J. F., D. W. Sutcliffe and M. T. Furse. 2000. Assessing the biological quality of fresh waters: rivpacs and other techniques. Freshwater Biological Association, Ambleside, United Kingdom.## ##</REF>
			</REFRENCE>
		</REFRENCES>

	</ARTICLE>


	<ARTICLE> 
		<TitleF>تعارضات اجتماعی و مدیریت مراتع: مطالعه موردی مراتع شهرستان کلات نادر</TitleF>
		<TitleE>Social Conflicts and Rangeland Management: A Case Study at Rangelands of Kalatnader County, Iran</TitleE>
		<TitleLang_ID>1</TitleLang_ID>
		<ABSTRACTS>
			<ABSTRACT>
			<Language_ID>1</Language_ID>
			<CONTENT>کمبود یا محدودیت منابع طبیعی از یک طرف و نیازهای معیشتی مردم از طرف دیگر، باعث افزایش بهره&#8207;برداری&#8207;ها و اختلافات و درگیری&#8207;ها بر سر استفاده از منابع طبیعی می&#8204;شود. با توجه به هدف اصلی پژوهش یعنی بررسی تعارضات اجتماعی- مدیریتی مراتع شهرستان کلات&#172;&#172;&#172;نادر، اسامی بهره&#8207;برداران مراتع از اداره منابع &#8204;طبیعی و آبخیزداری شهرستان تهیه شد و ایشان از طریق مصاحبه و پرسش-نامه مورد پرسشگری قرار گرفتند. داده&#8207;ها، پایش و کدگذاری شده و سپس به&#172;وسیله نرم&#8207;افزارهای SPSS و Amos مورد تجزیه و تحلیل و مدل&#172;سازی قرار گرفتند. نتایج نشان داد 52 درصد پاسخگویان، نگرش مثبت به منابع &#8204;طبیعی دارند ولی 36 درصد با اداره منابع &#8204;طبیعی، 41 درصد با سایر نهادها و 43 درصد با سایر مرتع&#8204;داران در تعارض هستند. 67 درصد، مشارکت با سایر مرتع&#8204;داران را راهکار حل تعارض دانسته&#8204;اند. مهم&#172;ترین متغیرهای تأثیرگذار، اعتماد اجتماعی و خشونت&#8204;طلبی به&#172;دست آمد که قدرت تبیین مسئله را تا بیش از 71 درصد دارند. بررسی تعارضات اجتماعی در زمینه منابع طبیعی نشان داد که ظرفیت ایجاد تعارضات در منطقه بالاست. در نتیجه، رویکرد حل تعارضات و پیشبرد روش&#8207;های مذاکره برای حل اختلافات ضروری است. همچنین تهیه نقشه&#8207;های مستند جامع (کاداستر)، بررسی دقیق موضوعات مورد تعارض، و اطلاع&#8207;رسانی مستمر فرایند بررسی&#8207;ها، زمینه&#8207;ساز کاهش تعارضات ارضی است.</CONTENT>
			</ABSTRACT>
			<ABSTRACT>
			<Language_ID>2</Language_ID>
			<CONTENT>Conflicts over natural resources increase due to a lack or limitation of natural resources and an increasing demand for growing populations. The current research aimed to investigate the conflict management between people and natural resources organizations. A list of local beneficiaries was obtained from Office of Natural Resources and Watershed Management of Kalatnader County, Khorasan-Razavi Province, Iran. The beneficiaries were surveyed through the in-person interview as well as a researcher-made questionnaire. Data were analyzed and modeled by SPSS and Amos softwares. The results indicated that 52% of the respondents had a positive attitude towards natural resources, but 36% were in conflict with the Office, 41% with other institutions, and 43% with other ranchers. Sixty seven percent of participants believed that collaboration with other ranchers could be a solution for the conflict. The most important influencing variables were social trust and violence, which could explain the dependent variable up to 71%. As a result, a conflict resolution approach and advancing negotiation techniques are needed to resolve disputes. Furthermore, the preparation of comprehensive cadastral maps, detailed investigation of conflicting issues, and continuous updating of the investigation process lead to a reduction of land conflicts.</CONTENT>
			</ABSTRACT>
		</ABSTRACTS>

		<PAGES>
			<PAGE>
			<FPAGE>77</FPAGE>
			<TPAGE>97</TPAGE>
			</PAGE>
		</PAGES>

		<RECEIVE_DATE>
			2020/02/32020/01/142020/04/172020/02/12019/12/22020/06/27
		</RECEIVE_DATE>

		<RECEIVE_DATE_FA>
			1399/4/7
		</RECEIVE_DATE_FA>

		<ACCEPT_DATE>
			2020/08/232020/08/312020/10/32020/10/72020/10/212020/11/10
		</ACCEPT_DATE>

		<ACCEPT_DATE_FA>
			1399/8/20
		</ACCEPT_DATE_FA>

		<AUTHORS>
			<AUTHOR>
				<Name>محمدعلی</Name>
				<MidName></MidName>
				<Family>جنتی چنار</Family>
				<NameE>M. A.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Jannatichenar</FamilyE>
				<Organizations>
				<Organization>دانشگاه فردوسی مشهد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mjanati92@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>مهدی</Name>
				<MidName></MidName>
				<Family>کلاهی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Kolahi</FamilyE>
				<Organizations>
				<Organization>دانشگاه فردوسی مشهد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mahdikolahi@um.ac.ir</Email>
				</EMAILS>
			</AUTHOR>

			<AUTHOR>
				<Name>منصور</Name>
				<MidName></MidName>
				<Family>مصداقی</Family>
				<NameE>M.</NameE>
				<MidNameE></MidNameE>
				<FamilyE>Mesdaghi</FamilyE>
				<Organizations>
				<Organization>دانشگاه فردوسی مشهد</Organization>
				</Organizations>
				<Countries>
				<Country>ایران</Country>
				</Countries>
				<EMAILS>
				<Email>mesdagh@yahoo.com</Email>
				</EMAILS>
			</AUTHOR>
		</AUTHORS>


		<KEYWORDS>
			<KEYWORD>
				<KeyText>Social Issues</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>Range Beneficiaries</KeyText>
			</KEYWORD>

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

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

			<KEYWORD>
				<KeyText>Negotiation.</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مسائل اجتماعی</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مرتع‌داران</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مدیریت تضادها</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>حل تعارضات</KeyText>
			</KEYWORD>

			<KEYWORD>
				<KeyText>مذاکره</KeyText>
			</KEYWORD>
		</KEYWORDS>

		<REFRENCES>
			<REFRENCE>
				<REF>1.	Adeli, K. and A. Rahimi Nasab 2012. Investigating the legislation process in Iran's natural resources. In: Proceeding of First National Conference on Zagros Environmental Law and Natural Resources. Khorramabad, Iran. pp. 115-124. (In Farsi)##2.	Afrakhteh, H., M. Hajipour, M. Gourzin and B. Nejati. 2013. The situation of sustainable agricultural development in Iran development plans case: five-year plans after the revolution. Quarterly Journal of the Macro and Strategic Policies 1(l): 43-62. (In Farsi)##3.	Ahmadi, M., M. Nourpour and M. S. Esfandiari. 2012. Iran's criminal policy on protection and conservation of forests and rangelands. In: Proceeding of First National Conference on Zagros Environmental Law and Natural Resources. Khorramabad, Iran. pp. 374-385. (In Farsi)##4.	Ansari, N., J. Seyed Akhlaghi Shal and M. Ghasemi. 2009. Determination of socio-economic factors on natural resources degradation of Iran. 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			</REFRENCE>
		</REFRENCES>

	</ARTICLE>

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