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<!DOCTYPE ArticleSet PUBLIC "-//NLM//DTD PubMed 2.7//EN" "https://dtd.nlm.nih.gov/ncbi/pubmed/in/PubMed.dtd">
<ArticleSet>
<Article>
<Journal>
				<PublisherName>Shahid Beheshti University</PublisherName>
				<JournalTitle>Advanced Environmental Sciences</JournalTitle>
				<Issn>3115-7173</Issn>
				<Volume>6</Volume>
				<Issue>2</Issue>
				<PubDate PubStatus="epublish">
					<Year>2008</Year>
					<Month>12</Month>
					<Day>21</Day>
				</PubDate>
			</Journal>
<ArticleTitle>Forest Landscape-and-Ecological Degradation Assessment of Sefidrod Watershed; Using Landscape Ecological Metrics, in Gilan Province of Iran</ArticleTitle>
<VernacularTitle>Forest Landscape-and-Ecological Degradation Assessment of Sefidrod Watershed; Using Landscape Ecological Metrics, in Gilan Province of Iran</VernacularTitle>
			<FirstPage></FirstPage>
			<LastPage></LastPage>
			<ELocationID EIdType="pii">95526</ELocationID>
			
			
			<Language>FA</Language>
<AuthorList>
<Author>
					<FirstName>Nooshin</FirstName>
					<LastName>Khazaei</LastName>
<Affiliation>Department of Student of Environmental Planning &amp; Management, Faculty of Environment, University of Tehran</Affiliation>

</Author>
<Author>
					<FirstName>, Forod</FirstName>
					<LastName>Azari Dehkordi</LastName>
<Affiliation>Department of Student of Environmental Planning &amp; Management, Faculty of Environment, University of Tehran</Affiliation>

</Author>
</AuthorList>
				<PublicationType>Journal Article</PublicationType>
			<History>
				<PubDate PubStatus="received">
					<Year>2015</Year>
					<Month>05</Month>
					<Day>17</Day>
				</PubDate>
			</History>
		<Abstract>&lt;span style=&quot;left: 126.08px; top: 631.107px; font-size: 10.72px; font-family: serif; transform: scaleX(0.957223);&quot; dir=&quot;ltr&quot;&gt;Landscape ecological metrics are quantitative tools that are &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 644.707px; font-size: 10.72px; font-family: serif; transform: scaleX(0.952066);&quot; dir=&quot;ltr&quot;&gt;used to evaluate the patterns of landscape. In this article we &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 658.147px; font-size: 10.72px; font-family: serif; transform: scaleX(0.96512);&quot; dir=&quot;ltr&quot;&gt;considered some landscape ecological metrics such as SDI &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 671.587px; font-size: 10.72px; font-family: serif; transform: scaleX(0.979011);&quot; dir=&quot;ltr&quot;&gt;(Shannon Diversity Index) or TE (Total Edge) to consider &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 685.027px; font-size: 10.72px; font-family: serif; transform: scaleX(1.0062);&quot; dir=&quot;ltr&quot;&gt;configuration and composition of the landscape patches. &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 698.627px; font-size: 10.72px; font-family: serif; transform: scaleX(0.939168);&quot; dir=&quot;ltr&quot;&gt;Then, a degradation model (DM) was conducted to compute &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 712.067px; font-size: 10.72px; font-family: serif; transform: scaleX(0.965425);&quot; dir=&quot;ltr&quot;&gt;the degradation hierarchy between working units. The DM &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.12754);&quot; dir=&quot;ltr&quot;&gt;was introduced as &quot;L&lt;/span&gt;&lt;span style=&quot;left: 227.68px; top: 729.787px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;D&lt;/span&gt;&lt;span style=&quot;left: 232.16px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.29719);&quot; dir=&quot;ltr&quot;&gt;&quot; = &lt;/span&gt;&lt;span style=&quot;left: 258.56px; top: 725.507px; font-size: 10.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;∑&lt;/span&gt;&lt;span style=&quot;left: 265.92px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.12514);&quot; dir=&quot;ltr&quot;&gt;kI/V, where &quot;L&lt;/span&gt;&lt;span style=&quot;left: 336.96px; top: 729.787px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;D&lt;/span&gt;&lt;span style=&quot;left: 341.44px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.13822);&quot; dir=&quot;ltr&quot;&gt;&quot; was &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 739.107px; font-size: 10.72px; font-family: serif; transform: scaleX(1.03698);&quot; dir=&quot;ltr&quot;&gt;degradation coefficient of landscape compartment, &quot;k&quot; &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 752.547px; font-size: 10.72px; font-family: serif; transform: scaleX(1.06769);&quot; dir=&quot;ltr&quot;&gt;(intensity) and &quot;I&quot; metrics of landscape, and &quot;V&quot; was &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 765.987px; font-size: 10.72px; font-family: serif; transform: scaleX(0.960484);&quot; dir=&quot;ltr&quot;&gt;vulnerability of the natural habitat (here number of patches &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 779.587px; font-size: 10.72px; font-family: serif; transform: scaleX(0.929066);&quot; dir=&quot;ltr&quot;&gt;in each working unit). &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 793.027px; font-size: 10.72px; font-family: serif; transform: scaleX(1.07349);&quot; dir=&quot;ltr&quot;&gt;Thirteen sub watersheds in Sefidrod Watershed were &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 806.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.999378);&quot; dir=&quot;ltr&quot;&gt;considered and thus, degradation model was deployed to &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 820.067px; font-size: 10.72px; font-family: serif; transform: scaleX(0.952444);&quot; dir=&quot;ltr&quot;&gt;assess the status of each working unit. On the other hand, if &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 833.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.02566);&quot; dir=&quot;ltr&quot;&gt;there are deep red pixels in an infrared image, there are &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 846.947px; font-size: 10.72px; font-family: serif; transform: scaleX(1.07979);&quot; dir=&quot;ltr&quot;&gt;more areas of older ecosystems. Therefore, to reveal &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 860.547px; font-size: 10.72px; font-family: serif; transform: scaleX(1.1278);&quot; dir=&quot;ltr&quot;&gt;relationship between a metric and the status of the &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 873.987px; font-size: 10.72px; font-family: serif; transform: scaleX(0.95079);&quot; dir=&quot;ltr&quot;&gt;ecosystems in each working unit, the pixel number of deep-&lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 887.427px; font-size: 10.72px; font-family: serif; transform: scaleX(0.944087);&quot; dir=&quot;ltr&quot;&gt;redness of infrared images was plotted against each metrics. &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 901.027px; font-size: 10.72px; font-family: serif; transform: scaleX(0.93248);&quot; dir=&quot;ltr&quot;&gt;Therefore, it was cleared that SDI has the highest correlation &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 914.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.931305);&quot; dir=&quot;ltr&quot;&gt;(R&lt;/span&gt;&lt;span style=&quot;left: 136.16px; top: 912.827px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;2&lt;/span&gt;&lt;span style=&quot;left: 139.2px; top: 914.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.923672);&quot; dir=&quot;ltr&quot;&gt; = 0.85) with the color intensity of infrared images. &lt;/span&gt;</Abstract>
			<OtherAbstract Language="FA">&lt;span style=&quot;left: 126.08px; top: 631.107px; font-size: 10.72px; font-family: serif; transform: scaleX(0.957223);&quot; dir=&quot;ltr&quot;&gt;Landscape ecological metrics are quantitative tools that are &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 644.707px; font-size: 10.72px; font-family: serif; transform: scaleX(0.952066);&quot; dir=&quot;ltr&quot;&gt;used to evaluate the patterns of landscape. In this article we &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 658.147px; font-size: 10.72px; font-family: serif; transform: scaleX(0.96512);&quot; dir=&quot;ltr&quot;&gt;considered some landscape ecological metrics such as SDI &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 671.587px; font-size: 10.72px; font-family: serif; transform: scaleX(0.979011);&quot; dir=&quot;ltr&quot;&gt;(Shannon Diversity Index) or TE (Total Edge) to consider &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 685.027px; font-size: 10.72px; font-family: serif; transform: scaleX(1.0062);&quot; dir=&quot;ltr&quot;&gt;configuration and composition of the landscape patches. &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 698.627px; font-size: 10.72px; font-family: serif; transform: scaleX(0.939168);&quot; dir=&quot;ltr&quot;&gt;Then, a degradation model (DM) was conducted to compute &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 712.067px; font-size: 10.72px; font-family: serif; transform: scaleX(0.965425);&quot; dir=&quot;ltr&quot;&gt;the degradation hierarchy between working units. The DM &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.12754);&quot; dir=&quot;ltr&quot;&gt;was introduced as &quot;L&lt;/span&gt;&lt;span style=&quot;left: 227.68px; top: 729.787px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;D&lt;/span&gt;&lt;span style=&quot;left: 232.16px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.29719);&quot; dir=&quot;ltr&quot;&gt;&quot; = &lt;/span&gt;&lt;span style=&quot;left: 258.56px; top: 725.507px; font-size: 10.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;∑&lt;/span&gt;&lt;span style=&quot;left: 265.92px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.12514);&quot; dir=&quot;ltr&quot;&gt;kI/V, where &quot;L&lt;/span&gt;&lt;span style=&quot;left: 336.96px; top: 729.787px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;D&lt;/span&gt;&lt;span style=&quot;left: 341.44px; top: 725.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.13822);&quot; dir=&quot;ltr&quot;&gt;&quot; was &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 739.107px; font-size: 10.72px; font-family: serif; transform: scaleX(1.03698);&quot; dir=&quot;ltr&quot;&gt;degradation coefficient of landscape compartment, &quot;k&quot; &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 752.547px; font-size: 10.72px; font-family: serif; transform: scaleX(1.06769);&quot; dir=&quot;ltr&quot;&gt;(intensity) and &quot;I&quot; metrics of landscape, and &quot;V&quot; was &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 765.987px; font-size: 10.72px; font-family: serif; transform: scaleX(0.960484);&quot; dir=&quot;ltr&quot;&gt;vulnerability of the natural habitat (here number of patches &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 779.587px; font-size: 10.72px; font-family: serif; transform: scaleX(0.929066);&quot; dir=&quot;ltr&quot;&gt;in each working unit). &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 793.027px; font-size: 10.72px; font-family: serif; transform: scaleX(1.07349);&quot; dir=&quot;ltr&quot;&gt;Thirteen sub watersheds in Sefidrod Watershed were &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 806.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.999378);&quot; dir=&quot;ltr&quot;&gt;considered and thus, degradation model was deployed to &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 820.067px; font-size: 10.72px; font-family: serif; transform: scaleX(0.952444);&quot; dir=&quot;ltr&quot;&gt;assess the status of each working unit. On the other hand, if &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 833.507px; font-size: 10.72px; font-family: serif; transform: scaleX(1.02566);&quot; dir=&quot;ltr&quot;&gt;there are deep red pixels in an infrared image, there are &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 846.947px; font-size: 10.72px; font-family: serif; transform: scaleX(1.07979);&quot; dir=&quot;ltr&quot;&gt;more areas of older ecosystems. Therefore, to reveal &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 860.547px; font-size: 10.72px; font-family: serif; transform: scaleX(1.1278);&quot; dir=&quot;ltr&quot;&gt;relationship between a metric and the status of the &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 873.987px; font-size: 10.72px; font-family: serif; transform: scaleX(0.95079);&quot; dir=&quot;ltr&quot;&gt;ecosystems in each working unit, the pixel number of deep-&lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 887.427px; font-size: 10.72px; font-family: serif; transform: scaleX(0.944087);&quot; dir=&quot;ltr&quot;&gt;redness of infrared images was plotted against each metrics. &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 901.027px; font-size: 10.72px; font-family: serif; transform: scaleX(0.93248);&quot; dir=&quot;ltr&quot;&gt;Therefore, it was cleared that SDI has the highest correlation &lt;/span&gt;&lt;span style=&quot;left: 126.08px; top: 914.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.931305);&quot; dir=&quot;ltr&quot;&gt;(R&lt;/span&gt;&lt;span style=&quot;left: 136.16px; top: 912.827px; font-size: 6.72px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;2&lt;/span&gt;&lt;span style=&quot;left: 139.2px; top: 914.467px; font-size: 10.72px; font-family: serif; transform: scaleX(0.923672);&quot; dir=&quot;ltr&quot;&gt; = 0.85) with the color intensity of infrared images. &lt;/span&gt;</OtherAbstract>
		<ObjectList>
			<Object Type="keyword">
			<Param Name="value">Keywords: landscape ecology metrics</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Quantification</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">degradation modeling</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Sefidrod</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Gilan</Param>
			</Object>
		</ObjectList>
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