<?xml version="1.0" encoding="utf-8"?>
<journal>
<title>Environmental Erosion Research</title>
<title_fa>پژوهش هاي فرسايش محيطي</title_fa>
<short_title>E.E.R.</short_title>
<subject>Literature &amp; Humanities</subject>
<web_url>http://magazine.hormozgan.ac.ir</web_url>
<journal_hbi_system_id>1</journal_hbi_system_id>
<journal_hbi_system_user>admin</journal_hbi_system_user>
<journal_id_issn>2251-7812</journal_id_issn>
<journal_id_issn_online>2717-3968</journal_id_issn_online>
<journal_id_pii></journal_id_pii>
<journal_id_doi>10.61882/jeer</journal_id_doi>
<journal_id_iranmedex></journal_id_iranmedex>
<journal_id_magiran></journal_id_magiran>
<journal_id_sid>6561</journal_id_sid>
<journal_id_nlai>8888</journal_id_nlai>
<journal_id_science>45855/11/3/90</journal_id_science>
<language>fa</language>
<pubdate>
	<type>jalali</type>
	<year>1403</year>
	<month>12</month>
	<day>1</day>
</pubdate>
<pubdate>
	<type>gregorian</type>
	<year>2025</year>
	<month>3</month>
	<day>1</day>
</pubdate>
<volume>15</volume>
<number>1</number>
<publish_type>online</publish_type>
<publish_edition>1</publish_edition>
<article_type>fulltext</article_type>
<articleset>
	<article>


	<language>fa</language>
	<article_id_doi></article_id_doi>
	<title_fa>اثرپذیری ویژگی‌های بیولوژیک خاک مرتع در مواجهه با تغییر کاربری به دیمزار(مطالعه موردی: مراتع کرمانشاه)</title_fa>
	<title>Effectiveness of biological characteristics of rangeland soil in the face of land use change to dryland (Case study: Rangelands in Kermanshah)</title>
	<subject_fa>مدیریت و کنترل اثرات فرسایش محیطی</subject_fa>
	<subject></subject>
	<content_type_fa>مستخرج از پایان‌نامه / رساله / طرح پژوهشی</content_type_fa>
	<content_type></content_type>
	<abstract_fa>&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;direction:rtl&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;پژوهش حاضر با هدف بررسی اثرپذیری ویژگی&#8204;های بیولوژیک خاک مرتع در برابر تغییر کاربری به دیمزار در سه محدوده قلعه، چشمه&#8204;قادر و محمودآباد کرمانشاه صورت گرفت. بدین منظور در هر محدوده، دو تیمار دیمزار و مرتع انتخاب شد و ویژگی&#8204;های بیولوژیک خاک اندازه&#8204;گیری گردیده و با استفاده از آزمون تی&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&amp;lrm;&lt;/span&gt;&lt;/span&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;استیودنت مستقل مقایسه شد. نتایج نشان داد حداکثر و حداقل میزان تنفس پایه خاک به&#8204;ترتیب در دیمزار قلعه و مرتع چشمه&#8204;قادر بود. میزان تنفس برانگیخته در مراتع چشمه&#8204;قادر، قلعه و محمودآباد به&#8204;ترتیب 27/98 و 97/95 و 63/87 و در دیمزار 57/92، 47/86 و 97/81 میلی&#8204;گرم در کیلوگرم اندازه&#8204;گیری شد. کربن زیست توده میکروبی در مراتع قلعه، چشمه&#8204;قادر و محمودآباد به&#8204;ترتیب 189، 197 و 181 و در دیمزار 191، 155 و 181 میلی&#8204;گرم در کیلوگرم اندازه&#8204;گیری شد. بیشترین و کمترین میزان نیتـروژن زیسـت توده میکروبی به&#8204;ترتیب در مرتع چشمه&#8204;قادر (13میلی&#8204;گرم در کیلوگرم) و دیمزارها محمودآباد ( 77/5 میلی&#8204;گرم در کیلوگرم) حاصل آمد. ضریب متابولیکی میکروبی در دیمزار قلعه، چشمه&#8204;قادر و محمودآباد به&#8204;ترتیب 12/5، 96/3 و 5 میلی&#8204;گرم در کیلوگرم بود که در مرتع به&#8204;ترتیب به 21/3، 83/2 و 52/3 کاهش یافت. براساس نتایج، پارامترهای تنفس پایه خاک، کربن زیست توده میکروبی، نیتـروژن زیست توده میکروبی، نیتـروژن زیسـت توده میکروبی به نیتروژن کل و ضریب متابولیکی میکروبی در سطح 01/0 و پارامترهای تنفس بر انگیخته و شاخص قابلیت دسترسی کربن در سطح 05/0 تغییرات معنی&#8204;داری داشتند. بنابراین اتخاذ شیوه&#8204;های مناسب برای کاهش اثرات منفی تغییر کاربری مراتع به اراضی کشاورزی بر سلامت خاک در بلندمدت بسیار مهم است.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&amp;nbsp;</abstract_fa>
	<abstract>&lt;span style=&quot;font-size:11pt&quot;&gt;&lt;span style=&quot;line-height:normal&quot;&gt;&lt;span calibri=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;a name=&quot;_Hlk179542787&quot;&gt;&lt;/a&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:8pt&quot;&gt;&lt;span style=&quot;line-height:normal&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-style:italic&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.5pt&quot;&gt;1- Introduction&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;Changing the use of rangeland to agriculture is a significant process in land and natural resource management. This practice has gained increased attention in recent years due to the growing global demand for food and agricultural products. While this land-use change can potentially address food security concerns, it also poses environmental challenges and consequences. These include damage to natural ecosystems, soil degradation, biodiversity loss, and climate change. Therefore, a thorough understanding of both the benefits and drawbacks of this transition is crucial to ensure sustainable growth and the conservation of natural resources. The present study aimed to investigate the impact of land-use change from rangeland to dryland agriculture on the biological characteristics of rangeland soil in a specific region of Kermanshah. &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.5pt&quot;&gt;2-Methodology&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;In this study, several including as basic soil respiration, stimulated respiration, microbial biomass carbon, microbial biomass nitrogen, carbon to nitrogen ratio of microbial biomass, microbial ratio, microbial metabolic coefficient and carbon availability index were measured. After the sampling and laboratory examinations, one-way analysis of variance (ANOVA) was used to compare the soil characteristics in two land use of rangeland and rainfed agricultural land in the three areas of Qala, Cheshme Qadir and Mahmoud Abad region. Moreover, Duncan&amp;#39;s test was employed in SPSS software to compare the mean of biological parameters.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.5pt&quot;&gt;3- Results &lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;The results showed that the highest amount of basic soil respiration was recorded in the dry agricultural use of Qala area with the amount of 78.3 mg/kg of dry soil and the lowest amount was recorded in the rangeland use of Cheshme Qadir area. The amount of stimulated respiration was measured in rangeland land use in two areas of Cheshme Qadir and Qala, 27.98 and 95.97, respectively, and in dryland land use, 57.92 and 86.47 mg/kg of dry soil were measured. Meanwhile, in Mahmoud Abad area, the stimulated respiration of soil in the dryland agricultural use was more than that of the rangeland land, and its amount was measured at 87.63 mg/kg dry soil in the dry land land use and 81.97 mg/kg in the rangeland land use. The carbon values of microbial biomass were measured in three areas of Qala, Cheshme Qadir and Mahmood Abad in rangeland land, respectively 189, 197 and 181, and in agricultural land, 191, 155 and 181 mg of carbon per kilogram of soil, respectively. The highest amount of microbial biomass nitrogen among rangeland uses among the three studied areas was measured in Cheshme Qadir rangeland with a value of 13.60 mg per kilogram of dry matter. The lowest amount was also obtained in the agricultural use of Mahmoud Abad region with the amount of 5.77 mg per kilogram of dry bark. Nitrogen values of microbial biomass to total nitrogen were measured in the three areas of Qala, Cheshme Qadir and Mahmoodabad, respectively, 28.09, 26.92, and 36.25 in rangeland land use, and also in agricultural land use, 22.70, 24.49, respectively. and it was 33.31 and the ratio of carbon to nitrogen of microbial biomass was almost equal in all the studied areas in both studied uses. Also, the highest amount of microbial ratio was measured in agricultural use of Cheshme Qadir area with 0.78 mg/kg of soil. The values of microbial metabolic coefficient were measured in three areas of Qala, Cheshme Qadir and Mahmoodabad, respectively, 5.12, 3.96 and 5 mg/kg of soil in agricultural use, and in rangeland use it was 3.21, 2.83 and 2.83, respectively. It decreased by 3.52 and the results showed that the value of carbon availability index was higher in agricultural use than rangeland use&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;page-break-after:avoid&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.5pt&quot;&gt;4- Discussion &amp; &lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.2pt&quot;&gt;Conclusions&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;b&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;letter-spacing:-.5pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:10pt&quot;&gt;&lt;span style=&quot;unicode-bidi:embed&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;Based on the results obtained from the present research, the conversion of land from rangelands to rainfed land causes a change in the basic soil respiration parameters, microbial biomass carbon, microbial biomass nitrogen, microbial biomass nitrogen to total nitrogen and microbial metabolic coefficient at a significant level of 1%. confidence factor was 99 percent). Also, the parameters of stimulated respiration and the index of carbon availability were changed with the conversion of rangeland to dryland with a significant level of 5% (95% confidence coefficient). The parameters of carbon to nitrogen ratio of microbial biomass and microbial ratio did not change significantly. Accordingly, it can be acknowledged that the conversion of rangeland to agriculture significantly changes the biological properties of the soil. While it can lead to increased productivity, it is important to adopt sustainable practices to minimize negative impacts on soil health and maintain its long-term. &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;letter-spacing:-.3pt&quot;&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&amp;nbsp;</abstract>
	<keyword_fa>تغییر کاربری اراضی, تنفس پایه خاک, ضریب متابولیکی میکروبی, سلامت خاک.</keyword_fa>
	<keyword>Land use change, Sustainable agriculture, Grazing, Soil biodiversity.</keyword>
	<start_page>25</start_page>
	<end_page>44</end_page>
	<web_url>http://magazine.hormozgan.ac.ir/browse.php?a_code=A-10-200-2&amp;slc_lang=fa&amp;sid=1</web_url>


<author_list>
	<author>
	<first_name>Hamed</first_name>
	<middle_name></middle_name>
	<last_name>Joneidi</last_name>
	<suffix></suffix>
	<first_name_fa>حامد</first_name_fa>
	<middle_name_fa></middle_name_fa>
	<last_name_fa>جنیدی</last_name_fa>
	<suffix_fa></suffix_fa>
	<email>hjoneidi@ut.ac.ir</email>
	<code>10031947532846009473</code>
	<orcid>0009-0007-2753-3738</orcid>
	<coreauthor>Yes
</coreauthor>
	<affiliation>Faculty of Natural Resources, University of Tehran, Tehran, Iran</affiliation>
	<affiliation_fa>دانشکده منابع طبیعی دانشگاه تهران، تهران</affiliation_fa>
	 </author>


	<author>
	<first_name>Elham</first_name>
	<middle_name></middle_name>
	<last_name>Bazgir</last_name>
	<suffix></suffix>
	<first_name_fa>الهام</first_name_fa>
	<middle_name_fa></middle_name_fa>
	<last_name_fa>بازگیر</last_name_fa>
	<suffix_fa></suffix_fa>
	<email>elhambazgir136464@gmail.com</email>
	<code>10031947532846009474</code>
	<orcid>0009-0002-6745-670X</orcid>
	<coreauthor>No</coreauthor>
	<affiliation>University of Kurdistan, Sanandaj, Iran</affiliation>
	<affiliation_fa>دانشگاه کردستان، سنندج</affiliation_fa>
	 </author>


	<author>
	<first_name>Nadia</first_name>
	<middle_name></middle_name>
	<last_name>Kamali</last_name>
	<suffix></suffix>
	<first_name_fa>نادیا</first_name_fa>
	<middle_name_fa></middle_name_fa>
	<last_name_fa>کمالی</last_name_fa>
	<suffix_fa></suffix_fa>
	<email>kamalinadia1982@gmail.com</email>
	<code>10031947532846009475</code>
	<orcid>10031947532846009475</orcid>
	<coreauthor>No</coreauthor>
	<affiliation>Rangeland Research Division, Research Institute of Forests and Rangelands, Agricultural Research Education and Extension Organization (AREEO), Tehran, Iran</affiliation>
	<affiliation_fa>بخش تحقیقات مرتع، مؤسسه تحقیقات جنگل‌ها و مراتع کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، تهران</affiliation_fa>
	 </author>


</author_list>


	</article>
</articleset>
</journal>
