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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Water</journal-id>
<journal-title-group>
<journal-title>Frontiers in Water</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Water</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2624-9375</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/frwa.2025.1755117</article-id>
<article-version article-version-type="Version of Record" vocab="NISO-RP-8-2008"/>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Impact of spatio-temporal variations and altitudinal gradient on bacterial dynamics along the Eastern Himalayan river Teesta</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Chettri</surname>
<given-names>Upashna</given-names>
</name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/3273176"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Das</surname>
<given-names>Santanu</given-names>
</name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Chakrabarty</surname>
<given-names>Tapan Kumar</given-names>
</name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
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</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Joshi</surname>
<given-names>Santa Ram</given-names>
</name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
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<aff id="aff1"><label>1</label><institution>Department of Botany, The Assam Royal Global University</institution>, <city>Guwahati</city>, <state>Assam</state>, <country country="in">India</country></aff>
<aff id="aff2"><label>2</label><institution>Molecular Biology and Microbial Biotechnology Laboratory, Division of Life Sciences, Institute of Advanced Study in Science and Technology (IASST)</institution>, <city>Guwahati</city>, <state>Assam</state>, <country country="in">India</country></aff>
<aff id="aff3"><label>3</label><institution>Department of Statistics, North-Eastern Hill University</institution>, <city>Shillong</city>, <state>Meghalaya</state>, <country country="in">India</country></aff>
<aff id="aff4"><label>4</label><institution>Department of Biotechnology and Bioinformatics, North-Eastern Hill University</institution>, <city>Shillong</city>, <state>Meghalaya</state>, <country country="in">India</country></aff>
<author-notes>
<corresp id="c001"><label>&#x002A;</label>Correspondence: Santa Ram Joshi, <email xlink:href="mailto:srjoshi@gmail.com">srjoshi2006@gmail.com</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-03-02">
<day>02</day>
<month>03</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2025</year>
</pub-date>
<volume>7</volume>
<elocation-id>1755117</elocation-id>
<history>
<date date-type="received">
<day>26</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>23</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>29</day>
<month>12</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2026 Chettri, Das, Chakrabarty and Joshi.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Chettri, Das, Chakrabarty and Joshi</copyright-holder>
<license>
<ali:license_ref start_date="2026-03-02">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</license-p>
</license>
</permissions>
<abstract>
<p>Teesta, an Eastern Himalayan River is an important lifeline of the state of Sikkim and parts of West Bengal. However, the river is under the influence of human activities and hydrological disturbances. Microbes are sensitive to environmental changes which make them indicators of pollution, nutrient load, heavy metal and ecological disturbances. This study investigated spatial and temporal variations in bacterial communities along the altitudinal gradient of the Teesta River using 16S metabarcoding of water and sediment samples. Multivariate analyses were used to assess seasonal shifts and the influence of physicochemical factors on microbial community structure. Our study revealed that bacterial species richness significantly varied across the sites along the river gradient but bacterial composition was less influenced by the sites, seasons and sample type. While dominant phyla remain consistent across samples, season-driven shifts and niche preferences such as winter enrichment of Actinobacteriota and LEfSe-identified genus-level biomarkers highlight the ecological heterogeneity and functional diversification of riverine microbial communities. Altitude and heavy metal lead (Pb) was found to strongly influence on occurrence of bacterial phyla like Proteobacteria, Chloroflexota, Acidobacteriota, and Actinobacteriota. Whereas, environmental parameters like pH, temperature, alkalinity and dissolved oxygen exhibited the most significant association with major bacterial phyla. The Teesta River displayed distinct taxonomic signatures in water and sediment, particularly at the genus level that is strongly shaped by both seasonal dynamics and habitat-specific conditions. Our findings offer valuable insights on how seasonal shifts and habitat-specific conditions within the Teesta River shape bacterial community structure and composition with significant implications in predicting ecosystem responses to environmental change in an Eastern Himalayan river system.</p>
</abstract>
<kwd-group>
<kwd>altitudinal gradient</kwd>
<kwd>anthropogenic impact</kwd>
<kwd>bacterial diversity</kwd>
<kwd>Himalayan river ecology</kwd>
<kwd>next generation sequencing</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was not received for this work and/or its publication.</funding-statement>
</funding-group>
<counts>
<fig-count count="8"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="44"/>
<page-count count="12"/>
<word-count count="7298"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Environmental Water Quality</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="sec1">
<label>1</label>
<title>Introduction</title>
<p>The Teesta River, originating from the pristine glaciers of the Eastern Himalayas, is a vital freshwater resource for the Sikkim region, sustaining diverse ecosystems and local livelihoods. The flow of the river is sustained by glacial melt, rainfall, and snowmelt, with glaciers contributing significantly to its discharge. Seasonal variations in its isotopic composition reveal its reliance on diverse moisture sources, offering valuable insights into its hydrological behavior (<xref ref-type="bibr" rid="ref18">Kumar Mondal et al., 2023</xref>). However, pollution poses a major challenge, particularly in downstream areas, where heavy metal contamination from industrial and urban sources has exceeded safe limits for cadmium, chromium, lead, and zinc. The heavy metal risk assessment indices indicate that, while upstream waters remain relatively unpolluted, downstream sections experience moderate to high pollution levels, primarily due to human activities (<xref ref-type="bibr" rid="ref5">Chettri et al., 2022</xref>). Given its significance as a freshwater resource and its role in supporting biodiversity, human livelihoods, and ecosystem services, understanding the health and functioning of the Teesta River is of paramount importance.</p>
<p>Microbial communities play a fundamental role in maintaining river ecosystem health by driving biogeochemical cycles, regulating nutrient fluxes, and contributing to self-purification processes (<xref ref-type="bibr" rid="ref25">Ouyang et al., 2020</xref>). While some bacteria serve as bioindicators of pollution, others facilitate the degradation of contaminants, including heavy metals and organic pollutants (<xref ref-type="bibr" rid="ref13">Hong and Gu, 2009</xref>; <xref ref-type="bibr" rid="ref33">Sohn et al., 2004</xref>). However, anthropogenic activities alter river hydrology and physicochemical parameters, leading to shifts in microbial community composition and the influx of allochthonous microorganisms (<xref ref-type="bibr" rid="ref30">Reddy and Dubey, 2021</xref>). Furthermore, hydrological dynamics, including flow rate, sediment transport, and water residence time, play a crucial role in shaping riverine microbial communities. Variations in flow patterns influence microbial dispersal and resource availability, while sediment transport introduces new taxa downstream. Water residence time affects community turnover by regulating organic matter accumulation. Seasonal changes in temperature and precipitation further alter microbial diversity, composition, and metabolic activity, suggesting the adaptive and dynamic nature of the river microbiome (<xref ref-type="bibr" rid="ref4">Chaturvedi et al., 2024</xref>). Therefore, understanding microbial dynamics is crucial for evaluating the resilience of riverine ecosystems to environmental stressors.</p>
<p>Traditional culture-based methods provide only limited insights into microbial diversity, as they fail to capture the vast array of non-culturable microorganisms in complex aquatic habitats such as the Teesta River. The advent of a culture-independent approach has revolutionized microbial ecology by enabling comprehensive taxonomic analysis through direct DNA sequencing of environmental samples (<xref ref-type="bibr" rid="ref15">Hugenholtz and Tyson, 2008</xref>; <xref ref-type="bibr" rid="ref37">Valverde and Mellado, 2013</xref>). This approach has been instrumental in uncovering the profound impact of human activities on riverine microbial communities, revealing shifts in bacterial abundance and diversity in response to pollution (<xref ref-type="bibr" rid="ref22">Marti et al., 2013</xref>; <xref ref-type="bibr" rid="ref38">Wang et al., 2018</xref>).</p>
<p>In the context of the Teesta River, assessing microbial ecology is particularly crucial due to its exposure to multiple contamination sources, including heavy metals. Previous studies have demonstrated that heavy metal pollution can significantly alter bacterial composition and metabolic functions, leading to cascading effects on ecosystem health (<xref ref-type="bibr" rid="ref40">Zhuang et al., 2019</xref>; <xref ref-type="bibr" rid="ref19">Li et al., 2020</xref>). However, microbial responses to such stressors can be complex, with some studies reporting minimal changes in bacterial abundance despite high heavy metal concentrations (<xref ref-type="bibr" rid="ref12">Guo et al., 2019</xref>). Given the critical role of microbial communities in maintaining ecosystem stability, investigating their response to heavy metals and other pollutants is essential for safeguarding the Teesta River&#x2019;s ecological balance.</p>
<p>This study uses Illumina HiSeq 16S rRNA sequencing to analyze and compare bacterial communities in surface water and sediment samples from the Teesta River. By assessing spatial and temporal variations in bacterial composition, with a focus on non-culturable microbes, this research provides a comprehensive perspective on microbial diversity along an altitudinal gradient. Additionally, the study evaluates the influence of heavy metals on microbial structure and function in both water and sediment samples. To our knowledge, this study represents the first large-scale investigation of the Teesta River&#x2019;s microbial communities, offering critical insights into their ecological structure and response to variations in riverine environmental conditions.</p>
<p>Given the Teesta River&#x2019;s ecological and socioeconomic significance, understanding its microbial dynamics is essential for monitoring pollution impacts and informing conservation efforts. Integrating advanced molecular techniques into environmental assessments can help identify key microbial indicators of pollution, evaluate anthropogenic effects, and guide restoration initiatives. Such efforts are crucial to ensuring the long-term health and sustainability of the Teesta River and the communities that depend on it.</p>
</sec>
<sec sec-type="materials|methods" id="sec2">
<label>2</label>
<title>Materials and methods</title>
<sec id="sec3">
<label>2.1</label>
<title>Study area and sample collection</title>
<p>Teesta, an Eastern Himalayan river, originates from Cho Lhamu Lake (28&#x00B0; 01&#x2032;7.8672&#x201D; N, 88&#x00B0; 45&#x2032;30.456&#x2033;E), situated at an elevation of 7,068&#x202F;m in the Eastern Himalayas. The river, largely fed by glaciers, seasonal rain, and tributaries, has a total catchment area of 12,159 km<sup>2</sup> [<xref ref-type="bibr" rid="ref9">Environmental Information System (ENVIS), 2019</xref>]. Starting from late March, the melting of the snow in the Himalayas leads to gradual rise in river water. Maximum flow occurs between July and September due to heavy rainfall in monsoon and the flow decreases from October to April (<xref ref-type="bibr" rid="ref8">Chowdhury, 2010</xref>; <xref ref-type="bibr" rid="ref24">Mullick et al., 2013</xref>). The Teesta River, as it approaches the border between Sikkim and West Bengal, becomes wide and finally joins the Brahmaputra in Bangladesh. Along its course through Sikkim and North Bengal, the river is influenced by various human interventions.</p>
<p>Rapid economic development in Sikkim has increased environmental risk, particularly to river ecosystems. Significant problems, especially in the eco-sensitive Indian Himalayan region, are primarily due to the growing human population, industrialization, illegal mining, inefficient solid waste management, and indiscriminate waste dumping (<xref ref-type="bibr" rid="ref35">Thakur et al., 2021</xref>). Various industries in Sikkim&#x2014;including pharmaceutical companies, tourism-related businesses, food processing units, breweries, and cosmetics manufacturers&#x2014;are primarily located near the riverbanks. The river&#x2019;s steep gradients and swift flow make it a powerful source of hydroelectric energy, capable of generating thousands of megawatts of electricity. Currently, there are five hydroelectric projects along the river, distributed across the states of Sikkim and West Bengal (<xref ref-type="bibr" rid="ref28">Rahaman and Al Mamun, 2020</xref>). Rapid industrial growth has often resulted in the unchecked exploitation of the river, leading to the deterioration of its ecological health.</p>
<p>For the present study, surface water and sediment samples were collected from six sites (S1 to S6) along the river during the monsoon (August) and winter (February) seasons between 2018 and 2020. At each site, 500&#x202F;mL of water and 200&#x202F;g of sediment samples were collected and stored at 4&#x202F;&#x00B0;C. The sampling locations are detailed in <xref ref-type="supplementary-material" rid="SM1">Supplementary Table S1</xref> and <xref ref-type="fig" rid="fig1">Figure 1</xref>.</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Study area map shows the altitudinal gradient across sampling sites (ArcGIS version 10.8).</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g001.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Map depicting altitudinal gradients in the Darjeeling and Sikkim regions with labeled sites S1 to S6, rivers and streams marked in blue. The altitude ranges from under 500 meters (green) to over 7900 meters (red). Inset shows India's location, with a legend indicating boundaries and altitude categories. Coordinates are marked, and a scale bar indicates distance in kilometers.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec4">
<label>2.2</label>
<title>Total DNA extraction</title>
<p>Extraction of total DNA from the water and sediment samples was conducted using the DNeasy Power Water Kit and DNeasy Power Soil Kit (Qiagen USA), respectively, following the manufacturer&#x2019;s protocol. The quantification of the extracted DNA was estimated using Qubit Fluorimeter (v.3.0) Eugene, Oregon, USA.</p>
</sec>
<sec id="sec5">
<label>2.3</label>
<title>Amplification of the target gene and next-generation sequencing</title>
<p>The V3-V4 region of the 16S rRNA gene was amplified using the V3 forward primer (CCTACGGGNBGCASCAG) and V4 reverse primer (GACTACNVGGGTATCTAATCC). Approximately 5&#x202F;ng of the amplified product was used for library preparation using the NEBNext Ultra DNA Library Preparation Kit. Library quality and concentration were assessed using an Agilent 2200 TapeStation, and sequencing was performed on the Illumina HiSeq 2500 platform.</p>
</sec>
<sec id="sec6">
<label>2.4</label>
<title>Analysis of the amplicon dataset</title>
<p>The paired-end reads generated from Illumina sequencing were processed using the LotuS2 pipeline (<xref ref-type="bibr" rid="ref26">&#x00D6;zkurt et al., 2022</xref>), with certain modifications to the default parameters as previously described by <xref ref-type="bibr" rid="ref2">Bhaskar et al. (2023)</xref>. The sequences were clustered into Amplicon Sequence Variants (ASVs) using the DADA2 algorithm within LotuS2 (<xref ref-type="bibr" rid="ref3">Callahan et al., 2016</xref>). Taxonomic assignment of the ASVs was carried out by aligning with Lambda against the SILVA 138.1 database (<xref ref-type="bibr" rid="ref27">Quast et al., 2012</xref>). For the removal of sequencing primers, the forward primer and reverse primer options in the LotuS2 pipeline were used. Out of 11,975,865 total reads, 8,549,296 reads (71.38%) were classified as &#x201C;high-quality&#x201D; and retained for downstream analyses. A total of 16,705 ASVs were generated from these high-quality reads and retained for diversity and taxonomic analyses.</p>
<p>Downstream analyses of the amplicon data were performed in R (v 4.4.1) using the phyloseq and microeco packages (<xref ref-type="bibr" rid="ref20">Liu et al., 2021</xref>; <xref ref-type="bibr" rid="ref23">McMurdie and Holmes, 2013</xref>). For the calculation and estimation of the diversity indices, the vegan package (v 2.6&#x2013;8) was used.</p>
</sec>
<sec id="sec7">
<label>2.5</label>
<title>Statistical analysis</title>
<p>Statistical analyses were performed in R (v 4.4.1) using base functions and specialized packages. To calculate microbial diversity, samples were first rarefied to an even depth. Differential abundance and significance testing were performed using the Kruskal&#x2013;Wallis H test followed by the Wilcoxon rank-sum test. Correlations between the microbiota and the physicochemical parameters were assessed using Spearman&#x2019;s and Mantel correlations. In brief, the normalized abundance of the microbiome was compared against the counts of the physicochemical parameters. Correlation calculations were performed in R using the correlations and &#x201C;ggcor packages&#x201D;.</p>
</sec>
</sec>
<sec sec-type="results" id="sec8">
<label>3</label>
<title>Results</title>
<p>The present study investigated altitudinal and seasonal variations in bacterial communities and examined the relationships between these communities and physicochemical parameters, including heavy metal concentrations, across various sites along the Teesta River.</p>
<sec id="sec9">
<label>3.1</label>
<title>Changes in microbial richness along the altitudinal gradient of the Teesta river</title>
<p>Alpha diversity, which measures the diversity and richness within a sample, was evaluated using two indices: the Shannon Index and Chao1, representing species diversity and species richness, respectively (<xref ref-type="fig" rid="fig2">Figures 2A</xref>&#x2013;<xref ref-type="fig" rid="fig2">D</xref>). In general, we observed that species diversity significantly increased (<italic>p</italic>&#x202F;=&#x202F;0.055) during the winter season within the sediment samples, highlighting the role of seasonal variance in shaping the microbial diversity of a river ecosystem (<xref ref-type="fig" rid="fig2">Figure 2A</xref>). Although diversity was elevated during winters, we observed a marginal reduction (<italic>p&#x202F;=</italic> 0.07) in species richness within the water samples (<xref ref-type="fig" rid="fig2">Figure 2D</xref>). However, we did not observe any variance in the alpha-diversity between water and sediment samples, thereby indicating a uniform diversity among water and sediment samples within the same river (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S1</xref>). Since the samples were collected from various sites across the altitudinal gradient of the Teesta River, we evaluated the changes in alpha diversity across the sites using four parameters (Shannon and Simpson for diversity; Chao1 and Observed OTUs for richness). Interestingly, we observed that, despite a similar diversity, richness varies across the different sites (Chao1 <italic>p</italic>&#x202F;=&#x202F;0.026; Observed OTUs <italic>p</italic>&#x202F;=&#x202F;0.044) (<xref ref-type="fig" rid="fig3">Figure 3</xref>). Finally, we created a linear model to evaluate the contribution of each of the parameters, namely seasons, sites, sample type (water and sediment), and elevation, to the overall alpha diversity. As observed earlier, sites (ANOVA Chao1 <italic>p</italic>&#x202F;=&#x202F;0.008129; Observed OTUs <italic>p</italic>&#x202F;=&#x202F;0.004) had the largest overall impact only on the microbial richness of the Teesta River (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S2</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Alpha diversity variation in water and sediment samples according to seasons: <bold>(A)</bold> Shannon diversity in sediment samples, <bold>(B)</bold> Chao1 in sediment samples, <bold>(C)</bold> Shannon diversity in water samples, and <bold>(D)</bold> Chao1 in water samples.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g002.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Four panel plot comparing environmental diversity indices between monsoon and winter seasons. Panel A shows Shannon Diversity (Sediment) with p=0.055; Panel B, Chao1 (Sediment) with p=0.34; Panel C, Shannon Diversity (Water) with p=0.26; Panel D, Chao1 (Water) with p=0.078. Monsoon season is in red and winter in blue.</alt-text>
</graphic>
</fig>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Variation in alpha diversity across the sites, irrespective of sample type (sediment or water).</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g003.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Four violin plots comparing microbial diversity metrics across sites S1 to S6. The top left plot shows Shannon Diversity with a p-value of 0.31. The top right plot shows Chao1 Richness with a p-value of 0.026, indicating a significant difference. The bottom left plot shows Observed OTUs with a p-value of 0.044, also indicating significance. The bottom right plot shows the Simpson Index with a p-value of 0.5.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec10">
<label>3.2</label>
<title>The microbial composition is heavily influenced by seasonal variations and the ecological niche</title>
<p>The compositional diversity, the beta diversity, was evaluated considering Bray&#x2013;Curtis and weighted UniFrac (phylogenetic-based) distances. The variation in compositional diversity was plotted as PCoA plots. For the Bray&#x2013;Curtis-based PCoA plot, the axes were separated by 18.9 and 15.7%, respectively. However, the weighted UniFrac-based plot had higher variation in the axes with 66.2 and 11.2%, respectively (<xref ref-type="fig" rid="fig4">Figures 4A</xref>,<xref ref-type="fig" rid="fig4">B</xref>). Although the variation in sample collection sites had the largest overall impact on the microbial richness, we did not observe any such significant contribution in the compositional diversity (Bray&#x2013;Curtis R<sup>2</sup>&#x202F;=&#x202F;0.2151, <italic>p</italic>&#x202F;=&#x202F;0.502; weighted UniFrac R<sup>2</sup>&#x202F;=&#x202F;0.198, <italic>p</italic>&#x202F;=&#x202F;0.504). This finding highlights that, even though microbial richness varied among the sites, the overall community composition remained stable, indicating the resilience of the microbial community. However, by combining the sample variation, we were able to detect a slight variation in the Bray&#x2013;Curtis-based distance matrix (R<sup>2</sup>&#x202F;=&#x202F;0.35736, <italic>p</italic>&#x202F;=&#x202F;0.01), which diminished while considering the phylogeny in weighted UniFrac (R<sup>2</sup>&#x202F;=&#x202F;0.31165, <italic>p</italic>&#x202F;=&#x202F;0.205). Contrary to site-specific variation, seasonal changes significantly influenced microbial composition, although the variation was subtle (Bray&#x2013;Curtis R<sup>2</sup>&#x202F;=&#x202F;0.127, <italic>p</italic>&#x202F;=&#x202F;0.001); however, this effect was diminished when phylogenetic relationships were considered (weighted UniFrac R<sup>2</sup>&#x202F;=&#x202F;0.07808, <italic>p</italic>&#x202F;=&#x202F;0.157). Considering sample variations (water and sediments) along with the season, the variation is more pronounced in both Bray&#x2013;Curtis and weighted UniFrac (Bray&#x2013;Curtis R<sup>2</sup>&#x202F;=&#x202F;0.27, <italic>p</italic>&#x202F;=&#x202F;0.001; weighted UniFrac R<sup>2</sup>&#x202F;=&#x202F;0.19136, <italic>p</italic>&#x202F;=&#x202F;0.018). Elevation, represented by samples collected along the river gradient, also had a significant impact on niche-specific microbiomes (Bray&#x2013;Curtis R<sup>2</sup>&#x202F;=&#x202F;0.16224, <italic>p</italic>&#x202F;=&#x202F;0.002), though the strength of this association was reduced upon considering phylogenetic distance (weighted UniFrac R<sup>2</sup>&#x202F;=&#x202F;0.18449, <italic>p</italic>&#x202F;=&#x202F;0.062). Moreover, microbial composition shifts in elevation were accompanied by pronounced and significant compositional changes in both water and sediment microbiota (Bray&#x2013;Curtis R<sup>2</sup>&#x202F;=&#x202F;0.30499, <italic>p</italic>&#x202F;=&#x202F;0.001; weighted UniFrac R<sup>2</sup>&#x202F;=&#x202F;0.298, <italic>p</italic>&#x202F;=&#x202F;0.033).</p>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Beta diversity analysis. <bold>(A)</bold> PCoA plot based on the Bray&#x2013;Curtis distance matrix and <bold>(B)</bold> PCoA plot based on the weighted UniFrac-based distance matrix.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g004.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Two principal coordinate analysis (PCoA) plots with boxplots. Panel A shows a Weighted UniFrac PCoA with types: sediment (red) and water (blue), and sites represented by different shapes. Panel B shows a Bray-Curtis PCoA with similar sample types and sites. Blue and red ellipses represent data clusters. Boxplots indicate data distribution, with blue and red boxes reflecting water and sediment samples respectively. PERMANOVA results and significance values are included in both plots.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec11">
<label>3.3</label>
<title>Heavy metals and environmental parameters exert a crucial influence on the microbiome irrespective of the ecological niche</title>
<p>Environmental parameters, including heavy metals, play an important role in shaping microbial communities in a river ecosystem; therefore, we were interested in understanding environmental factors&#x2019; influence on the river microbiome. Previously collected data of environmental factors, such as the physicochemical parameters and heavy metals&#x2019; concentration, determined across the sites and seasons in the river, were used in this analysis (<xref ref-type="bibr" rid="ref6">Chettri and Joshi, 2022</xref>; <xref ref-type="bibr" rid="ref5">Chettri et al., 2022</xref>). In general, we observed a significant positive association between heavy metals and distance-based matrices (<italic>p(adj)</italic>&#x202F;=&#x202F;0.032), depicting the probable influence of the heavy metals in shaping the microbial composition. Very similar observations were also made with the other physicochemical parameters; however, the composition of the microbiome was not affected by the change in pH and biological oxygen demand (BOD) (<xref ref-type="fig" rid="fig5">Figure 5A</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S3</xref>). Although we could not derive any significant correlation of alpha diversity with the heavy metals (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S4</xref>), physico-chemical properties were significantly associated with the alpha diversity. Notable among them were the positive associations between temperature, alkalinity, and dissolved oxygen (DO) and several parameters of alpha diversity. Contrary to the positive association, hardness, conductivity, and total dissolved solute were negatively correlated with the coverage (<xref ref-type="fig" rid="fig5">Figure 5B</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Association of diversity with other co-factors. <bold>(A)</bold> The association co-efficient of bray Curtis distance with the co-factors which includes the sample variables, heavy metals and physicochemical parameters. <bold>(B)</bold> Association of alpha-diversity with the co-factors.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g005.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Part A shows three grouped bar charts comparing R&#x00B2; values for variables, heavy metals, and physicochemical parameters. Part B displays a heatmap with hierarchical clustering, showing Pearson correlation coefficients for various environmental metrics, with a gradient from blue to red.</alt-text>
</graphic>
</fig>
<p>Interestingly, the Mantel test and the correlation analysis revealed significant associations between environmental factors and microbial community composition. Altitude and lead (Pb) exerted strong and significant correlations with the major bacterial phyla (Proteobacteria, Chloroflexota, Acidobacteriota, and Actinobacteriota; Mantel&#x2019;s <italic>p</italic>&#x202F;&#x003C;&#x202F;0.01). In contrast, other heavy metals such as zinc (Zn), copper (Cu), nickel (Ni), and chromium (Cr) exhibited strong inter-correlations (Pearson&#x2019;s r&#x202F;&#x003E;&#x202F;0.75, <italic>p</italic>&#x202F;&#x003C;&#x202F;0.001), but their direct associations with microbial phyla were comparatively weaker (Mantel&#x2019;s r&#x202F;&#x003C;&#x202F;0.3). These results indicate that, although metals often co-vary in the environment, only a subset (in this case, Pb) exerts a pronounced influence on shaping microbial community composition across river niches (<xref ref-type="fig" rid="fig6">Figure 6</xref>). Similarly, for the physicochemical parameters, pH, temperature, and alkalinity showed the strongest associations with microbial community structure (Mantel&#x2019;s r&#x202F;=&#x202F;0.35&#x2013;0.48, <italic>p</italic>&#x202F;&#x003C;&#x202F;0.01), particularly influencing Proteobacteria, Bacteroidota, Acidobacteriota, and Chloroflexota. Dissolved oxygen also exhibited a moderate but significant association (Mantel&#x2019;s r&#x202F;=&#x202F;0.28, <italic>p</italic>&#x202F;&#x003C;&#x202F;0.05). In contrast, total dissolved solids (TDS), conductivity, BOD, and hardness showed weak or non-significant associations with microbial communities (Mantel&#x2019;s r&#x202F;&#x003C;&#x202F;0.2, <italic>p</italic>&#x202F;&#x003E;&#x202F;0.05). A correlation analysis of environmental parameters indicated strong inter-relationships, particularly between TDS and conductivity (Pearson&#x2019;s r&#x202F;&#x003E;&#x202F;0.75, <italic>p</italic>&#x202F;&#x003C;&#x202F;0.001).</p>
<fig position="float" id="fig6">
<label>Figure 6</label>
<caption>
<p>Mantel correlation of the co-factors and overall diversity.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g006.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Correlation heatmap and network diagram showing relationships between bacterial phyla and environmental factors like Pb, Co, Zn, Cu, Ni, Cr, Cd, and altitude. Dark blue squares indicate significant correlations (Pearson's r), with color intensity showing significance level. Lines represent Mantel's p-values, with orange for p &#x003C; 0.01 and green for p &#x2265; 0.05. Thicker lines indicate higher Mantel's r values.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec12">
<label>3.4</label>
<title>Microbial composition is influenced by seasonal variation and ecological niches, with sediments harboring taxon associated with sulfur and nitrogen cycling</title>
<p>Across all samples, the microbial communities were dominated by Proteobacteria, which accounted for 57&#x2013;59% during the monsoon and 42&#x2013;45% during winter in both the sediment and water niches. Bacteroidota, Acidobacteriota, and Actinobacteriota were the major subdominant phyla detected across both niches. Interestingly, among all the phyla, Actinobacteriota showed a marked seasonal shift, increasing from 2 to 5% in monsoon to 20% in winter sediment samples. Verrucomicrobiota and Chloroflexota exhibited niche-specific enrichment, particularly Verrucomicrobiota in water samples collected during the winter season (5.6%) and Chloroflexota in sediment collected during winter (6.4%). Minor phyla, such as Patescibacteria, Firmicutes_D, Myxococcota, and Nitrospirota, were present in low but detectable abundances, with Firmicutes_D notably enriched in water during winters (6.1%) (<xref ref-type="fig" rid="fig7">Figure 7A</xref>).</p>
<fig position="float" id="fig7">
<label>Figure 7</label>
<caption>
<p>Composition of bacterial diversity in the Teesta River system: <bold>(A)</bold> top 10 phyla across all the samples and <bold>(B)</bold> top 25 genera across all the samples.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g007.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Heatmaps labeled (A) and (B) compare relative abundances of various bacteria phyla and genera during monsoon and winter. In (A), Proteobacteria dominate both seasons, while others like Actinobacteriota and Acidobacteriota vary. In (B), individual bacterial genera show different adaptations, with notable changes such as Pseudomonas and Bacillus between seasons. Blue indicates higher abundance, red indicates lower.</alt-text>
</graphic>
</fig>
<p>At the genus level, we observed that the composition of microbes is more heterogeneous. Within Proteobacteria, <italic>Aeromonas</italic>, <italic>Caulobacter</italic>, <italic>Pseudomonas</italic>, <italic>Thiobacillus</italic>, <italic>Nevskia</italic>, and <italic>Serratia</italic> were variably enriched across both niches and seasons. While <italic>Aeromonas</italic> was abundant in sediment samples from the monsoon (8.3%), <italic>Caulobacter</italic> dominated in the samples from water collected during the monsoon (7.5%). <italic>Serratia,</italic> on the other hand, was undetected in monsoon samples but strongly enriched during the winters, especially in water samples (5%). <italic>Mycobacterium</italic> (Actinobacteriota) and <italic>Flavobacterium</italic> (Bacteroidota) appeared consistently across conditions, although in relatively low abundances. <italic>Nitrososphaera</italic> (Thermoproteota) and <italic>Nitrospira</italic> (Nitrospirota) represented key functional taxa with niche-specific presence, particularly in water samples collected in the winters (<xref ref-type="fig" rid="fig7">Figure 7B</xref>). Overall, genus-level composition revealed both seasonal and habitat-specific fluctuations, with several taxa restricted to seasonal conditions.</p>
<p>Linear discriminant analysis effect size (LEfSe) analysis identified distinct taxonomic signatures between sediment and water microbiomes. Sediment samples were significantly enriched in genera such as <italic>Thiobacillus</italic>, <italic>GWC2-73-18</italic>, <italic>Marmoricola, Nocardiodes, Rhodococcus, Anaeromyxobacter, Bradyrhizobium,</italic> and <italic>Methanobacterium</italic> (LDA score &#x003E; 2, <italic>p</italic>&#x202F;&#x003C;&#x202F;0.05). In contrast, water samples were characterized by enrichment of <italic>Caulobacter, Rugosibacter, Planktophila</italic>, <italic>Sediminibacterium</italic>, <italic>Novimethylophilus,</italic> and <italic>UBA11358</italic> (<xref ref-type="fig" rid="fig8">Figure 8A</xref>). Similarly, considering the variations in seasons, <italic>Nevskia, Massilia, Tolumonas, Pararheinheimera,</italic> and <italic>Cupriavidus</italic> were enriched during the monsoon season, whereas genera such as <italic>Serratia, Listeria, Pandoraea, Methanobrevibacter, Ohtaekwangia, Escherichia,</italic> and <italic>Bacillus</italic> were enriched in the winter season (<xref ref-type="fig" rid="fig8">Figure 8B</xref>). Taken together, our results highlight strong habitat-specific differentiation, where sediment communities are dominated by metabolically diverse lineages associated with sulfur and nitrogen cycling, while water communities harbor lineages adapted to planktonic or surface-associated lifestyles.</p>
<fig position="float" id="fig8">
<label>Figure 8</label>
<caption>
<p><bold>(A)</bold> Differentially abundant genera according to niche, sediment, or water and <bold>(B)</bold> differentially abundant genera across two seasons, monsoon and winter.</p>
</caption>
<graphic xlink:href="frwa-07-1755117-g008.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Two bar charts labeled A and B compare LDA scores. Chart A features red and blue bars representing sediment and water groups, respectively, with the sediment group having higher scores. Chart B shows green and blue bars depicting monsoon and winter groups, with the winter group displaying higher scores. Both charts list various scientific names along the y-axis.</alt-text>
</graphic>
</fig>
</sec>
</sec>
<sec sec-type="discussion" id="sec13">
<label>4</label>
<title>Discussion</title>
<p>Bacterial communities in freshwater play a vital role in nutrient cycling and energy flux in the system. Changes in the nutrient input and physical environment have a profound impact on bacterial composition and species abundance. A culture-independent microbial analysis study provides insights into non-culturable bacterial composition and diversity, thereby increasing the understanding of microbial ecology in a river gradient. In this study, bacterial diversity in the water and sediment samples during the monsoon and winter seasons was analyzed using Illumina high-throughput sequencing.</p>
<p>In the Teesta River, microbial richness varied across sampling sites, but the overall community composition remained stable, suggesting the persistence of a resilient core microbiome. Such stability, despite richness changes, has been reported in other large river systems and is often attributed to the stochastic turnover of rare taxa while dominant taxa remain conserved (<xref ref-type="bibr" rid="ref11">Fortunato et al., 2013</xref>; <xref ref-type="bibr" rid="ref29">Read et al., 2015</xref>). Habitat heterogeneity also played a strong role, with distinct assemblages between water and sediment, consistent with previous reports that sediments provide more stable, nutrient-rich niches compared to the highly dynamic water column (<xref ref-type="bibr" rid="ref32">Savio et al., 2015</xref>). Elevation further structured microbial assemblages along the river gradient, highlighting deterministic filtering by physicochemical changes across altitudes. Elevation-driven variation was accompanied by significant compositional shifts in both water and sediment microbiota. This pattern could be attributed to the rapid urbanization in the lower stretches (Site 3 to Site 6) compared to the upper two sites. Similar upstream&#x2013;downstream patterns have been reported in other Himalayan rivers, such as the glacier-fed Ganga, where altitudinal and physicochemical gradients strongly influence microbial assembly (<xref ref-type="bibr" rid="ref31">Samson et al., 2025</xref>). These findings highlight that, much like land-use gradients observed in large basins such as the Yangtze (<xref ref-type="bibr" rid="ref21">Liu et al., 2024</xref>), elevation in Himalayan rivers creates strong ecological partitions that structure riverine microbiomes.</p>
<p>Seasonality introduced additional variation in the microbial composition, particularly between wet and dry seasons. Riverine ecosystems are subject to significant temporal changes in matter and energy input, which in turn drive shifts in microbial communities. During the dry season, lower water flow and higher temperatures create stable conditions that promote microbial activity and diversity. In contrast, monsoon or post-monsoon high flows and nutrient dilution can reduce overall richness but favor the relative abundance of taxa adapted to disturbance, leading to compositional shifts (<xref ref-type="bibr" rid="ref10">Fang et al., 2023</xref>). Our results showed subtle but significant seasonal influences, a finding supported by earlier studies demonstrating that both deterministic and stochastic processes regulate bacterioplankton assembly across seasons.</p>
<p>Our findings from the Teesta River reflect a dual pattern: deterministic processes (such as habitat type, elevation, and environmental filtering) maintain stable core taxa, while seasonal fluctuations drive richness and subtle compositional shifts. Microbial community structure and functioning in freshwater ecosystems are greatly influenced by several environmental parameters, thereby making them reliable ecological indicators (<xref ref-type="bibr" rid="ref14">Hou et al., 2017</xref>). It becomes imperative to study and discuss the crucial environmental factors that influence the microbial ecology of the fragile riverine ecosystem of the Himalayan river Teesta. Continuous accumulation of multiple heavy metals in an ecosystem can intensify existing environmental pressures by altering water chemistry, increasing toxicity, and disrupting nutrient cycling. It has been further elucidated that microplastics and nanoplastics disrupt nitrogen cycling by altering microbial composition and function (<xref ref-type="bibr" rid="ref39">Zhang et al., 2024</xref>). This reinforces our findings from the Teesta River, where heavy metals, particularly lead, act as strong environmental filters shaping microbial assemblages and influencing nutrient cycling. Together, these studies highlight the fact that emerging pollutants and traditional contaminants can jointly restructure river microbiomes and impair key biogeochemical processes. These factors often act synergistically, leading to shifts in microbial community structure, reduced biodiversity, and impaired ecosystem functioning (<xref ref-type="bibr" rid="ref12">Guo et al., 2019</xref>).</p>
<p>Our results highlight the strong influence of environmental parameters, particularly heavy metals, and key environmental factors such as temperature, dissolved oxygen, and alkalinity, on shaping the microbiome of the Teesta River. While overall heavy metals were significantly associated with microbial composition, only lead showed a strong direct effect on dominant phyla such as Proteobacteria, Chloroflexota, Acidobacteriota, and Actinobacteriota. This suggests that, although metals such as Zn, Cu, Ni, and Cr frequently co-vary, their ecological influence is secondary compared to Pb, which acts as a stronger environmental filter. Similar associations of Pb with microbial structuring have been reported in other river systems, where Pb stress often drives shifts in dominant bacterial groups, reflecting selective tolerance and adaptation. The positive correlation of bacterial groups with heavy metals indicates their potential resilience or adaptability to contaminated environments (<xref ref-type="bibr" rid="ref1">Beattie et al., 2018</xref>). This could be attributed to the selective growth of species that can adapt to environmental stressors such as metal contamination, while sensitive species are eliminated via the process of natural selection (<xref ref-type="bibr" rid="ref16">Jordaan et al., 2019</xref>). Consistent with South Asian rivers, microbial patterns in the Teesta are strongly shaped by temperature, pH, and dissolved oxygen, with pollution-driven changes, especially heavy metals, further restructuring community composition and function (<xref ref-type="bibr" rid="ref36">Thakur et al., 2025</xref>).</p>
<p>An earlier study revealed that the concentration of Pb was found to exceed the standard values provided by the Indian River System (IRS) for sediment samples in the lower stretches of the Teesta River (<xref ref-type="bibr" rid="ref5">Chettri et al., 2022</xref>). In the present study, <italic>Aeromonas</italic>, <italic>Caulobacter</italic>, <italic>Pseudomonas</italic>, <italic>Thiobacillus</italic>, <italic>Nevskia</italic>, <italic>Listeria,</italic> and <italic>Serratia</italic> were found to be enriched across sites and seasons. The detection of <italic>Listeria</italic> species in the winter samples from the Teesta River indicates natural environmental occurrence and potential fecal contamination within the watershed. As <italic>Listeria</italic> is commonly found in soil, decaying vegetation, and animal feces, its presence suggests introduction by surrounding anthropogenic sources (<xref ref-type="bibr" rid="ref17">Kayode et al., 2021</xref>). The organism&#x2019;s recovery during winter aligns with its ability to survive and persist at low temperatures, which enhances its stability in aquatic environments. The highest percentage of the culturable bacterial isolates belonging to the genera <italic>Pseudomonas</italic> and <italic>Serratia</italic> was previously reported from the Teesta River, which displayed the highest resistance to Pb and harbored heavy metal and antibiotic resistance genes (<xref ref-type="bibr" rid="ref7">Chettri et al., 2023</xref>). Collectively, these findings suggest their resilience to environmental stressors and can be regarded as ecological indicators of heavy metal pollution.</p>
<p>Heavy metals are extensively used in industrial processes and enter river systems through multiple pathways, including industrial discharge, vehicular emissions, battery waste, mining activities, and gasoline spillage (<xref ref-type="bibr" rid="ref1001">Mahato et al., 2017</xref>). Prolonged heavy metal contamination imposes strong selective pressure on riverine microbial communities, often leading to reductions in microbial biomass and diversity; while trace metal concentrations may stimulate microbial activity, elevated levels exert toxic effects that suppress bacterial growth and diversity (<xref ref-type="bibr" rid="ref4">Chaturvedi et al., 2024</xref>). Polluted riverine ecosystems, therefore, act as potential hotspots for bacteria exhibiting dual resistance to heavy metals and antibiotics, driven by co-resistance and cross-resistance mechanisms (<xref ref-type="bibr" rid="ref1002">Baker-Austin et al., 2006</xref>). In this context, the dominance of Proteobacteria displaying resistance to both heavy metals and antibiotics has been widely reported across contaminated river ecosystems (<xref ref-type="bibr" rid="ref1003">Yewale et al., 2020</xref>; <xref ref-type="bibr" rid="ref1004">Tapia-Arreola et al., 2022</xref>). While the present study is based on field-derived physicochemical and microbial analyses, recent advances in hyperspectral remote sensing provide valuable complementary approaches to water quality assessment. Hyperspectral imagery enables high-resolution monitoring of surface water parameters and captures spatial&#x2013;temporal variability driven by anthropogenic and hydrological stressors (<xref ref-type="bibr" rid="ref34">Srivastava et al., 2025</xref>). Integrating hyperspectral data with microbial indicators could facilitate near-real-time river health assessment and scalable biomonitoring, particularly in large and dynamic South Asian river systems where sustained ground-based monitoring is challenging.</p>
</sec>
<sec sec-type="conclusions" id="sec14">
<label>5</label>
<title>Conclusion</title>
<p>This study explored spatial, seasonal, and sample-type variations in bacterial communities and provided insights into their interrelationships with the physico-chemical parameters, including heavy metals. Our results indicated that the microbial composition relatively remained stable across seasons, sites, and sample types; however, species richness showed notable spatial variations along the altitudinal gradient of the Teesta River. Significant variation in richness across sites was observed, despite comparable diversity patterns. Linear modelling further confirmed that site-specific factors exerted the strongest influence on richness metrics such as the Chao1 and Observed OTUs. As revealed by the beta-diversity analyses, seasonal shifts and sample types (water vs. sediment) contributed modest yet detectable differences, particularly in Bray&#x2013;Curtis distances. Elevation also influenced microbial composition, with clearer differences observed when water and sediment samples were analyzed together. Environmental factors, particularly heavy metals and key physico-chemical parameters, showed a significant association with the bacterial community structure of the Teesta River. Lead (Pb) emerged as the strongest driver of compositional shifts, whereas other metals, despite high intercorrelation, exhibited weaker biological effects. Physico-chemical parameters, such as pH, temperature, alkalinity, and dissolved oxygen, exhibited the strongest relationships with major bacterial phyla, whereas parameters such as TDS, conductivity, BOD, and hardness showed minimal influence. The Teesta River microbiome displayed clear seasonal and habitat-specific taxonomic patterns, with Proteobacteria dominating across all samples and marked winter enrichment of Actinobacteriota in sediments. Genus-level composition revealed strong niche differentiation, further supported by LEfSe analysis, which identified distinct microbial signatures in water and sediment communities. Seasonal shifts also shaped genus-level abundances, with monsoon and winter each favoring specific taxa. Collectively, the study highlighted the critical role of local environmental heterogeneity in shaping microbial richness. The observed patterns suggest that environmental gradients shape subtle compositional shifts while maintaining a largely conserved community structure in the Himalayan river ecosystem. The study further concluded that both habitat and season play major roles in structuring the river&#x2019;s microbial assemblages.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="sec15">
<title>Data availability statement</title>
<p>The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: <ext-link xlink:href="https://www.ncbi.nlm.nih.gov/" ext-link-type="uri">https://www.ncbi.nlm.nih.gov/</ext-link>, SAMN53384420, SAMN53384421, SAMN53384422, SAMN53384423, SAMN53384424, SAMN53384425, SAMN53384426, SAMN53384427, SAMN53384428, SAMN53384429, SAMN53384430, SAMN53384431, SAMN53399705, SAMN53399706, SAMN53399707, SAMN53399708, SAMN53399709, SAMN53399710, SAMN53399711, SAMN53399712, SAMN53399713, SAMN53399714, SAMN53399715, and SAMN53399716.</p>
</sec>
<sec sec-type="author-contributions" id="sec16">
<title>Author contributions</title>
<p>UC: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. SD: Formal analysis, Investigation, Methodology, Software, Visualization, Writing &#x2013; original draft. TC: Conceptualization, Formal analysis, Methodology, Writing &#x2013; review &#x0026; editing. SJ: Conceptualization, Funding acquisition, Project administration, Supervision, Visualization, Writing &#x2013; review &#x0026; editing.</p>
</sec>
<sec sec-type="COI-statement" id="sec17">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="sec18">
<title>Generative AI statement</title>
<p>The author(s) declared that Generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="sec19">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec sec-type="supplementary-material" id="sec20">
<title>Supplementary material</title>
<p>The Supplementary material for this article can be found online at: <ext-link xlink:href="https://www.frontiersin.org/articles/10.3389/frwa.2025.1755117/full#supplementary-material" ext-link-type="uri">https://www.frontiersin.org/articles/10.3389/frwa.2025.1755117/full#supplementary-material</ext-link></p>
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</sec>
<ref-list>
<title>References</title>
<ref id="ref1002"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Baker-Austin</surname><given-names>C.</given-names></name> <name><surname>Wright</surname><given-names>M. S.</given-names></name> <name><surname>Stepanauskas</surname><given-names>R.</given-names></name> <name><surname>McArthur</surname><given-names>J. V.</given-names></name></person-group> (<year>2006</year>). <article-title>Major uncertainties and future research opportunities in metal&#x2013;antibiotic co-selection</article-title>. <source>Trends Microbiol.</source> <volume>14</volume>, <fpage>176</fpage>&#x2013;<lpage>82</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.tim.2006.02.006</pub-id></mixed-citation></ref>
<ref id="ref1"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Beattie</surname><given-names>R. E.</given-names></name> <name><surname>Henke</surname><given-names>W.</given-names></name> <name><surname>Campa</surname><given-names>M. F.</given-names></name> <name><surname>Hazen</surname><given-names>T. C.</given-names></name> <name><surname>McAliley</surname><given-names>L. R.</given-names></name> <name><surname>Campbell</surname><given-names>J. H.</given-names></name></person-group> (<year>2018</year>). <article-title>Variation in microbial community structure correlates with heavy-metal contamination in soils decades after mining ceased</article-title>. <source>Soil Biol. Biochem.</source> <volume>126</volume>, <fpage>57</fpage>&#x2013;<lpage>63</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.soilbio.2018.08.011</pub-id></mixed-citation></ref>
<ref id="ref2"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Bhaskar</surname><given-names>B.</given-names></name> <name><surname>Bhattacharya</surname><given-names>A.</given-names></name> <name><surname>Adak</surname><given-names>A.</given-names></name> <name><surname>Das</surname><given-names>S.</given-names></name> <name><surname>Khan</surname><given-names>M. R.</given-names></name></person-group> (<year>2023</year>). <article-title>A human and animal based study reveals that a traditionally fermented rice beverage alters gut microbiota and fecal metabolites for better gut health</article-title>. <source>Fermentation</source> <volume>9</volume>:<fpage>126</fpage>. doi: <pub-id pub-id-type="doi">10.3390/fermentation9020126</pub-id></mixed-citation></ref>
<ref id="ref3"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Callahan</surname><given-names>B. J.</given-names></name> <name><surname>McMurdie</surname><given-names>P. J.</given-names></name> <name><surname>Rosen</surname><given-names>M. J.</given-names></name> <name><surname>Han</surname><given-names>A. W.</given-names></name> <name><surname>Johnson</surname><given-names>A. J. A.</given-names></name> <name><surname>Holmes</surname><given-names>S. P.</given-names></name></person-group> (<year>2016</year>). <article-title>DADA2: high-resolution sample inference from Illumina amplicon data</article-title>. <source>Nat. Methods</source> <volume>13</volume>, <fpage>581</fpage>&#x2013;<lpage>583</lpage>. doi: <pub-id pub-id-type="doi">10.1038/nmeth.3869</pub-id>, <pub-id pub-id-type="pmid">27214047</pub-id></mixed-citation></ref>
<ref id="ref4"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chaturvedi</surname><given-names>S.</given-names></name> <name><surname>Chakraborty</surname><given-names>B.</given-names></name> <name><surname>Min</surname><given-names>L.</given-names></name> <name><surname>Kumar</surname><given-names>A.</given-names></name> <name><surname>Pathak</surname><given-names>B.</given-names></name> <name><surname>Kumar</surname><given-names>R.</given-names></name> <etal/></person-group>. (<year>2024</year>). <article-title>Exploring the dynamic microbial tapestry of south Asian rivers: insights from the Ganges and Yamuna ecosystems</article-title>. <source>Ecohydrology</source> <volume>17</volume>:<fpage>e2662</fpage>. doi: <pub-id pub-id-type="doi">10.1002/eco.2662</pub-id></mixed-citation></ref>
<ref id="ref5"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chettri</surname><given-names>U.</given-names></name> <name><surname>Chakrabarty</surname><given-names>T. K.</given-names></name> <name><surname>Joshi</surname><given-names>S. R.</given-names></name></person-group> (<year>2022</year>). <article-title>Pollution index assessment of surface water and sediment quality with reference to heavy metals in Teesta River in eastern Himalayan range, India</article-title>. <source>Environ. Nanotechnol. Monit. Manag.</source> <volume>18</volume>:<fpage>100742</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.enmm.2022.100742</pub-id></mixed-citation></ref>
<ref id="ref6"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chettri</surname><given-names>U.</given-names></name> <name><surname>Joshi</surname><given-names>S. R.</given-names></name></person-group> (<year>2022</year>). <article-title>A first calibration of Culturable bacterial diversity and their dual resistance to heavy metals and antibiotics along altitudinal zonation of the Teesta River</article-title>. <source>Arch. Microbiol.</source> <volume>204</volume>:<fpage>241</fpage>. doi: <pub-id pub-id-type="doi">10.1007/s00203-022-02858-1</pub-id>, <pub-id pub-id-type="pmid">35378604</pub-id></mixed-citation></ref>
<ref id="ref7"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chettri</surname><given-names>U.</given-names></name> <name><surname>Nongkhlaw</surname><given-names>M.</given-names></name> <name><surname>Joshi</surname><given-names>S. R.</given-names></name></person-group> (<year>2023</year>). <article-title>Molecular evidence for occurrence of heavy metal and antibiotic resistance genes among predominant metal tolerant Pseudomonas Sp. and Serratia Sp. prevalent in the Teesta River</article-title>. <source>Curr. Microbiol.</source> <volume>80</volume>:<fpage>226</fpage>. doi: <pub-id pub-id-type="doi">10.1007/s00284-023-03334-9</pub-id>, <pub-id pub-id-type="pmid">37227565</pub-id></mixed-citation></ref>
<ref id="ref8"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chowdhury</surname><given-names>N. T.</given-names></name></person-group> (<year>2010</year>). <article-title>Water management in Bangladesh: an analytical review</article-title>. <source>Water Policy</source> <volume>12</volume>, <fpage>32</fpage>&#x2013;<lpage>51</lpage>. doi: <pub-id pub-id-type="doi">10.2166/wp.2009.112</pub-id></mixed-citation></ref>
<ref id="ref9"><mixed-citation publication-type="other"><collab id="coll1">Environmental Information System (ENVIS)</collab>. (<year>2019</year>). The Teesta and Its Tributaries. Sikkim. Available online at: <ext-link xlink:href="http://sikenvis.nic.in/Database/Rivers_781.aspx" ext-link-type="uri">http://sikenvis.nic.in/Database/Rivers_781.aspx</ext-link></mixed-citation></ref>
<ref id="ref10"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Fang</surname><given-names>W.</given-names></name> <name><surname>Fan</surname><given-names>T.</given-names></name> <name><surname>Wang</surname><given-names>S.</given-names></name> <name><surname>Yu</surname><given-names>X.</given-names></name> <name><surname>Lu</surname><given-names>A.</given-names></name> <name><surname>Wang</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2023</year>). <article-title>Seasonal changes driving shifts in microbial community assembly and species coexistence in an urban river</article-title>. <source>Sci. Total Environ.</source> <volume>905</volume>:<fpage>167027</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2023.167027</pub-id></mixed-citation></ref>
<ref id="ref11"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Fortunato</surname><given-names>C. S.</given-names></name> <name><surname>Eiler</surname><given-names>A.</given-names></name> <name><surname>Herfort</surname><given-names>L.</given-names></name> <name><surname>Needoba</surname><given-names>J. A.</given-names></name> <name><surname>Peterson</surname><given-names>T. D.</given-names></name> <name><surname>Crump</surname><given-names>B. C.</given-names></name></person-group> (<year>2013</year>). <article-title>Determining Indicator taxa across spatial and seasonal gradients in the Columbia River coastal margin</article-title>. <source>ISME J.</source> <volume>7</volume>, <fpage>1899</fpage>&#x2013;<lpage>1911</lpage>. doi: <pub-id pub-id-type="doi">10.1038/ismej.2013.79</pub-id>, <pub-id pub-id-type="pmid">23719153</pub-id></mixed-citation></ref>
<ref id="ref12"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Guo</surname><given-names>Q.</given-names></name> <name><surname>Li</surname><given-names>N.</given-names></name> <name><surname>Xie</surname><given-names>S.</given-names></name></person-group> (<year>2019</year>). <article-title>Heavy metal spill influences bacterial communities in freshwater sediments</article-title>. <source>Arch. Microbiol.</source> <volume>201</volume>, <fpage>847</fpage>&#x2013;<lpage>854</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s00203-019-01650-y</pub-id>, <pub-id pub-id-type="pmid">30888453</pub-id></mixed-citation></ref>
<ref id="ref13"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Hong</surname><given-names>Y.</given-names></name> <name><surname>Gu</surname><given-names>J.-D.</given-names></name></person-group> (<year>2009</year>). <article-title>Bacterial anaerobic respiration and electron transfer relevant to the biotransformation of pollutants</article-title>. <source>Int. Biodeterior. Biodegrad.</source> <volume>63</volume>, <fpage>973</fpage>&#x2013;<lpage>980</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.ibiod.2009.08.001</pub-id></mixed-citation></ref>
<ref id="ref14"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Hou</surname><given-names>D.</given-names></name> <name><surname>Huang</surname><given-names>Z.</given-names></name> <name><surname>Zeng</surname><given-names>S.</given-names></name> <name><surname>Liu</surname><given-names>J.</given-names></name> <name><surname>Wei</surname><given-names>D.</given-names></name> <name><surname>Deng</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2017</year>). <article-title>Environmental factors shape water microbial community structure and function in shrimp cultural enclosure ecosystems</article-title>. <source>Front. Microbiol.</source> <volume>8</volume>:<fpage>2359</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fmicb.2017.02359</pub-id>, <pub-id pub-id-type="pmid">29238333</pub-id></mixed-citation></ref>
<ref id="ref15"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Hugenholtz</surname><given-names>P.</given-names></name> <name><surname>Tyson</surname><given-names>G. W.</given-names></name></person-group> (<year>2008</year>). <article-title>Metagenomics</article-title>. <source>Nature</source> <volume>455</volume>, <fpage>481</fpage>&#x2013;<lpage>483</lpage>. doi: <pub-id pub-id-type="doi">10.1038/455481a</pub-id>, <pub-id pub-id-type="pmid">18818648</pub-id></mixed-citation></ref>
<ref id="ref16"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Jordaan</surname><given-names>K.</given-names></name> <name><surname>Comeau</surname><given-names>A. M.</given-names></name> <name><surname>Khasa</surname><given-names>D. P.</given-names></name> <name><surname>Bezuidenhout</surname><given-names>C. C.</given-names></name></person-group> (<year>2019</year>). <article-title>An integrated insight into the response of bacterial communities to anthropogenic contaminants in a river: a case study of the Wonderfonteinspruit catchment area, South Africa</article-title>. <source>PLoS One</source> <volume>14</volume>:<fpage>e0216758</fpage>. doi: <pub-id pub-id-type="doi">10.1371/journal.pone.0216758</pub-id>, <pub-id pub-id-type="pmid">31112559</pub-id></mixed-citation></ref>
<ref id="ref17"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Kayode</surname><given-names>A. J.</given-names></name> <name><surname>Semerjian</surname><given-names>L.</given-names></name> <name><surname>Osaili</surname><given-names>T.</given-names></name> <name><surname>Olapade</surname><given-names>O.</given-names></name> <name><surname>Okoh</surname><given-names>A. I.</given-names></name></person-group> (<year>2021</year>). <article-title>Occurrence of multidrug-resistant Listeria monocytogenes in environmental waters: a menace of environmental and public health concern</article-title>. <source>Front. Environ. Sci.</source> <volume>9</volume>:<fpage>737435</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fenvs.2021.737435</pub-id></mixed-citation></ref>
<ref id="ref18"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Kumar Mondal</surname><given-names>S.</given-names></name> <name><surname>Bharti</surname><given-names>R.</given-names></name> <name><surname>Kumar</surname><given-names>S.</given-names></name></person-group> (<year>2023</year>). <article-title>Spatio-temporal variations in oxygen and deuterium isotope of different water sources in Sikkim Himalayas: an understanding towards regional scale basin hydrology</article-title>. <source>J. Hydrol.</source> <volume>621</volume>:<fpage>129613</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.jhydrol.2023.129613</pub-id></mixed-citation></ref>
<ref id="ref19"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Li</surname><given-names>C.</given-names></name> <name><surname>Quan</surname><given-names>Q.</given-names></name> <name><surname>Gan</surname><given-names>Y.</given-names></name> <name><surname>Dong</surname><given-names>J.</given-names></name> <name><surname>Fang</surname><given-names>J.</given-names></name> <name><surname>Wang</surname><given-names>L.</given-names></name> <etal/></person-group>. (<year>2020</year>). <article-title>Effects of heavy metals on microbial communities in sediments and establishment of bioindicators based on microbial taxa and function for environmental monitoring and management</article-title>. <source>Sci. Total Environ.</source> <volume>749</volume>:<fpage>141555</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2020.141555</pub-id>, <pub-id pub-id-type="pmid">32841857</pub-id></mixed-citation></ref>
<ref id="ref20"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname><given-names>Y.</given-names></name> <name><surname>Lin</surname><given-names>Q.</given-names></name> <name><surname>Huang</surname><given-names>X.</given-names></name> <name><surname>Jiang</surname><given-names>G.</given-names></name> <name><surname>Li</surname><given-names>C.</given-names></name> <name><surname>Zhang</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2021</year>). <article-title>Effects of dietary Ferulic acid on the intestinal microbiota and the associated changes on the growth performance, serum cytokine profile, and intestinal morphology in ducks</article-title>. <source>Front. Microbiol.</source> <volume>12</volume>:<fpage>698213</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fmicb.2021.698213</pub-id>, <pub-id pub-id-type="pmid">34326826</pub-id></mixed-citation></ref>
<ref id="ref21"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname><given-names>X.</given-names></name> <name><surname>Zhang</surname><given-names>L.</given-names></name> <name><surname>Wang</surname><given-names>Y.</given-names></name> <name><surname>Hu</surname><given-names>S.</given-names></name> <name><surname>Zhang</surname><given-names>J.</given-names></name> <name><surname>Huang</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2024</year>). <article-title>Microbiome analysis in Asia&#x2019;s largest watershed reveals inconsistent biogeographic pattern and microbial assembly mechanisms in river and Lake systems</article-title>. <source>iScience</source> <volume>27</volume>:<fpage>110053</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.isci.2024.110053</pub-id>, <pub-id pub-id-type="pmid">38947525</pub-id></mixed-citation></ref>
<ref id="ref1001"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Mahato</surname><given-names>M. K.</given-names></name> <name><surname>Singh</surname><given-names>G.</given-names></name> <name><surname>Singh</surname><given-names>P. K.</given-names></name> <name><surname>Singh</surname><given-names>A. K.</given-names></name> <name><surname>Tiwari</surname><given-names>A. K.</given-names></name></person-group> (<year>2017</year>). <article-title>Assessment of mine water quality using heavy metal pollution index in a coal mining area of Damodar River Basin, India</article-title>. <source>Bull. Environ. Contam. Toxicol.</source> <volume>99</volume>, <fpage>54</fpage>&#x2013;<lpage>61</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s00128-017-2097-3</pub-id></mixed-citation></ref>
<ref id="ref22"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Marti</surname><given-names>E.</given-names></name> <name><surname>Jofre</surname><given-names>J.</given-names></name> <name><surname>Balcazar</surname><given-names>J. L.</given-names></name></person-group> (<year>2013</year>). <article-title>Prevalence of antibiotic resistance genes and bacterial community composition in a river influenced by a wastewater treatment plant</article-title>. <source>PLoS One</source> <volume>8</volume>:<fpage>e78906</fpage>. doi: <pub-id pub-id-type="doi">10.1371/journal.pone.0078906</pub-id>, <pub-id pub-id-type="pmid">24205347</pub-id></mixed-citation></ref>
<ref id="ref23"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>McMurdie</surname><given-names>P. J.</given-names></name> <name><surname>Holmes</surname><given-names>S.</given-names></name></person-group> (<year>2013</year>). <article-title>Phyloseq: an R package for reproducible interactive analysis and graphics of microbiome census data</article-title>. <source>PLoS One</source> <volume>8</volume>:<fpage>e61217</fpage>. doi: <pub-id pub-id-type="doi">10.1371/journal.pone.0061217</pub-id>, <pub-id pub-id-type="pmid">23630581</pub-id></mixed-citation></ref>
<ref id="ref24"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Mullick</surname><given-names>M. R. A.</given-names></name> <name><surname>Babel</surname><given-names>M. S.</given-names></name> <name><surname>Perret</surname><given-names>S. R.</given-names></name></person-group> (<year>2013</year>). <article-title>Marginal benefit based optimal water allocation: case of Teesta River, Bangladesh</article-title>. <source>Water Policy</source> <volume>15</volume>, <fpage>126</fpage>&#x2013;<lpage>146</lpage>. doi: <pub-id pub-id-type="doi">10.2166/wp.2013.004</pub-id></mixed-citation></ref>
<ref id="ref25"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Ouyang</surname><given-names>L.</given-names></name> <name><surname>Chen</surname><given-names>H.</given-names></name> <name><surname>Liu</surname><given-names>X.</given-names></name> <name><surname>Wong</surname><given-names>M. H.</given-names></name> <name><surname>Xu</surname><given-names>F.</given-names></name> <name><surname>Yang</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2020</year>). <article-title>Characteristics of spatial and seasonal bacterial community structures in a river under anthropogenic disturbances</article-title>. <source>Environ. Pollut.</source> <volume>264</volume>:<fpage>114818</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envpol.2020.114818</pub-id>, <pub-id pub-id-type="pmid">32559870</pub-id></mixed-citation></ref>
<ref id="ref26"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>&#x00D6;zkurt</surname><given-names>E.</given-names></name> <name><surname>Fritscher</surname><given-names>J.</given-names></name> <name><surname>Soranzo</surname><given-names>N.</given-names></name> <name><surname>Ng</surname><given-names>D. Y. K.</given-names></name> <name><surname>Davey</surname><given-names>R. P.</given-names></name> <name><surname>Bahram</surname><given-names>M.</given-names></name> <etal/></person-group>. (<year>2022</year>). <article-title>LotuS2: an ultrafast and highly accurate tool for amplicon sequencing analysis</article-title>. <source>Microbiome</source> <volume>10</volume>:<fpage>176</fpage>. doi: <pub-id pub-id-type="doi">10.1186/s40168-022-01365-1</pub-id>, <pub-id pub-id-type="pmid">36258257</pub-id></mixed-citation></ref>
<ref id="ref27"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Quast</surname><given-names>C.</given-names></name> <name><surname>Pruesse</surname><given-names>E.</given-names></name> <name><surname>Yilmaz</surname><given-names>P.</given-names></name> <name><surname>Gerken</surname><given-names>J.</given-names></name> <name><surname>Schweer</surname><given-names>T.</given-names></name> <name><surname>Yarza</surname><given-names>P.</given-names></name> <etal/></person-group>. (<year>2012</year>). <article-title>The SILVA ribosomal RNA gene database project: improved data processing and web-based tools</article-title>. <source>Nucleic Acids Res.</source> <volume>41</volume>, <fpage>D590</fpage>&#x2013;<lpage>D596</lpage>. doi: <pub-id pub-id-type="doi">10.1093/nar/gks1219</pub-id></mixed-citation></ref>
<ref id="ref28"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Rahaman</surname><given-names>M. M.</given-names></name> <name><surname>Al Mamun</surname><given-names>A.</given-names></name></person-group> (<year>2020</year>). <article-title>Hydropower development along Teesta River basin: opportunities for cooperation</article-title>. <source>Water Policy</source> <volume>22</volume>, <fpage>641</fpage>&#x2013;<lpage>657</lpage>. doi: <pub-id pub-id-type="doi">10.2166/wp.2020.136</pub-id></mixed-citation></ref>
<ref id="ref29"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Read</surname><given-names>E. K.</given-names></name> <name><surname>Patil</surname><given-names>V. P.</given-names></name> <name><surname>Oliver</surname><given-names>S. K.</given-names></name> <name><surname>Hetherington</surname><given-names>A. L.</given-names></name> <name><surname>Brentrup</surname><given-names>J. A.</given-names></name> <name><surname>Zwart</surname><given-names>J. A.</given-names></name> <etal/></person-group>. (<year>2015</year>). <article-title>The importance of Lake-specific characteristics for water quality across the continental United States</article-title>. <source>Ecol. Appl.</source> <volume>25</volume>, <fpage>943</fpage>&#x2013;<lpage>955</lpage>. doi: <pub-id pub-id-type="doi">10.1890/14-0935.1</pub-id>, <pub-id pub-id-type="pmid">26465035</pub-id></mixed-citation></ref>
<ref id="ref30"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Reddy</surname><given-names>B.</given-names></name> <name><surname>Dubey</surname><given-names>S. K.</given-names></name></person-group> (<year>2021</year>). <article-title>Exploring the Allochthonous pollution influence on bacterial community and co-occurrence dynamics of river ganga water through 16S rRNA-tagged amplicon metagenome</article-title>. <source>Environ. Sci. Pollut. Res.</source> <volume>28</volume>, <fpage>26990</fpage>&#x2013;<lpage>27005</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11356-021-12342-w</pub-id>, <pub-id pub-id-type="pmid">33501578</pub-id></mixed-citation></ref>
<ref id="ref31"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Samson</surname><given-names>R.</given-names></name> <name><surname>Kumar</surname><given-names>S.</given-names></name> <name><surname>Dastager</surname><given-names>S.</given-names></name> <name><surname>Khairnar</surname><given-names>K.</given-names></name> <name><surname>Dharne</surname><given-names>M.</given-names></name></person-group> (<year>2025</year>). <article-title>Deciphering the comprehensive microbiome of glacier-fed Ganges and functional aspects: implications for one health</article-title>. <source>Microbiology Spectrum</source> <volume>13</volume>, <fpage>e01720</fpage>&#x2013;<lpage>e01724</lpage>. doi: <pub-id pub-id-type="doi">10.1128/spectrum.01720-24</pub-id>, <pub-id pub-id-type="pmid">40621926</pub-id></mixed-citation></ref>
<ref id="ref32"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Savio</surname><given-names>D.</given-names></name> <name><surname>Sinclair</surname><given-names>L.</given-names></name> <name><surname>Ijaz</surname><given-names>U. Z.</given-names></name> <name><surname>Parajka</surname><given-names>J.</given-names></name> <name><surname>Reischer</surname><given-names>G. H.</given-names></name> <name><surname>Stadler</surname><given-names>P.</given-names></name> <etal/></person-group>. (<year>2015</year>). <article-title>Bacterial diversity along a 2600 Km River continuum</article-title>. <source>Environ. Microbiol.</source> <volume>17</volume>, <fpage>4994</fpage>&#x2013;<lpage>5007</lpage>. doi: <pub-id pub-id-type="doi">10.1111/1462-2920.12886</pub-id>, <pub-id pub-id-type="pmid">25922985</pub-id></mixed-citation></ref>
<ref id="ref33"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Sohn</surname><given-names>J. H.</given-names></name> <name><surname>Kwon</surname><given-names>K. K.</given-names></name> <name><surname>Kang</surname><given-names>J.-H.</given-names></name> <name><surname>Jung</surname><given-names>H.-B.</given-names></name> <name><surname>Kim</surname><given-names>S.-J.</given-names></name></person-group> (<year>2004</year>). <article-title>Novosphingobium pentaromativorans sp. nov., a high-molecular-mass polycyclic aromatic hydrocarbon-degrading bacterium isolated from estuarine sediment</article-title>. <source>Int. J. Syst. Evol. Microbiol.</source> <volume>54</volume>, <fpage>1483</fpage>&#x2013;<lpage>1487</lpage>. doi: <pub-id pub-id-type="doi">10.1099/ijs.0.02945-0</pub-id>, <pub-id pub-id-type="pmid">15388699</pub-id></mixed-citation></ref>
<ref id="ref34"><mixed-citation publication-type="book"><person-group person-group-type="author"><name><surname>Srivastava</surname><given-names>M. K.</given-names></name> <name><surname>Gaur</surname><given-names>S.</given-names></name> <name><surname>Ohri</surname><given-names>A.</given-names></name> <name><surname>Srivastava</surname><given-names>P. K.</given-names></name> <name><surname>Chaturvedi</surname><given-names>S.</given-names></name></person-group> (<year>2025</year>). &#x201C;<article-title>Hyperspectral remote sensing: potential prospects in water quality monitoring and assessment</article-title>&#x201D; in <source>Earth observation for monitoring and modeling land use</source> (<publisher-name>Elsevier</publisher-name>). doi: <pub-id pub-id-type="doi">10.1016/B978-0-323-95193-7.00015-4</pub-id></mixed-citation></ref>
<ref id="ref1004"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Tapia-Arreola</surname><given-names>A. K.</given-names></name> <name><surname>Ruiz-Garcia</surname><given-names>D. A.</given-names></name> <name><surname>Rodulfo</surname><given-names>H.</given-names></name> <name><surname>Sharma</surname><given-names>A.</given-names></name> <name><surname>De Donato</surname><given-names>M.</given-names></name></person-group> (<year>2022</year>). <article-title>High frequency of antibiotic resistance genes (ARGs) in the Lerma River Basin, Mexico</article-title>. <source>Int. J. Environ. Res. Public Health,</source> <volume>19</volume>:<fpage>13988</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ijerph192113988</pub-id>, <pub-id pub-id-type="pmid">40621926</pub-id></mixed-citation></ref>
<ref id="ref35"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Thakur</surname><given-names>A.</given-names></name> <name><surname>Kumari</surname><given-names>S.</given-names></name> <name><surname>Borker</surname><given-names>S. S.</given-names></name> <name><surname>Prashant</surname><given-names>S. P.</given-names></name> <name><surname>Kumar</surname><given-names>A.</given-names></name> <name><surname>Kumar</surname><given-names>R.</given-names></name></person-group> (<year>2021</year>). <article-title>Solid waste management in Indian Himalayan region: current scenario, resource recovery, and way forward for sustainable development</article-title>. <source>Front. Energy Res.</source> <volume>9</volume>:<fpage>609229</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fenrg.2021.609229</pub-id></mixed-citation></ref>
<ref id="ref36"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Thakur</surname><given-names>T. K.</given-names></name> <name><surname>Patel</surname><given-names>D. K.</given-names></name> <name><surname>Saini</surname><given-names>S.</given-names></name> <name><surname>Thakur</surname><given-names>A.</given-names></name> <name><surname>Swamy,</surname><given-names>S. L.</given-names></name> <name><surname>Bakshi</surname><given-names>S.</given-names></name> <etal/></person-group>. (<year>2025</year>). <article-title>A geospatial analysis of coal mine overburden reclamation: land use, carbon stock, biomass, and soil genesis in chronosequence plantations</article-title>. <source>J. Geochem. Explor.</source> <volume>271</volume>:<fpage>107674</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.gexplo.2025.107674</pub-id></mixed-citation></ref>
<ref id="ref37"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Valverde</surname><given-names>J. R.</given-names></name> <name><surname>Mellado</surname><given-names>R. P.</given-names></name></person-group> (<year>2013</year>). <article-title>Analysis of metagenomic data containing high biodiversity levels</article-title>. <source>PLoS One</source> <volume>8</volume>:<fpage>e58118</fpage>. doi: <pub-id pub-id-type="doi">10.1371/journal.pone.0058118</pub-id>, <pub-id pub-id-type="pmid">23505458</pub-id></mixed-citation></ref>
<ref id="ref38"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Wang</surname><given-names>L.</given-names></name> <name><surname>Zhang</surname><given-names>J.</given-names></name> <name><surname>Li</surname><given-names>H.</given-names></name> <name><surname>Yang</surname><given-names>H.</given-names></name> <name><surname>Peng</surname><given-names>C.</given-names></name> <name><surname>Peng</surname><given-names>Z.</given-names></name> <etal/></person-group>. (<year>2018</year>). <article-title>Shift in the microbial community composition of surface water and sediment along an Urban River</article-title>. <source>Sci. Total Environ.</source> <volume>627</volume>, <fpage>600</fpage>&#x2013;<lpage>612</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2018.01.203</pub-id>, <pub-id pub-id-type="pmid">29426184</pub-id></mixed-citation></ref>
<ref id="ref1003"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Yewale</surname><given-names>P. P.</given-names></name> <name><surname>Lokhande</surname><given-names>K. B.</given-names></name> <name><surname>Sridhar</surname><given-names>A.</given-names></name> <name><surname>Vaishnav</surname><given-names>M.</given-names></name> <name><surname>Khan</surname><given-names>F. A.</given-names></name> <name><surname>Mandal</surname><given-names>A.</given-names></name> <etal/></person-group>. (<year>2020</year>). <article-title>Molecular profiling of multidrug-resistant river water isolates: insights into resistance mechanism and potential inhibitors</article-title>. <source>Env. Sci. Pollut. Res.</source> <volume>27</volume>, <fpage>27279</fpage>&#x2013;<lpage>27292</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11356-019-05738-2</pub-id>, <pub-id pub-id-type="pmid">25922985</pub-id></mixed-citation></ref>
<ref id="ref39"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Zhang</surname><given-names>T.</given-names></name> <name><surname>Luo</surname><given-names>X.-S.</given-names></name> <name><surname>Kumar</surname><given-names>A.</given-names></name> <name><surname>Liu</surname><given-names>X.</given-names></name> <name><surname>Tong</surname><given-names>X.</given-names></name> <name><surname>Yao</surname><given-names>X.</given-names></name> <etal/></person-group>. (<year>2024</year>). <article-title>Effects of Micro-Nano plastics on the environmental biogeochemical cycle of nitrogen: a comprehensive review</article-title>. <source>Chemosphere</source> <volume>357</volume>:<fpage>142079</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.chemosphere.2024.142079</pub-id>, <pub-id pub-id-type="pmid">38642771</pub-id></mixed-citation></ref>
<ref id="ref40"><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Zhuang</surname><given-names>M.</given-names></name> <name><surname>Sanganyado</surname><given-names>E.</given-names></name> <name><surname>Li</surname><given-names>P.</given-names></name> <name><surname>Liu</surname><given-names>W.</given-names></name></person-group> (<year>2019</year>). <article-title>Distribution of microbial communities in metal-contaminated nearshore sediment from eastern Guangdong, China</article-title>. <source>Environ. Pollut.</source> <volume>250</volume>, <fpage>482</fpage>&#x2013;<lpage>492</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envpol.2019.04.041</pub-id>, <pub-id pub-id-type="pmid">31026695</pub-id></mixed-citation></ref>
</ref-list>
<fn-group>
<fn fn-type="custom" custom-type="edited-by" id="fn0001">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1525684/overview">Lorenzo Antonio Picos Corrales</ext-link>, Universidad Aut&#x00F3;noma de Sinaloa, Mexico</p>
</fn>
<fn fn-type="custom" custom-type="reviewed-by" id="fn0002">
<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2779652/overview">Sadashiv Chaturvedi</ext-link>, Nanjing University of Information Science and Technology, China</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3298331/overview">Ana M. Morales-Burgos</ext-link>, Universidad Aut&#x00F3;noma de Sinaloa, Mexico</p>
</fn>
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</article>