<?xml version="1.0" encoding="utf-8"?>
<journal>
<title>Iranian Scientific Fisheries Journal</title>
<title_fa>مجله علمي شيلات ايران</title_fa>
<short_title>isfj</short_title>
<subject>Agriculture</subject>
<web_url>http://isfj.ir</web_url>
<journal_hbi_system_id>1</journal_hbi_system_id>
<journal_hbi_system_user>admin</journal_hbi_system_user>
<journal_id_issn>1026-1354</journal_id_issn>
<journal_id_issn_online>2322-5998</journal_id_issn_online>
<journal_id_pii></journal_id_pii>
<journal_id_doi>10.18869/acadpub.isfj</journal_id_doi>
<journal_id_iranmedex></journal_id_iranmedex>
<journal_id_magiran></journal_id_magiran>
<journal_id_sid>000000</journal_id_sid>
<journal_id_nlai>000000</journal_id_nlai>
<journal_id_science>000000</journal_id_science>
<language>fa</language>
<pubdate>
	<type>jalali</type>
	<year>1404</year>
	<month>5</month>
	<day>1</day>
</pubdate>
<pubdate>
	<type>gregorian</type>
	<year>2025</year>
	<month>8</month>
	<day>1</day>
</pubdate>
<volume>34</volume>
<number>4</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>مقاله علمی – پژوهشی:‌ پایش میکروبی منابع آب سطحی در حوضه آبریز سرشاخه‌های رودخانه سیروان (سنندج) طی سال‌های 1403-1402</title_fa>
	<title>Microbial monitoring of surface water resources in the Sirvan River tributary catchment basin (Sanandaj) during 2023-2024</title>
	<subject_fa>آلودگي محيطهاي آبي</subject_fa>
	<subject>آلودگي محيطهاي آبي</subject>
	<content_type_fa>پژوهشي</content_type_fa>
	<content_type>Research</content_type>
	<abstract_fa>&lt;span style=&quot;font-size:11pt&quot;&gt;&lt;span style=&quot;line-height:75%&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 style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;پایش میکروبی منابع آب سطحی به&#8204;ویژه در نواحی حساس مانند حوضه&#8204;های آبریز سدها، نقش حیاتی در حفظ سلامت عمومی و پایداری اکوسیستم&#8204;های آبی ایفاء می&#8204;کند. این مطالعه با هدف بررسی وضعیت آلودگی میکروبی در حوضه آبریز رودخانه سیروان در استان کردستان طی سال&#8204;های آبی 1403-1402 انجام شد. نمونه&#8204;برداری&#8204;ها به &#8204;صورت ماهانه و با رعایت شرایط استریل از شش ایستگاه منتخب شامل ایستگاه 1 (بالادست قشلاق، زیر پل)، ایستگاه 2 (شاخه قشلاق رود قبل از تصفیه خانه)، ایستگاه 3 (شاخه قشلاق رود، پایین دست تصفیه خانه)، ایستگاه 4 (شاخه قشلاق رود، حدود 3 کیلومتر پایین&#8204;تر از ایستگاه 2)، ایستگاه 5 (شاخه گاوه رود) و ایستگاه 6 (شاخه سیروان، پشت سد) انجام گرفت. شاخص&#8204;های میکروبی شامل شمارش کل باکتری&#8204;ها، کلیفرم&#8204;های کل، کلیفرم&#8204;های مدفوعی و &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;i&gt;&amp;nbsp;&lt;/i&gt;&lt;i&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Escherichia&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/i&gt;&lt;i&gt; &lt;/i&gt;&lt;i&gt;&lt;span dir=&quot;LTR&quot; style=&quot;color:black&quot;&gt;coli&lt;/span&gt;&lt;/i&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;با استفاده از محیط&#8204;های کشت پلیت کانت آگار و&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; ECC &lt;/span&gt;&lt;/span&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;کروم آگار مطابق با استاندارد&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; APHA &lt;/span&gt;&lt;/span&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&amp;nbsp;(2017) اندازه&#8204;گیری شدند&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;.&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; نتایج نشان داد که بار میکروبی در ایستگاه&#8204;ها تفاوت معنی&#8204;داری دارد&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; (05/0&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;i&gt;&lt;span dir=&quot;LTR&quot; style=&quot;color:black&quot;&gt;p&lt;/span&gt;&lt;/i&gt;&lt;span dir=&quot;LTR&quot; style=&quot;color:black&quot;&gt;&amp;le;&lt;/span&gt;&lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;)&lt;span style=&quot;background:white&quot;&gt; به&#8204;طوری&#8204;که ایستگاه ۴، واقع در پایین&#8204;دست تصفیه&#8204;خانه، دارای بیشترین میزان آلودگی بود و در ماه آبان غلظت کلیفرم&#8204;های کل تا ۷۰۰۰۰۰&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt; &lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;واحد تشکیل&#8204;دهنده کلنی در 100 میلی&#8204;&#8204;لیتر&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt; &lt;span lang=&quot;FA&quot; style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;ثبت شد. در مقابل، ایستگاه ۵ واقع در منطقه&#8204;ای با کمترین فعالیت انسانی، دارای کمترین بار میکروبی بود. تحلیل فصلی داده&#8204;ها نیز بیانگر افزایش قابل&#8204;ملاحظه شاخص&#8204;های آلودگی در فصل تابستان به&#8204;ویژه در ایستگاه&#8204;های مجاور فعالیت&#8204;های انسانی و کشاورزی بود&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;.&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:12.0pt&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span style=&quot;line-height:75%&quot;&gt;&lt;span b=&quot;&quot; compset=&quot;&quot; style=&quot;font-family:&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; یافته&#8204;های این تحقیق نشان&#8204;دهنده نقش مؤثر فاضلاب&#8204;های انسانی، رواناب&#8204;های کشاورزی و ناکارآمدی سیستم&#8204;های تصفیه در کاهش کیفیت بهداشتی منابع آب سطحی منطقه است. با توجه به اهمیت رودخانه سیروان در تأمین آب شرب و کشاورزی استان کردستان، نتایج این مطالعه می&#8204;تواند مبنایی برای شناسایی نقاط بحرانی، اصلاح زیرساخت&#8204;های تصفیه و تدوین برنامه&#8204;های پایش و مدیریت مستمر کیفیت آب سطحی در سطح حوضه آبریز باشد&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span dir=&quot;LTR&quot; style=&quot;background:white&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;</abstract_fa>
	<abstract>&lt;span style=&quot;font-size:11pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span style=&quot;tab-stops:right 9.0pt 14.4pt 18.0pt 27.0pt&quot;&gt;&lt;span style=&quot;text-autospace:none&quot;&gt;&lt;span style=&quot;font-family:Calibri,sans-serif&quot;&gt;&lt;b&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Introduction&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;
&lt;h3 style=&quot;text-align:justify&quot;&gt;&lt;span style=&quot;font-size:13.5pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-weight:bold&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt;The Sirvan River is a vital freshwater source in Kurdistan Province, flowing through both urban and rural landscapes. Its proximity to human settlements, agricultural zones, and livestock operations increases the risk of contamination from untreated wastewater and surface runoff. Consequently, microbial monitoring of surface water within this watershed is essential for evaluating the region&amp;rsquo;s sanitary and environmental conditions. Microorganisms in aquatic ecosystems, beyond their ecological functions, are widely recognized as reliable indicators of water quality. Fluctuations in microbial populations often signal the presence of pollutants such as domestic sewage, animal waste, and nutrient compounds (Bradshaw &lt;i&gt;et al.,&lt;/i&gt; 2016). Among these indicators, coliform bacteria particularly fecal coliforms and &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;i&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;font-weight:normal&quot;&gt;Escherichia&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/i&gt;&lt;i&gt; &lt;/i&gt;&lt;i&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt;coli&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/i&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt; are of critical importance due to their intestinal origin and thermotolerance, making them precise markers of contamination from human and animal sources (Aenab and Singh, 2015). Numerous international studies have explored the factors influencing the presence and distribution of indicator bacteria in surface waters. For example, Pall &lt;i&gt;et al.&lt;/i&gt; (2013) and Islam &lt;i&gt;et al&lt;/i&gt;. (2017) examined the roles of temperature, precipitation, land use, and wastewater treatment efficiency in microbial load variation. Newton and McMahon (2011) investigated the relationship between organic and inorganic compounds and microbial community structure in lakes. At the watershed scale, &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt;Flood&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt; &lt;i&gt;et al.&lt;/i&gt; (2022) highlighted the influence of geological and hydrological features on microbial contamination in rivers. Similarly, Park &lt;i&gt;et al.&lt;/i&gt; (2021) demonstrated the impact of vegetation cover and land slope on bacterial distribution in South Korea. In Iran, several studies have addressed microbial water quality. Roshani-Sefidkouhi &lt;i&gt;et al&lt;/i&gt;. (2025) assessed the Chahnimeh reservoirs in Sistan and Baluchestan Province, while Khatib Haghighi and Ghaani (2018) evaluated urban and rural drinking water sources in Gilan Province using total and fecal coliform indicators. However, most of these investigations were limited to cross-sectional designs or specific seasons. Comprehensive studies on spatial and seasonal variations of microbial indicators in Iranian rivers particularly the Sirvan River remain scarce. This study presents a year-long monitoring of microbial indicators, including total coliforms, fecal coliforms, and &lt;i&gt;E. coli&lt;/i&gt;, across six stations in the Sirvan River watershed, covering a full hydrological cycle (July 2023 to June 2024). By analyzing seasonal and spatial trends and examining the influence of surrounding human activities, this research offers a novel approach to surface water quality assessment. The findings aim to identify pollution hotspots, evaluate sanitary conditions, and inform water quality management strategies for Kurdistan Province and similar regions.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/h3&gt;
&lt;span style=&quot;font-size:11pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span style=&quot;tab-stops:right 9.0pt 14.4pt 18.0pt 27.0pt&quot;&gt;&lt;span style=&quot;text-autospace:none&quot;&gt;&lt;span style=&quot;font-family:Calibri,sans-serif&quot;&gt;&lt;b&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Results&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/b&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&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:11pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span style=&quot;tab-stops:right 9.0pt 14.4pt 18.0pt 27.0pt&quot;&gt;&lt;span style=&quot;text-autospace:none&quot;&gt;&lt;span style=&quot;font-family:Calibri,sans-serif&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Microbial contamination in the Sirvan River watershed was assessed by quantifying total bacteria, total coliforms, fecal coliforms, and &lt;i&gt;E. coli&lt;/i&gt; across multiple stations and seasons during 2023&amp;ndash;2024. Maximum recorded values were 1&amp;times;10⁸ CFU/100 ml for total bacteria, 7&amp;times;10⁵ for total coliforms, 4.2&amp;times;10⁵ for fecal coliforms, and 3.7&amp;times;10⁵ for &lt;i&gt;E. coli&lt;/i&gt;. The highest total bacterial count occurred at Station 2 in November 2023, while peak coliform and &lt;i&gt;E. coli&lt;/i&gt; levels were observed at Station 4 in January 2024.&lt;/span&gt;&lt;/span&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; Seasonal analysis revealed that bacterial concentrations peaked in summer (6.56 &amp;plusmn; 0.32 log CFU/100 ml) and were lowest in winter (5.55 &amp;plusmn; 0.87 log CFU/100 ml). Spatially, Station 3 consistently exhibited the highest bacterial load, while Station 2 had the lowest. Statistically significant differences were found between winter and other seasons (&lt;i&gt;p&lt;/i&gt;&amp;le;0.05), as well as among stations (&lt;i&gt;p&lt;/i&gt;&amp;le;0.05). Total coliforms followed a similar seasonal pattern, with highest mean counts in summer (4.87&amp;plusmn;0.77 log CFU/100 ml), followed by autumn (4.27&amp;plusmn;0.95), spring (3.86&amp;plusmn;0.50), and winter (3.12&amp;plusmn;1.91). Stations 3 and 4 were the most contaminated, while Stations 1 and 5 consistently showed the lowest levels. Seasonal variation in total coliforms was statistically significant (&lt;i&gt;p&lt;/i&gt;&amp;le;0.05), with summer values markedly higher than winter. Fecal coliforms also peaked in summer (3.23&amp;plusmn;1.72 log CFU/100 ml) and were lowest in winter (2.72&amp;plusmn;1.72). Station 4 recorded the highest levels, significantly differing from other stations (&lt;i&gt;p&lt;/i&gt;&amp;le;0.05), while Stations 1 and 5 had the lowest. However, seasonal differences in fecal coliforms were not statistically significant. &lt;i&gt;E. coli&lt;/i&gt; concentrations were highest in summer (3.09&amp;plusmn;1.58 log CFU/100 ml) and lowest in winter (2.97&amp;plusmn;1.51). Stations 3 and 4 again showed the highest contamination, with statistically significant differences compared to other stations (&lt;i&gt;p&lt;/i&gt;&amp;le;0.05). Stations 1 and 5 did not show significant contamination levels. Seasonal variation in &lt;i&gt;E. coli&lt;/i&gt; density was not statistically significant. Overall, the data revealed pronounced spatial heterogeneity in microbial contamination, with consistently elevated levels at Stations 3 and 4 areas characterized by intensive human and agricultural activity. Seasonal effects, particularly during summer and autumn, were major contributors to increased bacterial loads due to higher temperatures and runoff. These findings underscore the need for targeted pollution control measures in identified hotspots within the Sirvan River catchment.&lt;/span&gt;&lt;/span&gt;&lt;b&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;/span&gt;&lt;/b&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;

&lt;h3 style=&quot;text-align:justify&quot;&gt;&lt;span style=&quot;font-size:13.5pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-weight:bold&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;Discussion and conclusion&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&amp;nbsp; &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/h3&gt;

&lt;h3 style=&quot;text-align:justify&quot;&gt;&lt;span style=&quot;font-size:13.5pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-weight:bold&quot;&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;&lt;span style=&quot;font-weight:normal&quot;&gt;The elevated bacterial concentrations observed in downstream stations (2, 3, and 4) of the Sirvan River reflect the impact of human activities, including the discharge of untreated or partially treated sewage and agricultural runoff (Helmer and Hespanhol, 1997; Agarwal and Rajwar, 2010; Aenab and Singh, 2015). These conditions are exacerbated by warm water temperatures, reduced flow rates, increased evaporation, and higher pollutant loads factors consistent with microbial contamination patterns in similar ecosystems (Rusi&amp;ntilde;ol &lt;i&gt;et al&lt;/i&gt;., 2020; Rather &lt;i&gt;et al&lt;/i&gt;., 2023; Al-Afify &lt;i&gt;et al&lt;/i&gt;., 2023). The presence of &lt;i&gt;E. coli&lt;/i&gt; in elevated concentrations is a clear indicator of fecal contamination and poses serious health risks to communities near the river. The findings highlight the inadequacy of existing wastewater treatment systems and the urgent need for infrastructure upgrades to mitigate pollution. Lower bacterial concentrations at upstream sites suggest the effectiveness of natural filtration by vegetation, topographical separation from pollution sources, and hydrological buffering (Yaghoubzadeh and Safari, 2016; Wang &lt;i&gt;et al.,&lt;/i&gt; 2022). This study reinforces the importance of regular microbial water quality monitoring in the Sirvan River watershed using robust indicators such as &lt;i&gt;E. coli&lt;/i&gt;. Effective management requires prioritizing the identification and control of both point and non-point source pollution, especially during peak contamination seasons. Strategies should include improved wastewater treatment, public awareness campaigns, and ecological restoration of water bodies. Integrated watershed management, supported by collaboration among water, health, and environmental authorities, is essential for safeguarding water quality and public health.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/h3&gt;

&lt;h3 style=&quot;text-align:justify&quot;&gt;&lt;span style=&quot;font-size:13.5pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;font-weight:bold&quot;&gt;&lt;strong&gt;&lt;span style=&quot;font-size:11.0pt&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Conflict of interest&lt;/span&gt;&lt;/span&gt;&lt;/strong&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/h3&gt;
&lt;span style=&quot;font-size:12pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&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;color:black&quot;&gt;The authors declare that they have no conflict of interest&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;br&gt;
&lt;span style=&quot;font-size:11pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span style=&quot;tab-stops:right 9.0pt 14.4pt 18.0pt 27.0pt&quot;&gt;&lt;span style=&quot;text-autospace:none&quot;&gt;&lt;span style=&quot;font-family:Calibri,sans-serif&quot;&gt;&lt;b&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Acknowledgment&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/b&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:11pt&quot;&gt;&lt;span style=&quot;line-height:17.0pt&quot;&gt;&lt;span style=&quot;tab-stops:right 9.0pt 14.4pt 18.0pt 27.0pt&quot;&gt;&lt;span style=&quot;text-autospace:none&quot;&gt;&lt;span style=&quot;font-family:Calibri,sans-serif&quot;&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;We hereby sincerely thank the &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Caspian Sea Ecology Research Center&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; and &lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt;Iranian Fisheries Science Research Institute&lt;/span&gt;&lt;/span&gt;&lt;span style=&quot;background:white&quot;&gt;&lt;span new=&quot;&quot; roman=&quot;&quot; style=&quot;font-family:&quot; times=&quot;&quot;&gt;&lt;span style=&quot;color:black&quot;&gt; for providing the scientific and laboratory basis for this research.&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;&lt;/span&gt;</abstract>
	<keyword_fa>پایش میکروبی, کلیفرم مدفوعی, Escherichia coli, رودخانه سیروان, کیفیت آب</keyword_fa>
	<keyword>Microbial monitoring, fecal coliform, Escherichia coli, Sirvan River, water quality</keyword>
	<start_page>69</start_page>
	<end_page>81</end_page>
	<web_url>http://isfj.ir/browse.php?a_code=A-10-1386-13&amp;slc_lang=fa&amp;sid=1</web_url>


<author_list>
	<author>
	<first_name>zahra</first_name>
	<middle_name></middle_name>
	<last_name>yaghoubzadeh</last_name>
	<suffix></suffix>
	<first_name_fa>زهرا</first_name_fa>
	<middle_name_fa></middle_name_fa>
	<last_name_fa>یعقوب زاده</last_name_fa>
	<suffix_fa></suffix_fa>
	<email>za_yaghoub@yahoo.com</email>
	<code>100319475328460040964</code>
	<orcid>100319475328460040964</orcid>
	<coreauthor>Yes
</coreauthor>
	<affiliation>Agricultural Research, Education and Extension Organization</affiliation>
	<affiliation_fa>پژوهشکده اکولوژی دریای خزر، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، ساری، ایران</affiliation_fa>
	 </author>


	<author>
	<first_name>Faezeh</first_name>
	<middle_name></middle_name>
	<last_name>Turk Pahnabi</last_name>
	<suffix></suffix>
	<first_name_fa>فائزه</first_name_fa>
	<middle_name_fa></middle_name_fa>
	<last_name_fa>ترک پهنابی</last_name_fa>
	<suffix_fa></suffix_fa>
	<email>pahnabifaezeh@gmail.com</email>
	<code>100319475328460040965</code>
	<orcid>100319475328460040965</orcid>
	<coreauthor>No</coreauthor>
	<affiliation>Agricultural Research, Education and Extension Organization</affiliation>
	<affiliation_fa>پژوهشکده اکولوژی دریای خزر، مؤسسه تحقیقات علوم شیلاتی کشور، سازمان تحقیقات، آموزش و ترویج کشاورزی، ساری، ایران</affiliation_fa>
	 </author>


</author_list>


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