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<journal-id journal-id-type="publisher-id">Front. Environ. Sci.</journal-id>
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<journal-title>Frontiers in Environmental Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Environ. Sci.</abbrev-journal-title>
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<issn pub-type="epub">2296-665X</issn>
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<article-id pub-id-type="publisher-id">1730654</article-id>
<article-id pub-id-type="doi">10.3389/fenvs.2025.1730654</article-id>
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<subject>Original Research</subject>
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<title-group>
<article-title>Bridging traditional and conventional knowledge for soil classification in landslide-prone areas using exploratory factor analysis</article-title>
<alt-title alt-title-type="left-running-head">Sankhyan et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fenvs.2025.1730654">10.3389/fenvs.2025.1730654</ext-link>
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<name>
<surname>Sankhyan</surname>
<given-names>Sahil</given-names>
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<sup>1</sup>
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<name>
<surname>Uday</surname>
<given-names>K. V.</given-names>
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<sup>2</sup>
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<name>
<surname>Dutt</surname>
<given-names>Varun</given-names>
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<sup>1</sup>
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<aff id="aff1">
<label>1</label>
<institution>ACS Lab, Indian Institute of Technology Mandi</institution>, <city>Mandi</city>, <state>Himachal Pradesh</state>, <country country="IN">India</country>
</aff>
<aff id="aff2">
<label>2</label>
<institution>Geohazard Studies Laboratory, Indian Institute of Technology Kamand</institution>, <city>Mandi</city>, <state>Himachal Pradesh</state>, <country country="IN">India</country>
</aff>
<author-notes>
<corresp id="c001">
<label>&#x2a;</label>Correspondence: Varun Dutt, <email xlink:href="mailto:varun@iitmandi.ac.in">varun@iitmandi.ac.in</email>
</corresp>
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<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-01-06">
<day>06</day>
<month>01</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2025</year>
</pub-date>
<volume>13</volume>
<elocation-id>1730654</elocation-id>
<history>
<date date-type="received">
<day>24</day>
<month>10</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>01</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>05</day>
<month>12</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Sankhyan, Uday and Dutt.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Sankhyan, Uday and Dutt</copyright-holder>
<license>
<ali:license_ref start_date="2026-01-06">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>
<sec>
<title>Introduction</title>
<p>Understanding soil movement and landslide susceptibility requires accurate soil classification. Traditional knowledge (TK) from ancient Indian texts describes soil color, texture, smell, and taste as key indicators, yet such qualitative insights remain underutilized in modern geotechnical assessments.</p>
</sec>
<sec>
<title>Methods</title>
<p>A questionnaire comprising 32 TK-based soil characteristics (color, texture, smell, taste) was developed and applied by 12 experts across 55 landslide-prone sites in Himachal Pradesh, India. Soil samples were also collected for laboratory-based geotechnical testing. Exploratory Factor Analyses (EFA) were conducted on TK-only, geotechnical-only, and combined datasets to identify latent soil categories and compare their explanatory power.</p>
</sec>
<sec>
<title>Results</title>
<p>Three principal soil categories earthy, coarse-grained, and fine-grained were identified. Retained factors explained 65.17%, 68.32%, and 71.46% of total variance for TK, geotechnical, and combined datasets, respectively. Expert discipline and educational background significantly influenced soil categorization, particularly in the fine-grained and coarse-grained groups.</p>
</sec>
<sec>
<title>Discussion</title>
<p>Integrating traditional and modern indicators enhances soil classification accuracy and provides a cost-effective framework for assessing landslide susceptibility in Himalayan regions. TK-based soil descriptors, when combined with quantitative geotechnical data, offer a holistic approach to slope stability analysis and risk mitigation.</p>
</sec>
</abstract>
<kwd-group>
<kwd>exploratory factor analysis</kwd>
<kwd>landslides</kwd>
<kwd>soil classification</kwd>
<kwd>traditional knowledge</kwd>
<kwd>soil color</kwd>
<kwd>soil smell</kwd>
<kwd>soil texture</kwd>
<kwd>soil stability</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This work was supported by the Indian Institute of Technology Mandi, who provided the necessary financial and computational resources for this experiment. Also, this project was partially supported by a grant from the national mission on Himalayan studies (IITM/NMHS-MoEF/VD/499) to VD.</funding-statement>
</funding-group>
<counts>
<fig-count count="4"/>
<table-count count="12"/>
<equation-count count="0"/>
<ref-count count="71"/>
<page-count count="18"/>
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<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Soil Processes</meta-value>
</custom-meta>
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</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<title>Introduction</title>
<p>Landslides pose significant global risks, threatening lives, infrastructure, and ecosystems, particularly in geologically unstable regions (<xref ref-type="bibr" rid="B70">Wang et al., 2022</xref>). In India, steep slopes, diverse topography, and complex soil composition, especially in the Himalayan region, contribute to frequent landslides (<xref ref-type="bibr" rid="B58">Singh and Pandey, 2024</xref>). The region&#x2019;s heavy monsoonal rainfall, tectonic activity, and unstable soil composition necessitate improved risk-management strategies (<xref ref-type="bibr" rid="B58">Singh and Pandey, 2024</xref>). Understanding soil properties such as permeability, shear strength, and composition is crucial for assessing slope stability and enhancing landslide prediction models (<xref ref-type="bibr" rid="B51">Petley, 2012</xref>). Over the past 2&#xa0;decades, landslides have resulted in approximately 18,000 fatalities in India, underscoring the urgent need for robust soil-categorization frameworks to improve mitigation strategies (<xref ref-type="bibr" rid="B53">Ramesh et al., 2023</xref>). By incorporating region-specific soil properties, such frameworks can provide more precise risk assessments, ultimately reducing the impact of landslides in vulnerable areas (<xref ref-type="bibr" rid="B54">Ren and Ren, 2015</xref>).</p>
<p>Conventional geotechnical investigations employ laboratory testing, remote sensing, and machine learning models to assess soil properties and predict landslide risks (<xref ref-type="bibr" rid="B43">Mali et al., 2022</xref>). Advances such as LiDAR-based terrain mapping, GIS-based spatial modeling, and satellite imaging have significantly improved landslide prediction accuracy (<xref ref-type="bibr" rid="B12">Casagli et al., 2023</xref>). However, while these quantitative approaches provide precise geotechnical insights, they require expensive instrumentation and extensive field surveys, making them impractical for resource-limited regions (<xref ref-type="bibr" rid="B65">Uddin and Hassan, 2022</xref>). Additionally, these methods often overlook qualitative soil attributes such as color, texture, and smell, which have been historically used in traditional knowledge (TK) systems to assess soil stability (<xref ref-type="bibr" rid="B6">Arosio et al., 2009</xref>).</p>
<p>Despite advancements in geotechnical methodologies, the integration of traditional soil classification frameworks such as TK remains underexplored (<xref ref-type="bibr" rid="B15">Dearing et al., 2015</xref>). Existing frameworks lack a comprehensive approach that bridges the quantitative precision of conventional geotechnical methods with the qualitative richness of traditional knowledge, thereby limiting their applicability for cost-effective and rapid assessments in landslide-prone regions (<xref ref-type="bibr" rid="B25">Gupta and Satyam, 2024</xref>). This gap is particularly significant for the Himalayan region, where landslide risks result from the complex interplay of climate, topography, and human activity. Vrikshayurveda, an ancient Indian text attributed to Surapala (c. 1000 AD), provides detailed soil classifications based on observable characteristics such as color, moisture retention, fertility, and texture (<xref ref-type="bibr" rid="B45">Mishra, 2019</xref>). This text categorizes soils into three primary types: arid, marshy, and ordinary, each associated with specific properties influencing plant growth, water retention, and soil stability (<xref ref-type="bibr" rid="B36">Jallayu et al., 2024</xref>). Although Vrikshayurveda has traditionally been applied in agriculture, its principles can offer valuable insights for understanding soil behavior in dynamic landslide-prone environments (<xref ref-type="bibr" rid="B63">Srikanth et al., 2015</xref>). Unlike conventional geotechnical approaches that emphasize numerical thresholds for soil cohesion, plasticity, and permeability, Vrikshayurveda provides a qualitative assessment framework based on soil texture, color, and smell, which can serve as a rapid and cost-effective preliminary assessment tool in landslide-prone areas, particularly where terrain inaccessibility limits formal geotechnical testing (<xref ref-type="bibr" rid="B39">Kumar and Jigeesh, 2024</xref>; <xref ref-type="bibr" rid="B10">Beniwal et al., 2020</xref>). Traditional soil knowledge is deeply embedded in the community practices of agriculture, land use, and slope management (<xref ref-type="bibr" rid="B45">Mishra, 2019</xref>). These experiential assessments not only guide cropping and construction choices but also function as early indicators of slope instability in the region (<xref ref-type="bibr" rid="B63">Srikanth et al., 2015</xref>). Integrating such community-based understanding with geotechnical analyses enables participatory risk assessment, ensuring that local stakeholders who are most exposed to landslide hazards remain the central beneficiaries of this research. This synthesis aligns with the growing emphasis on the co-production of environmental knowledge for resilient mountain livelihoods.</p>
<p>Previous landslide risk assessment studies have predominantly relied on geotechnical, remote sensing, and GIS-based modeling techniques (<xref ref-type="bibr" rid="B36">Jallayu et al., 2024</xref>). While these methods provide high-resolution data for soil stability analysis, they often overlook traditional soil knowledge systems that have been used for centuries to evaluate soil behavior (<xref ref-type="bibr" rid="B61">Smith et al., 2021</xref>). By integrating TK-based soil classification with geotechnical parameters, this study developed a holistic soil categorization framework that bridges traditional and conventional knowledge systems to enhance landslide risk assessment methodologies. Studies in the Himalayan region have emphasized the importance of combining geotechnical and geomorphological factors with advanced spatial modeling for landslide risk assessment. GIS-based analyses and susceptibility mapping have been instrumental in identifying high-risk areas and improving hazard management strategies (<xref ref-type="bibr" rid="B28">Hassan et al., 2022</xref>). Recent research has advanced slope stability and susceptibility analysis through multi-criteria and machine-learning-based approaches, including slope mass rating (SMR) and GIS-integrated models (<xref ref-type="bibr" rid="B2">Abbasi et al., 2024</xref>; <xref ref-type="bibr" rid="B27">Hamedi et al., 2025</xref>). For instance, studies in Mandi district demonstrate that integrating spatial models with rainfall and slope data significantly improves risk identification accuracy (<xref ref-type="bibr" rid="B17">Dikshit et al., 2020</xref>). Similarly, rainfall-induced landslide studies in the Indian Himalayan region highlight the interactions among climate, soil, and geomorphology, underscoring the need for localized assessments (<xref ref-type="bibr" rid="B17">Dikshit et al., 2020</xref>). Similar studies have employed SVM and logistic regression methods to identify critical parameters influencing landslide-prone zones, underscoring the potential of data-driven frameworks that complement traditional knowledge systems (<xref ref-type="bibr" rid="B3">Ahadi and Rosta, 2024</xref>).</p>
<p>Advancements in geospatial modeling and soil stabilization techniques have further improved landslide risk management. Interpolation algorithms have provided critical insights into spatial variability in geotechnical properties (<xref ref-type="bibr" rid="B29">Hassan et al., 2023</xref>). Additionally, innovative soil stabilization techniques, such as the use of plaster of Paris kiln dust and potassium-rich ions for sodium-rich clays, have been effective in mitigating dispersive soil and internal erosion (<xref ref-type="bibr" rid="B29">Hassan et al., 2023</xref>). Similarly, fine marble dust has been explored as a solution for soil dispersion, with statistical evaluations further refining stabilization applications (<xref ref-type="bibr" rid="B35">Ijaz et al., 2023</xref>). These geotechnical approaches, when integrated with traditional soil classification systems, can enhance slope management strategies by offering a cost-effective and region-specific framework for landslide risk assessment. These methods, combined with geotechnical soil maps, support better slope management and disaster mitigation strategies (<xref ref-type="bibr" rid="B69">Wang and Nanehkaran, 2024</xref>). Prior research has examined how age and experience affect soil classification (<xref ref-type="bibr" rid="B18">Dornik et al., 2016</xref>). Combining expert knowledge with geographic object-based image analysis improves soil categorization accuracy (<xref ref-type="bibr" rid="B69">Wang and Nanehkaran, 2024</xref>). Specific expertise is also required to analyze soil spectral data (<xref ref-type="bibr" rid="B44">Marques et al., 2019</xref>).</p>
<p>However, conventional knowledge may differ from scientific classification in soil mapping (<xref ref-type="bibr" rid="B50">Pereira et al., 2017</xref>). Historical studies in Japan highlight the importance of geographical context and size in soil classification (<xref ref-type="bibr" rid="B30">Hirai and Hamazaki, 2004</xref>; <xref ref-type="bibr" rid="B24">Grinand et al., 2008</xref>; <xref ref-type="bibr" rid="B8">Baruck et al., 2016</xref>). Studies show experts&#x27; ages did not significantly impact their soil observations, so we hypothesize that soil observations are not affected by age (<xref ref-type="bibr" rid="B60">Slessarev et al., 2019</xref>). Integrating this knowledge with geotechnical and traditional attributes can enhance soil classification frameworks for landslide risk assessment. To achieve this, a questionnaire-based survey incorporating 32&#xa0;TK soil attributes (color, texture, smell, and moisture retention) was developed. These qualitative assessments were then compared against laboratory-tested geotechnical properties, such as cohesion, permeability, and plasticity, across 55 landslide sites in Himachal Pradesh. Using Exploratory Factor Analysis (EFA), distinct soil categories were identified that aligned with both TK classifications and conventional geotechnical findings, providing a statistically validated framework for landslide risk assessment. Additionally, this study investigated how expert background and education influence soil classification accuracy, addressing potential biases in soil assessment methodologies.</p>
<p>This study contributes to the growing discourse on integrating traditional ecological knowledge into contemporary scientific approaches. It provides a replicable model for rapid soil assessment in landslide-prone regions, particularly in areas where conventional laboratory-based methods may not be feasible (<xref ref-type="bibr" rid="B33">Hulathdoowage and Hadiwattage, 2022</xref>). These findings offer new perspectives on leveraging ancient wisdom for modern environmental risk management, emphasizing the importance of interdisciplinary approaches in landslide hazard mitigation. By systematically bridging traditional and geotechnical methods, this study enhances the predictive accuracy of landslide susceptibility assessments and offers policymakers practical tools for sustainable land use planning.</p>
<p>We begin by reviewing the literature on TK in soil and plant sciences. We then covered the procedures for gathering information from landslide sites and rating the information using a Likert scale. PCA, one-way analysis of variance (ANOVA), and EFA were used for data analysis. Finally, the factor analysis findings are presented and the component compositions for each type of soil are explained.</p>
</sec>
<sec sec-type="methods" id="s2">
<title>Methods</title>
<sec id="s2-1">
<title>Study area</title>
<p>The study was carried out in the Mandi geographical area, which is situated in Himachal Pradesh, India&#x2019;s mid-Himalayan region (see <xref ref-type="fig" rid="F1">Figure 1</xref>). Our research specifically concentrated on the region along the route that connects Mandi and Kamand; the coordinates of this area are from 76&#xb0;55&#x2032;54&#x2032;E to 76&#xb0;59&#x2032;42&#x2032;E and from 31&#xb0;42&#x2032;25&#xb0;N to 31&#xb0;46&#x2032;26&#xb0;N. The research area was situated between 850 and 1,250&#xa0;m above sea level. The frequent landslides in this area were the driving force behind our decision to research in Mandi (<xref ref-type="bibr" rid="B37">Kahlon et al., 2014</xref>). These landslide occurrences have sparked worries about the possible impact of precipitation, especially in a region where 1,380&#xa0;mm of precipitation falls on average annually (<xref ref-type="bibr" rid="B37">Kahlon et al., 2014</xref>). We determined that 55 places along the 25-km route in Mandi, Himachal Pradesh, were landslide-prone because they had recently had landslides. Two different kinds of data were gathered from the landslide areas for our investigation. There are two types of soil features: one is based on TK, and the other is geotechnical. Below are the specifics of both data collection methodologies.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Geographical location of the data collection sites in India. <bold>(A)</bold> Map of India, specifically highlighting the geographical location of Himachal Pradesh. <bold>(B)</bold> Map of Himachal Pradesh, highlighting Mandi District. <bold>(C)</bold> Locations within Mandi District from where the data were collected. The red dots represent the data collected from areas where landslides have occurred. The map was created using ArcGIS Pro version 3.2 (<ext-link ext-link-type="uri" xlink:href="https://www.esri.com/arcgis-blog/products/arcgis-pro/announcements/whats-new-in-arcgis-pro-3-2/">https://www.esri.com/arcgis-blog/products/arcgis-pro/announcements/whats-new-in-arcgis-pro-3-2/</ext-link>). In-built satellite and terrain maps were used as base layers, and the study area spans the coordinates 76&#xb0;55&#x2032;54&#x2032;E to 76&#xb0;59&#x2032;42&#x2032;E and 31&#xb0;42&#x2032;25&#xb0;N to 31&#xb0;46&#x2032;26&#xb0;N.</p>
</caption>
<graphic xlink:href="fenvs-13-1730654-g001.tif">
<alt-text content-type="machine-generated">Map divided into three parts. Panel A shows India with Himachal Pradesh highlighted. Panel B focuses on Himachal Pradesh&#x27;s boundaries. Panel C details a study area in Himachal Pradesh, marked with landslide locations near Mandi, indicated by small red triangles within the outlined region. Surrounding landmarks include Kullu, Hamirpur, Bilaspur, and Solan. A scale bar and compass are included.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s2-2">
<title>Experts</title>
<p>Twelve experts from a reputable university, aged 21&#x2013;33 years (mean &#x3d; 29, SD &#x3d; 2.8), participated in this study. All experts provided informed consent before their participation. Experts included a mix of geotechnical engineers, environmental scientists, and individuals with expertise in traditional soil classification methods such as TK. The experts held either master&#x2019;s or doctoral degrees and specialized in civil engineering, geotechnical engineering, and electronics and communication engineering. Seven experts had extensive research experience in geotechnical engineering and slope-stability analysis, whereas the remaining five had field experience in landslide risk assessment, soil mechanics, geomorphological analysis, and traditional soil classification techniques. Experts were selected based on the following criteria: (1) a minimum master&#x2019;s degree in geotechnical engineering, civil engineering, or other engineering disciplines; (2) research experience in landslide risk assessment and soil characterization; and (3) familiarity with traditional knowledge systems. Their combined academic and field experience facilitated the integration of conventional geotechnical assessments with TK-based soil classification, enabling a comprehensive analysis of soil-environment interactions. The experts conducted field assessments at 55 randomly selected landslide-prone sites and graded soils based on TK principles. The twelve experts evaluated distinct soil properties, including texture, color, and scent, and systematically recorded their observations using a structured questionnaire. To ensure consistency and minimize subjective bias, the assessments were conducted independently by each expert, and inter-rater reliability was analyzed to confirm agreement in soil classifications. This structured approach allowed for direct comparisons between conventional geotechnical features and traditional soil attributes, bridging the gap between conventional engineering assessments and TK soil categorization. Their collective expertise in both traditional and conventional soil characterization methods brought valuable perspectives to the study, allowing for a more comprehensive evaluation of soil properties and their implications for landslide susceptibility. By integrating traditional knowledge with conventional geotechnical assessments, this study highlighted the potential of TK as a complementary tool for rapid soil assessment in landslide-prone areas.</p>
</sec>
<sec id="s2-3">
<title>The geotechnical features</title>
<p>The soil samples from 55 locations were collected at a maximum depth of 0.5&#xa0;m along sloping surfaces for geotechnical analysis. Each sample included <italic>in situ</italic> moisture content, geographical coordinates, and recent landslide locations (<xref ref-type="bibr" rid="B68">Vogel et al., 2023</xref>). Soils were extracted by using a stainless-steel sampler (10&#xa0;cm diameter and 13&#xa0;cm in height) between 0.3 and 0.5&#xa0;m depths and with the help of a trowel for rocky strata, weighing approximately 40&#xa0;kg for each sample. The samples were analyzed in the laboratory for 16 geotechnical features such as <italic>in situ</italic> bulk density, <italic>in situ</italic> water content (wn), plasticity index, liquid and plasticity limits, saturation permeability, and more (<xref ref-type="bibr" rid="B7">ASTM Committee D-18 on Soil and Rock, 2009</xref>; <xref ref-type="bibr" rid="B5">American Society for Testing and Materials. Committee D18 on Soil and Rock, 2004</xref>; <xref ref-type="bibr" rid="B48">Nhantumbo and Cambule, 2006</xref>; <xref ref-type="bibr" rid="B47">Nguyen et al., 2022</xref>). In addition, the standard Proctor test was conducted to obtain optimum moisture content and dry density. Relative compaction was estimated by comparing <italic>in situ</italic> and laboratory dry density. The <italic>in situ</italic> density was used to compute the porosity. The geotechnical variables measured include gravel (%), sand (%), clay (%), silt (%), liquid limit, plastic limit, density, fine content (%), natural water content (%), specific gravity, and porosity (refer to <xref ref-type="table" rid="T1">Table 1</xref>).</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Geotechnical features and their minimum, maximum, mean values, and corresponding landslide susceptibility levels.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">S. No.</th>
<th colspan="2" align="center">Geotechnical feature</th>
<th align="center">Test standard</th>
<th align="center">Minimum value</th>
<th align="center">Maximum value</th>
<th align="center">Mean value</th>
<th align="center">Landslide susceptibility based on mean values</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">1</td>
<td colspan="2" align="left">Porosity</td>
<td align="left">ASTM 698-12E2</td>
<td align="left">44.8</td>
<td align="left">88</td>
<td align="left">66.6</td>
<td align="left">High</td>
</tr>
<tr>
<td align="left">2</td>
<td colspan="2" align="left">Fines content (%)</td>
<td align="left">ASTM-D422-63</td>
<td align="left">5</td>
<td align="left">75</td>
<td align="left">31.9</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">3</td>
<td colspan="2" align="left">Plastic limit (PL) (%)</td>
<td rowspan="3" align="left">ASTM D 4318-17e1</td>
<td align="left">4</td>
<td align="left">25</td>
<td align="left">15.9</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">4</td>
<td colspan="2" align="left">Liquid limit (LL) (%)</td>
<td align="left">8</td>
<td align="left">35</td>
<td align="left">24.4</td>
<td align="left">High</td>
</tr>
<tr>
<td align="left">5</td>
<td colspan="2" align="left">Plasticity index (PI) (%)</td>
<td align="left">3.70</td>
<td align="left">11.70</td>
<td align="left">8.34</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">6</td>
<td colspan="2" align="left">Saturated water content (%)</td>
<td align="left">ASTM D 2216&#x2013;19</td>
<td align="left">11.4</td>
<td align="left">16.8</td>
<td align="left">12.5</td>
<td align="left">High</td>
</tr>
<tr>
<td align="left">7</td>
<td colspan="2" align="left">Optimum moisture content</td>
<td align="left">ASTM D698</td>
<td align="left">8.5</td>
<td align="left">14.7</td>
<td align="left">10.3</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">8</td>
<td colspan="2" align="left">Sand (%)</td>
<td align="left">ASTM-D422-63</td>
<td align="left">21</td>
<td align="left">88</td>
<td align="left">52.4</td>
<td align="left">Low</td>
</tr>
<tr>
<td align="left">9</td>
<td colspan="2" align="left">Saturated unit weight</td>
<td align="left">ASTM D7263</td>
<td align="left">20.6</td>
<td align="left">21.8</td>
<td align="left">15.9</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">10</td>
<td colspan="2" align="left">Specific gravity</td>
<td align="left">ASTM D854</td>
<td align="left">2.5</td>
<td align="left">2.6</td>
<td align="left">2.6</td>
<td align="left">Low</td>
</tr>
<tr>
<td align="left">11</td>
<td colspan="2" align="left">Gravel (%)</td>
<td align="left">ASTM-D422-63</td>
<td align="left">0</td>
<td align="left">65</td>
<td align="left">14.8</td>
<td align="left">Low</td>
</tr>
<tr>
<td align="left">12</td>
<td rowspan="4" align="left">Particle sizes</td>
<td align="left">D10</td>
<td rowspan="4" align="left">ASTM-D422-63</td>
<td align="left">0.0</td>
<td align="left">0.7</td>
<td align="left">0.4</td>
<td align="left">Low</td>
</tr>
<tr>
<td align="left">13</td>
<td align="left">D30</td>
<td align="left">0.05</td>
<td align="left">2.8</td>
<td align="left">1.6</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">14</td>
<td align="left">D50</td>
<td align="left">0.0</td>
<td align="left">3.2</td>
<td align="left">2.2</td>
<td align="left">Moderate</td>
</tr>
<tr>
<td align="left">15</td>
<td align="left">D60</td>
<td align="left">2.5</td>
<td align="left">2.6</td>
<td align="left">2.3</td>
<td align="left">Low</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>We performed a Pearson&#x2019;s correlation analysis to establish the strength of relationships between traditional soil characteristics of color, texture, smell, and taste and geotechnical properties of moisture content, density, and gravel content. Correlations were considered statistically significant using a two-tailed test of significance at <italic>p</italic> &#x3c; 0.05. Strong correlations, <italic>r</italic> &#x2265; 0.5, were expected to confirm how well the traditional and conventional soil categorizations agreed. For example, we predicted that brown soil would correlate positively with density and moisture content, indicating compactness, while white soils, which are loosely structured, would negatively correlate with gravel content.</p>
<p>To further interpret the contribution of soil to slope instability, we used established literature thresholds and mean values observed in our dataset to qualitatively categorize the landslide susceptibility of each geotechnical feature as low, moderate, and high.</p>
<p>Soils with high porosity of more than 60% have lower particle packing and higher void ratios; hence, they are more susceptible to increase in water infiltration and pore pressure accumulation, which is a critical precursor to slope failure under rainfall conditions. With a mean porosity of 66.6%, these soils thus fall in the category of having high landslide susceptibility (<xref ref-type="bibr" rid="B52">Rahardjo et al., 2007</xref>; <xref ref-type="bibr" rid="B57">Sidle and Ochiai, 2006</xref>).</p>
<p>Fines content close to 32% represents a transitional soil system of silt and clay that retains water but without the cohesion attributed to high-clay content soil. Consequently, such soils are moderately susceptible to instability, especially under wet-dry cycles and gravitational loading (<xref ref-type="bibr" rid="B64">Thevanayagam, 1998</xref>).</p>
<p>A plastic limit of &#x223c;16% would indicate that the soil changes from semi-solid to plastic behavior at a moderate level of moisture. These soils have a tendency to show reduced shear strength under increasing saturation and, therefore, moderate susceptibility (<xref ref-type="bibr" rid="B66">Van Westen et al., 2008</xref>).</p>
<p>The liquid limit of 24.4% falls within the range typically associated with soil softening under rainfall and seismic triggers, thus classified as high susceptibility. Clays with LL &#x3e;20% have been linked to reduced stability during extreme hydrological events (<xref ref-type="bibr" rid="B67">Varnes, 1958</xref>).</p>
<p>Plasticity index values of 8%&#x2013;12% represent transition soils that are neither excessively plastic nor brittle. Accordingly, they are moderately susceptible to deformation by the action of applied external stressors (<xref ref-type="bibr" rid="B59">Skempton, 1953</xref>).</p>
<p>An average saturated water content of 12.5% indicates that these soils are capable of developing high moisture retention, with an associated gain in weight and loss of matric suction, which may well increase the potential for slope failure under sustained rainfall. It is considered to be of high susceptibility (<xref ref-type="bibr" rid="B21">Fredlund and Rahardjo, 1993</xref>).</p>
<p>While optimum moisture content at 10.3% also indicates moderate risk, it is favorable for compaction in dry conditions, but saturation beyond this point can destabilize the soil matrix and increase landslide risk (<xref ref-type="bibr" rid="B14">Das and Sobhan, 2006</xref>).</p>
<p>A sand content over 50% improves permeability normally and enables good drainage, hence a minimal development of pore pressure. Since the mean sand content is 52.4%, these soils are to be classified as having low susceptibility (<xref ref-type="bibr" rid="B11">Bishop, 1955</xref>).</p>
<p>Saturated unit weight of 15.9&#xa0;kN/m<sup>3</sup> indicates moderately dense soils, which, when saturated, may develop considerable driving forces downslope and justify a moderate risk classification (<xref ref-type="bibr" rid="B14">Das and Sobhan, 2006</xref>).</p>
<p>A specific gravity of 2.6 corresponds to a stable silicate mineralogy with coarse fractions, which indicates structural resistance and effective drainage. This corresponds to low susceptibility according to (<xref ref-type="bibr" rid="B14">Das and Sobhan, 2006</xref>).</p>
<p>Gravel content contributes to macro-porosity and facilitates drainage, lowering water retention and pore pressure accumulation, with a mean of 14.8%. Consequently, these soils are rated as low susceptibility (<xref ref-type="bibr" rid="B41">Macciotta and Hendry, 2021</xref>). Particle size parameters: D10 &#x3d; 0.4&#xa0;mm and D60 &#x3d; 2.3&#xa0;mm indicate that the well-graded soil allows for good compaction, reducing the risks of internal erosion, hence supporting low susceptibility. On the other hand, D30 &#x3d; 1.6&#xa0;mm and D50 &#x3d; 2.2&#xa0;mm indicate intermediate grading, which may show some sensitivity under stress and hence are rated as moderate susceptibility according to USDA Soil Survey (<xref ref-type="bibr" rid="B23">Garc and Frankenstein, 2015</xref>). Hence, the susceptibility classification in <xref ref-type="table" rid="T1">Table 1</xref> integrates these parameter thresholds and their known geomaterial behaviors to qualitatively indicate the relative potential for landslide initiation in the study area. This context strengthens the engineering geological relevance of the dataset by relating lab-measured soil properties to field-observed landslide patterns in a Himalayan terrain dominated by colluvial and weathered metamorphic formations.</p>
</sec>
<sec id="s2-4">
<title>Survey questionnaire</title>
<p>A structured questionnaire was developed based on the principles of traditional soil classification to gather expert evaluations and quantifiable data (see <xref ref-type="table" rid="T2">Table 2</xref>). As shown in <xref ref-type="table" rid="T2">Table 2</xref>, the questionnaire assessed soil properties, including soil color (e.g., red, white, yellow), smell (e.g., earthy and musty), texture (e.g., stickiness, smoothness), and taste (e.g., sweetness and saltiness), using a 5-point Likert scale (&#x2b;2 &#x3d; significant agreement, &#x2b;1 &#x3d; agreement, 0 &#x3d; neutrality, &#x2212;1 &#x3d; disagreement, &#x2212;2 &#x3d; significant disagreement) for standardized expert responses (<xref ref-type="bibr" rid="B4">Alabi and Jelili, 2023</xref>; <xref ref-type="bibr" rid="B62">South et al., 2022</xref>; <xref ref-type="bibr" rid="B38">Kumar and Brijesh, 2023</xref>). The 32 questions included in the questionnaire were carefully selected following a comprehensive review of the traditional texts and contemporary literature on soil properties. Experts in geotechnical engineering and environmental science evaluated the relevance of each question to ensure alignment with both the traditional and conventional soil classification methods. For more details on the questionnaire, refer to the <xref ref-type="sec" rid="s12">Supplementary Material</xref>.</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Traditional features and their minimum, maximum, and mean values.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Traditional features</th>
<th align="center">Minimum value</th>
<th align="center">Maximum value</th>
<th align="center">Mean value</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Color of the soil</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Red</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.6</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Brown</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;1.8</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Black</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;2.7</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;4.&#x2003;White</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;4.&#x2003;2.1</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;5.&#x2003;Green</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;5.&#x2003;1.7</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;6.&#x2003;Yellow</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;6.&#x2003;2.3</td>
</tr>
<tr>
<td align="left">Content</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Sand</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.6</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Silt</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;2.9</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Gravel</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;3.2</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;4.&#x2003;Clay</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;4.&#x2003;2.4</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;5.&#x2003;Rocks &#x26; debris</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;5.&#x2003;3.4</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;6.&#x2003;Coarseness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;6.&#x2003;3.3</td>
</tr>
<tr>
<td align="left">Related to water</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Retention</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.3</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Drainage</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;3.4</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Moisture</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;3.3</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;4.&#x2003;Dryness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;4.&#x2003;2.7</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;5.&#x2003;Hardness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;5.&#x2003;2.9</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;6.&#x2003;Smoothness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;6.&#x2003;2.8</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;7.&#x2003;Density</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;7.&#x2003;3.1</td>
</tr>
<tr>
<td align="left">Smell</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Earthy</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.6</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Musty</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;2.6</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Faul</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;1.8</td>
</tr>
<tr>
<td align="left">Taste</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Sweetness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.1</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Saltness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;2.9</td>
</tr>
<tr>
<td align="left">Fertility</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Fertile</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;3.8</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Plant health</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;3.9</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Deforestation</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;2.5</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;4.&#x2003;Vegetation cover</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;4.&#x2003;3.9</td>
</tr>
<tr>
<td align="left">Field test</td>
<td align="center">1</td>
<td align="center">5</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;1.&#x2003;Stickiness</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;1.&#x2003;2.9</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;2.&#x2003;Crumbling</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;2.&#x2003;3.3</td>
</tr>
<tr>
<td align="left">&#x2003;&#x2003;3.&#x2003;Clump</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="left">&#x2003;&#x2003;3.&#x2003;3.4</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Before the main data collection, a calibration session was conducted with all the participating experts to standardize the interpretation of qualitative descriptors, such as color, smell, taste, and texture. Experts were trained on how to assign ratings using the five-point Likert scale (&#x2212;2 to &#x2b;2) and were shown representative soil samples (black, white, and brown) to achieve a consensus on interpretation. This session ensured that the qualitative evaluations were harmonized across experts. To validate the questionnaire, two geotechnical experts independently reviewed the 32 questions for clarity, relevance, and comprehensiveness before full implementation. Each question was rated for validity and consistency using a 5-point Likert scale, and the inter-rater reliability was assessed using Cronbach&#x2019;s alpha, which was computed as 0.86, indicating a high level of agreement among experts. Additionally, Cronbach&#x2019;s alpha for the full dataset of 660 responses across 32 items was 0.77, further confirming the reliability of the questionnaire. This validation process ensured that the questionnaire effectively captured the intended soil characteristics while maintaining consistency in the expert assessments.</p>
<p>Experts administered the questionnaire at randomly selected landslide-prone sites to evaluate soil fertility, moisture content, water retention, drainage capacity, stickiness, hardness, and disturbance response. The effects of vegetation cover on soil stability were also analyzed. Soil color was noted to assess both organic and mineral components, providing insight into soil composition. These expert evaluations, guided by structured criteria, ensure consistency across assessments and enable objective comparisons between soil samples.</p>
<p>The structured questionnaire provided a standardized framework for evaluating soil characteristics, enabling comparisons across diverse landslide-prone sites, while minimizing variability in expert assessments. Given the challenges of conducting direct measurements in remote locations, the questionnaire facilitates an efficient and field-adaptable method for soil classification. This approach also incorporates diverse disciplinary perspectives, as experts from geotechnical, and civil engineering backgrounds apply a consistent evaluation framework to the same soil samples.</p>
</sec>
<sec id="s2-5">
<title>Data analyses</title>
<p>All statistical analyses were performed using SPSS software (<xref ref-type="bibr" rid="B34">IBM Corp, 2016</xref>). To determine the suitability of the data for factor analysis, the Kaiser-Meyer-Olkin (KMO) measure of sampling adequacy and Bartlett&#x2019;s Test of Sphericity were employed (<xref ref-type="bibr" rid="B26">Gupta and Shukla, 2018</xref>). The KMO measure assesses the proportion of variance among variables that might be a common variance, indicating the appropriateness of factor analysis. A KMO value above 0.5 was considered acceptable for proceeding with Exploratory factor analysis (EFA) (<xref ref-type="bibr" rid="B52">Rahardjo et al., 2007</xref>). Bartlett&#x2019;s Test of Sphericity tests the null hypothesis that the correlation matrix is an identity matrix, which would indicate that variables are unrelated and unsuitable for structure detection. A significant result (p &#x3c; 0.05) from Bartlett&#x2019;s test suggests that there are adequate relationships among variables for factor analysis (<xref ref-type="bibr" rid="B26">Gupta and Shukla, 2018</xref>). All traditional knowledge (TK) descriptors were transformed into numeric values using a five-point Likert scale (&#x2212;2 to &#x2b;2), representing the ordered intensity of each sensory attribute. These ordinal scores were treated as quasi-interval data, suitable for multivariate analysis. Significant correlations (<italic>r</italic> &#x2265; 0.3, <italic>p</italic> &#x3c; 0.05) confirmed that the Likert scale transformations captured meaningful gradations in soil properties. The suitability of the transformed three datasets for factor analysis was further verified using KMO (&#x3e;0.7) and Bartlett&#x2019;s test (<italic>p</italic> &#x3c; 0.01).</p>
<p>To minimize inter-rater bias among experts with different disciplinary and educational backgrounds, individual questionnaire scores were recorded independently and later aggregated using the mean Likert value for each descriptor. This approach reduces individual influence while preserving the collective trend. Before data collection, a calibration session was held with all experts to standardize the rating criteria and align the interpretation of qualitative descriptors, functioning similarly to the Delphi-style consensus process.</p>
<p>The EFA was executed using Principal Component Analysis (PCA) for factor extraction, followed by varimax rotation to achieve a clearer factor structure (<xref ref-type="bibr" rid="B19">Dziuban and Shirkey, 1974</xref>). EFA was executed using Principal Component Analysis (PCA) for factor extraction, followed by varimax rotation to achieve a clearer factor structure. The stability of the extracted factors was evaluated by comparing the loading patterns obtained from the traditional, geotechnical, and combined datasets. The factors consistently aligned with the same soil categories (fine-grained, coarse-grained, and earthy), confirming the stable structural relationships. The internal consistency of each factor was verified using Cronbach&#x2019;s alpha, which ranged from 0.75 to 0.86. Given the moderate sample size, confirmatory factor analysis (CFA) was deferred to future studies with larger datasets. The EFA was chosen for its ability to identify latent constructs and relationships within the dataset, which included both traditional and geotechnical soil properties (<xref ref-type="bibr" rid="B26">Gupta and Shukla, 2018</xref>). This method is particularly suitable for datasets in which multiple variables are expected to be grouped into distinct underlying factors, such as fine-grained, coarse-grained, and earthy soil categories (<xref ref-type="bibr" rid="B26">Gupta and Shukla, 2018</xref>). The traditional feature-based dataset consists of 660 data points derived from expert evaluations across 55 landslide sites (with twelev experts assessing each site). The geotechnical features dataset, on the other hand, comprised 55 laboratory analyzed soil samples collected from these same sites. In addition, the sample size met the recommended thresholds for EFA, ensuring the reliability of the extracted factors. By uncovering the underlying structure of soil properties, EFA allows for the development of a robust soil categorization framework that effectively integrates traditional and geotechnical characteristics.</p>
<p>The eigenvalues represent the amount of variance explained by each factor (<xref ref-type="bibr" rid="B56">Shrestha, 2021</xref>). Following the Kaiser Criterion, factors with eigenvalues greater than 1.0 were considered significant, as these factors explain more variance than an individual variable (<xref ref-type="bibr" rid="B71">Yong and Pearce, 2013</xref>). However, the ultimate threshold for retention was the cumulative variance explained by these factors. For each dataset, only the factors that collectively explained greater than 55% of the total variance were retained. Scree plots were also used to visually confirm the number of retained factors (<xref ref-type="bibr" rid="B31">Howard, 2016</xref>). This combined approach ensures that the retained factors meaningfully contribute to the overall explanatory power of the analysis, while minimizing noise.</p>
<p>Next, one-way ANOVA was used to explore the potential impacts of soil factors identified by EFA and to investigate the differences in factor scores among the demographic and expert groups, focusing on age and expertise level (education level and discipline) (<xref ref-type="bibr" rid="B9">Belkhiri and Narany, 2015</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>Results</title>
<sec id="s3-1">
<title>Correlation analyses</title>
<p>The results revealed several significant correlations, highlighting the interdependencies among soil color, composition, water retention, and geotechnical properties. Brown soil showed a significant positive correlation with rocks and debris (<italic>r</italic> (658) &#x3d; 0.112, <italic>p</italic> &#x3c; 0.05) and density (<italic>r</italic> (658) &#x3d; 0.351, <italic>p</italic> &#x3c; 0.01), suggesting that denser soils with rock fragments tended to exhibit brown coloration, which may indicate higher compaction levels. In contrast, white soils were positively correlated with silt content (<italic>r</italic> (658) &#x3d; 0.267, <italic>p</italic> &#x3c; 0.01) and negatively correlated with gravel content (<italic>r</italic> (658) &#x3d; &#x2212;0.202, <italic>p</italic> &#x3c; 0.01), indicating that soils with high silt proportions and fewer coarse particles appear lighter in color. Soil water retention exhibited a strong positive correlation with earthy soil smell (<italic>r</italic> (658) &#x3d; 0.483, <italic>p</italic> &#x3c; 0.01) and moisture content (<italic>r</italic> (658) &#x3d; 0.617, <italic>p</italic> &#x3c; 0.01) but was negatively correlated with sand content (<italic>r</italic> (658) &#x3d; &#x2212;0.417, <italic>p</italic> &#x3c; 0.01). These results suggest that soils with high organic content and finer particles tend to retain more water, whereas sandy soils drain moisture more rapidly. The specific gravity was significantly correlated with cohesion (<italic>r</italic> (658) &#x3d; 0.521, <italic>p</italic> &#x3c; 0.01), supporting the notion that denser soils tend to have stronger particle bonding and higher shear resistance. Stickiness was positively correlated with silt content (<italic>r</italic> (658) &#x3d; 0.352, <italic>p</italic> &#x3c; 0.01), suggesting that fine-grained soils exhibited greater plasticity and cohesion, reinforcing their vulnerability to landslides under wet conditions. Additionally, silt content was strongly correlated with the plasticity index (<italic>r</italic> (658) &#x3d; 0.239, <italic>p</italic> &#x3c; 0.01), reinforcing the importance of fine-grained soils in determining soil deformation characteristics. Soil drainage exhibited a strong positive correlation with soil density (<italic>r</italic> (658) &#x3d; 0.432, <italic>p</italic> &#x3c; 0.01), indicating that denser soils may exhibit better compaction and structural stability, and reduce permeability. Smoothness was significantly positively correlated with the sweet taste of soil (<italic>r</italic> (658) &#x3d; 0.137, <italic>p</italic> &#x3c; 0.01), which aligns with the presence of certain mineral compositions possibly linked to organic-rich soils. Additionally, vegetation cover was negatively correlated with soil thickness (<italic>r</italic> (658) &#x3d; &#x2212;0.276, <italic>p</italic> &#x3c; 0.01), implying that thicker soil layers may have lower vegetation cover owing to potential instability or poor nutrient retention. Soil clumping was positively associated with the average internal friction (<italic>r</italic> (658) &#x3d; 0.256, <italic>p</italic> &#x3c; 0.01), indicating that well-aggregated soils may resist shear forces more effectively.</p>
</sec>
<sec id="s3-2">
<title>Exploratory factor analysis of traditional features</title>
<p>Using the questionnaire, twelve experts assessed each of the 55 locations, generating a total of 660 responses. An EFA was performed on these 660 responses, and the results are presented in <xref ref-type="table" rid="T3">Table 3</xref> (<xref ref-type="bibr" rid="B46">Mvududu and Sink, 2013</xref>). Before conducting EFA, the suitability of the data was assessed. The KMO measure of sampling adequacy was 0.897, which confirmed that the sample size was appropriate. Bartlett&#x2019;s Test of Sphericity was significant (&#x3c7;<sup>2</sup> &#x3d; 2,137.6, <italic>p</italic> &#x3c; 0.01), suggesting that the dataset exhibited sufficient intercorrelations for factor extraction. PCA was employed for factor extraction, initially identifying four factors. However, factors that explained less than 55% of the total variance were excluded, resulting in three retained factors. KVN rotation was applied to optimize factor separation. <xref ref-type="fig" rid="F2">Figure 2</xref> shows the scree plot, where the eigenvalues dropped sharply after the third factor, confirming the retention of the three dominant factors. The final model retained three factors, which explained 65.17% of the total variance. The eigenvalues were 4.8, 4.7, and 3.8, corresponding to fine-grained soil (Factor 1), coarse-grained soil (Factor 2), and earthy soil (Factor 3), respectively, as detailed in <xref ref-type="table" rid="T3">Table 3</xref>. The factor loadings ranged from 0.504 to 0.838, while communalities varied between 0.294 and 0.926 (<xref ref-type="table" rid="T4">Table 4</xref>), indicating strong associations among the extracted variables. To interpret the retained factors, factor loadings were analyzed to identify the dominant soil characteristics. Factor 1, representing fine-grained soil, showed high loadings for variables such as clay content, black color, and water retention, which aligns with traditional classification of moisture-retentive and fertile soils. Factor 2, associated with coarse-grained soils, included high loadings for sand content, gravel, and coarseness, confirming the alignment with well-drained, low-cohesion traditional soil descriptions. Factor 3, representing earthy soils, exhibited high loadings for brown color and earthy smell, reinforcing its classification as an organic-rich soil with moderate cohesion.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Extraction of three factors from EFA traditional features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor</th>
<th align="center">Eigenvalue (rotated)</th>
<th align="center">% of variance (rotated)</th>
<th align="center">Cumulative % of variance (rotated)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">1</td>
<td align="center">4.8</td>
<td align="center">22.14</td>
<td align="center">22.14</td>
</tr>
<tr>
<td align="center">2</td>
<td align="center">4.7</td>
<td align="center">20.14</td>
<td align="center">43.01</td>
</tr>
<tr>
<td align="center">3</td>
<td align="center">3.8</td>
<td align="center">16.91</td>
<td align="center">65.17</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Scree plot for the traditional dataset.</p>
</caption>
<graphic xlink:href="fenvs-13-1730654-g002.tif">
<alt-text content-type="machine-generated">Scree plot showing eigenvalues on the y-axis and component numbers on the x-axis from one to twenty-four. The plot depicts a steep decline in eigenvalues from component one to six, followed by a gradual leveling off from component seven onward.</alt-text>
</graphic>
</fig>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Factors and communality loadings of traditional features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Item</th>
<th align="center">Factor 1</th>
<th align="center">Factor 2</th>
<th align="center">Factor 3</th>
<th align="center">Communalities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Clay content</td>
<td align="center">0.926</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.691</td>
</tr>
<tr>
<td align="center">Silt content</td>
<td align="center">0.789</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.660</td>
</tr>
<tr>
<td align="center">Black color</td>
<td align="center">0.773</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.653</td>
</tr>
<tr>
<td align="center">Water retention</td>
<td align="center">0.740</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.550</td>
</tr>
<tr>
<td align="center">Moisture</td>
<td align="center">0.725</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.539</td>
</tr>
<tr>
<td align="center">High fertility</td>
<td align="center">0.659</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.473</td>
</tr>
<tr>
<td align="center">Musty smell</td>
<td align="center">0.653</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.519</td>
</tr>
<tr>
<td align="center">Stickiness</td>
<td align="left">&#x200b;</td>
<td align="center">0.797</td>
<td align="left">&#x200b;</td>
<td align="center">0.759</td>
</tr>
<tr>
<td align="center">Sand content</td>
<td align="left">&#x200b;</td>
<td align="center">0.728</td>
<td align="left">&#x200b;</td>
<td align="center">0.689</td>
</tr>
<tr>
<td align="center">Gravel content</td>
<td align="left">&#x200b;</td>
<td align="center">0.684</td>
<td align="left">&#x200b;</td>
<td align="center">0.527</td>
</tr>
<tr>
<td align="center">Rocks &#x26; debris</td>
<td align="left">&#x200b;</td>
<td align="center">0.651</td>
<td align="left">&#x200b;</td>
<td align="center">0.650</td>
</tr>
<tr>
<td align="center">Yellow color</td>
<td align="left">&#x200b;</td>
<td align="center">0.608</td>
<td align="left">&#x200b;</td>
<td align="center">0.411</td>
</tr>
<tr>
<td align="center">White color</td>
<td align="left">&#x200b;</td>
<td align="center">0.602</td>
<td align="left">&#x200b;</td>
<td align="center">0.392</td>
</tr>
<tr>
<td align="center">Coarseness</td>
<td align="left">&#x200b;</td>
<td align="center">0.588</td>
<td align="left">&#x200b;</td>
<td align="center">0.390</td>
</tr>
<tr>
<td align="center">Easy to crumble</td>
<td align="left">&#x200b;</td>
<td align="center">0.552</td>
<td align="left">&#x200b;</td>
<td align="center">0.354</td>
</tr>
<tr>
<td align="center">Healthy plants</td>
<td align="left">&#x200b;</td>
<td align="center">0.527</td>
<td align="left">&#x200b;</td>
<td align="center">0.540</td>
</tr>
<tr>
<td align="center">High-water drainage</td>
<td align="left">&#x200b;</td>
<td align="center">0.504</td>
<td align="left">&#x200b;</td>
<td align="center">0.294</td>
</tr>
<tr>
<td align="center">Earthy smell</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.853</td>
<td align="center">0.735</td>
</tr>
<tr>
<td align="center">Brown color</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.838</td>
<td align="center">0.814</td>
</tr>
<tr>
<td align="center">Low water retention</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.596</td>
<td align="center">0.405</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-3">
<title>Traditional knowledge-based soil classification and correlations</title>
<p>Fine-grained soils included clay, silt, black color, high water retention, moisture content, high fertility, and a musty smell (<xref ref-type="table" rid="T5">Table 5</xref>). These attributes align with TK descriptions of fertile and moisture-retentive soils that support plant growth, but may experience stability issues under saturation. Coarse-grained soils comprised sand, gravel, rocks, debris, yellow and white colors, coarseness, easy crumbling, stickiness, healthy plants, and high-water drainage (<xref ref-type="table" rid="T3">Table 3</xref>). The presence of yellow and white coloration in conjunction with coarse particles suggests that these soils are well drained and prone to surface erosion rather than deep-seated movement. Earthy soils are characterized by a brown color, earthy smell, and moderate water retention. The significant correlation between earthy smell and water retention (<italic>r</italic> (658) &#x3d; 0.483, <italic>p</italic> &#x3c; 0.01) applies specifically to earthy soils, reinforcing their classification as moderately moisture-retentive with respect to organic content (<xref ref-type="table" rid="T5">Table 5</xref>). This classification aligns with TK description of ordinary soils that exhibit moderate stability but require external reinforcement for sustained fertility and structure. These findings validate the alignment between traditional soil classifications and conventional geotechnical assessments, demonstrating that qualitative attributes, such as color, smell, and texture, are strongly associated with measurable soil properties.</p>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>Composition of the extracted factors of traditional features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor name</th>
<th align="center">Composition of factor</th>
<th align="center">Significant correlations</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Fine-grained soil</td>
<td align="center">Clay, silt, black color, high water retention, moisture content, high fertility, and musty smell</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="center">Coarse-grained soil</td>
<td align="center">Sand, gravel, rocks and debris, yellow color, white color, coarseness, easy to crumble<break/>Stickiness, healthy plants and high-water drainage</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="center">Earthy soil</td>
<td align="center">Earthy smell, Brown color, and water retention</td>
<td align="left">Earthy smell with water retention (<italic>r</italic> (658) &#x3d; 0.483, <italic>p</italic> &#x3c; 0.01)</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-4">
<title>Exploratory factor analysis of geotechnical features</title>
<p>The geotechnical characteristics of the soil samples were analyzed using EFA on 55 laboratory test results to identify the significant underlying factors (<xref ref-type="bibr" rid="B46">Mvududu and Sink, 2013</xref>). The extraction results are summarized in <xref ref-type="table" rid="T6">Table 6</xref>. PCA was employed for factor extraction, with a KMO measure of sampling adequacy of 0.506, confirming that the sample size was acceptable for the factor analysis. Bartlett&#x2019;s Test of Sphericity was significant (&#x3c7;<sup>2</sup> &#x3d; 462.3, <italic>p</italic> &#x3c; 0.01), indicating that the correlation matrix was not an identity matrix and that factor analysis was appropriate. Factors that explained greater than 55% of the total variance were retained. The EFA of the geotechnical dataset identified three factors that explained a cumulative variance of 68.32%. KVN rotation was applied to improve factor interpretability (<xref ref-type="table" rid="T6">Table 6</xref>). <xref ref-type="fig" rid="F3">Figure 3</xref> illustrates the scree plot, which demonstrates a significant decline in eigenvalues after the third factor, thus supporting the three-factor solution. The three extracted factors were classified as fine-grained, coarse-grained, and earthy, based on the dominant geotechnical properties loading onto each factor. A factor loading threshold of 0.5 was applied, ensuring that each item loaded uniquely onto one factor without cross-loading (<xref ref-type="table" rid="T7">Table 7</xref>). The factor loadings ranged from 0.573 to 0.943, with communality values between 0.415 and 0.848, indicating a strong variable association with the respective factors. The interpretation of these factors was guided by factor loadings, with higher loading values indicating stronger contributions from specific geotechnical properties. Factor 1 (fine-grained soil) included cohesion, plasticity index, and specific gravity, confirming its classification as highly cohesive soil with high water retention. Factor 2 (coarse-grained soil) had high loadings for sand content and friction, reinforcing its characterization as a well-drained, granular soil. Factor 3 (earthy soil) was associated with water content and moderate cohesion, aligning with the traditional descriptions of soils with organic content and moderate stability.</p>
<table-wrap id="T6" position="float">
<label>TABLE 6</label>
<caption>
<p>Extraction of three factors from EFA of geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor</th>
<th align="center">Eigenvalue (rotated)</th>
<th align="center">% of variance (rotated)</th>
<th align="center">Cumulative % of variance (rotated)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">1</td>
<td align="center">4.1</td>
<td align="center">25.49</td>
<td align="center">28.49</td>
</tr>
<tr>
<td align="center">2</td>
<td align="center">2.4</td>
<td align="center">20.27</td>
<td align="center">51.23</td>
</tr>
<tr>
<td align="center">3</td>
<td align="center">1.8</td>
<td align="center">20.21</td>
<td align="center">68.32</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Scree plot for the geotechnical dataset.</p>
</caption>
<graphic xlink:href="fenvs-13-1730654-g003.tif">
<alt-text content-type="machine-generated">Scree plot displaying eigenvalues on the y-axis versus component number on the x-axis, showing a steep decline from component one to four, then leveling off from components five to twelve.</alt-text>
</graphic>
</fig>
<table-wrap id="T7" position="float">
<label>TABLE 7</label>
<caption>
<p>Factors and communality loadings of geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Item</th>
<th align="center">Factor 1</th>
<th align="center">Factor 2</th>
<th align="center">Factor 3</th>
<th align="center">Communalities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Specific gravity</td>
<td align="center">0.943</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.842</td>
</tr>
<tr>
<td align="center">Cohesion</td>
<td align="center">0.715</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.519</td>
</tr>
<tr>
<td align="center">Plastic limit</td>
<td align="center">0.618</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.740</td>
</tr>
<tr>
<td align="center">Silt content</td>
<td align="left">&#x200b;</td>
<td align="center">0.774</td>
<td align="left">&#x200b;</td>
<td align="center">0.623</td>
</tr>
<tr>
<td align="center">Plasticity index</td>
<td align="left">&#x200b;</td>
<td align="center">0.672</td>
<td align="left">&#x200b;</td>
<td align="center">0.649</td>
</tr>
<tr>
<td align="center">Sand content</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.712</td>
<td align="center">0.515</td>
</tr>
<tr>
<td align="center">Friction</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.636</td>
<td align="center">0.621</td>
</tr>
<tr>
<td align="center">Water content</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.623</td>
<td align="center">0.456</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-5">
<title>Geotechnical-based soil classification and correlations</title>
<p>Fine-grained soils were characterized by cohesiveness, specific gravity, and plastic limits (<xref ref-type="table" rid="T8">Table 8</xref>). The correlation between specific gravity and cohesion (<italic>r</italic> (658) &#x3d; 0.591, <italic>p</italic> &#x3c; 0.01) reinforces the geotechnical properties of fine-grained soils, highlighting their compact nature and resistance to structural failure under dry conditions. However, their high plasticity index and low permeability render them prone to reduced shear strength under saturation conditions. Coarse-grained soils comprised silt and the plasticity index, indicating their role in the soil deformability and drainage properties. The strong correlation between silt content and plasticity index (<italic>r</italic> (658) &#x3d; 0.573, <italic>p</italic> &#x3c; 0.01) suggests that fine material within coarse-grained soils contributes to their cohesion and water retention capacity, thereby affecting slope stability. Earthy soils exhibit sand, friction, and water content, confirming their role in soil drainage and surface erosion. These findings confirm that fine-grained soils, owing to their high cohesion and plasticity, require targeted stabilization strategies to mitigate landslide risks. Similarly, coarse-grained soils retain silt, which contributes to instability under fluctuating moisture conditions, despite their high drainage capacity.</p>
<table-wrap id="T8" position="float">
<label>TABLE 8</label>
<caption>
<p>Composition of the extracted factors of geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor name</th>
<th align="center">Composition of factor</th>
<th align="center">Significant correlations</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Fine-grained soil</td>
<td align="center">Specific gravity, cohesion, and plastic limit</td>
<td align="left">Specific gravity with cohesion (<italic>r</italic> (658) &#x3d; 0.521, <italic>p</italic> &#x3c; 0.01)</td>
</tr>
<tr>
<td align="center">Coarse-grained soil</td>
<td align="center">Silt and plasticity index</td>
<td align="left">Silt with plasticity index (<italic>r</italic> (658) &#x3d; 0.573, <italic>p</italic> &#x3c; 0.01)</td>
</tr>
<tr>
<td align="center">Earthy soil</td>
<td align="center">Sand, friction and water content</td>
<td align="left">&#x200b;</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-6">
<title>Factor analysis of traditional and geotechnical features</title>
<p>The EFA was conducted on 660 questionnaire responses and 55 laboratory test results to identify the shared structural components across the traditional soil classifications and geotechnical properties (<xref ref-type="bibr" rid="B46">Mvududu and Sink, 2013</xref>). The extraction results including eigenvalues are presented in <xref ref-type="table" rid="T9">Table 9</xref>. The KMO measure of sampling adequacy was 0.788, confirming that the combined dataset was suitable for the factor analysis. Bartlett&#x2019;s Test of Sphericity was significant (&#x3c7;<sup>2</sup> &#x3d; 1685.4, <italic>p</italic> &#x3c; 0.01), ensuring that inter-variable correlations justified factor extraction. PCA was applied for factor extraction, initially identifying four factors. However, based on the scree plot and total variance contribution, factors explaining less than 55% of the total variance were excluded. <xref ref-type="fig" rid="F4">Figure 4</xref> illustrates the scree plot, which shows a sharp eigenvalue drop beyond the third factor, justifying the retention of the three dominant factors. The final EFA model retained three factors that collectively explained 71.46% of the total variance (<xref ref-type="table" rid="T9">Table 9</xref>). The factor-loading analysis followed the same procedure as in the previous sections, with items loaded onto a given factor if they exhibited a factor loading &#x2265;0.5 and did not cross-load onto other factors (<xref ref-type="table" rid="T10">Table 10</xref>). The retained factors were classified as fine-grained, coarse-grained, and earthy soil types, aligned with both the traditional and geotechnical soil categorizations. The combined EFA dataset demonstrated a strong alignment between the traditional attributes and conventional geotechnical properties. For instance, factor loadings for soil color and moisture retention in the traditional dataset were strongly associated with geotechnical properties, such as water content and cohesion, confirming the validity of integrating traditional and quantitative methods. The correlation between earthy smell and water retention (r (658) &#x3d; 0.332, p &#x3c; 0.01) further supports the reliability of qualitative assessments for landslide-prone soil classification.</p>
<table-wrap id="T9" position="float">
<label>TABLE 9</label>
<caption>
<p>Extraction of three factors from EFA of traditional and geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor</th>
<th align="center">Eigenvalue (rotated)</th>
<th align="center">% of variance (rotated)</th>
<th align="center">Cumulative % of variance (rotated)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">1</td>
<td align="center">4.8</td>
<td align="center">24.86</td>
<td align="center">24.86</td>
</tr>
<tr>
<td align="center">2</td>
<td align="center">4.1</td>
<td align="center">18.55</td>
<td align="center">43.42</td>
</tr>
<tr>
<td align="center">3</td>
<td align="center">1.9</td>
<td align="center">14.32</td>
<td align="center">71.46</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Scree plot for the combined dataset.</p>
</caption>
<graphic xlink:href="fenvs-13-1730654-g004.tif">
<alt-text content-type="machine-generated">Scree plot showing eigenvalues on the y-axis and component numbers on the x-axis from one to twenty. The plot indicates a steep decline from component one to three, leveling off after component four.</alt-text>
</graphic>
</fig>
<table-wrap id="T10" position="float">
<label>TABLE 10</label>
<caption>
<p>Factors and communality loadings of traditional and geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Item</th>
<th align="center">Factor 1</th>
<th align="center">Factor 2</th>
<th align="center">Factor 3</th>
<th align="center">Communalities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Water retention</td>
<td align="center">0.832</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.719</td>
</tr>
<tr>
<td align="center">Stickiness</td>
<td align="center">0.795</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.660</td>
</tr>
<tr>
<td align="center">Smoothness</td>
<td align="center">0.789</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.657</td>
</tr>
<tr>
<td align="center">Hardness</td>
<td align="center">0.724</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.524</td>
</tr>
<tr>
<td align="center">Soil clump easily</td>
<td align="center">0.717</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.528</td>
</tr>
<tr>
<td align="center">Silt content</td>
<td align="center">0.676</td>
<td align="center">0.794</td>
<td align="left">&#x200b;</td>
<td align="center">0.480</td>
</tr>
<tr>
<td align="center">Rocks and debris</td>
<td align="left">&#x200b;</td>
<td align="center">0.742</td>
<td align="left">&#x200b;</td>
<td align="center">0.777</td>
</tr>
<tr>
<td align="center">Sand content</td>
<td align="left">&#x200b;</td>
<td align="center">0.741</td>
<td align="left">&#x200b;</td>
<td align="center">0.739</td>
</tr>
<tr>
<td align="center">White color</td>
<td align="left">&#x200b;</td>
<td align="center">0.734</td>
<td align="left">&#x200b;</td>
<td align="center">0.737</td>
</tr>
<tr>
<td align="center">Black color</td>
<td align="left">&#x200b;</td>
<td align="center">0.655</td>
<td align="left">&#x200b;</td>
<td align="center">0.544</td>
</tr>
<tr>
<td align="center">Density</td>
<td align="left">&#x200b;</td>
<td align="center">0.794</td>
<td align="left">&#x200b;</td>
<td align="center">0.461</td>
</tr>
<tr>
<td align="center">Earthy smell</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.814</td>
<td align="center">0.669</td>
</tr>
<tr>
<td align="center">Musty smell</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.761</td>
<td align="center">0.707</td>
</tr>
<tr>
<td align="center">Plastic limit</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.628</td>
<td align="center">0.439</td>
</tr>
<tr>
<td align="center">High moisture</td>
<td align="left">&#x200b;</td>
<td align="left">&#x200b;</td>
<td align="center">0.609</td>
<td align="center">0.428</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-7">
<title>Traditional and geotechnical features with significant correlations</title>
<p>The composition of each extracted factor is listed in <xref ref-type="table" rid="T11">Table 11</xref>. Fine-grained soil (Factor 1) accounted for the highest variance (24.86%), followed by coarse-grained soil (18.55%), and earthy soil (14.32%). Fine-grained soil exhibits properties such as water retention, stickiness, smoothness, hardness, soil clumping tendency, and silt content. A significant correlation was observed between stickiness and silt content (<italic>r</italic> (658) &#x3d; 0.450, <italic>p</italic> &#x3c; 0.01), thereby reinforcing the role of fine particles in soil cohesion and permeability. This supports the traditional classification of fertile moisture-retentive soils, which exhibit high plasticity under saturation, making them susceptible to landslides in wet conditions. Earthy soil includes density, earthy smell, musty smell, plastic limit, and high moisture content. A significant correlation was found between the earthy smell and plastic limit (<italic>r</italic> (658) &#x3d; 0.312, <italic>p</italic> &#x3c; 0.01), suggesting that organic-rich soils retain moderate plasticity, water content, and balance stability with permeability. This aligns with traditional description of transitional soils that exhibit mixed characteristics of moisture retention and structural variability under wet-dry cycles. Unlike fine-grained and earthy soils, no statistically significant correlations were observed for coarse-grained soils. This suggests that coarse-grained soils, which include components such as sand, gravel, and rocks, behave more independently of finer geotechnical and traditional soil attributes. Their properties are largely governed by the granular structure rather than cohesive interactions, reinforcing their high permeability and low susceptibility to plasticity-related instabilities. These findings demonstrate that transitional qualitative soil classifications closely align with measurable geotechnical parameters in fine-grained and earthy soils, reinforcing the importance of integrating traditional ecological knowledge into conventional landslide risk assessments.</p>
<table-wrap id="T11" position="float">
<label>TABLE 11</label>
<caption>
<p>Composition of the extracted factors of traditional and geotechnical features.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Factor name</th>
<th align="center">Composition of factor</th>
<th align="center">Significant correlations</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Fine-grained soil</td>
<td align="center">Transitional: Stickiness, smoothness, hardness, soil clump together easily; geotechnical: Water retention, silt content</td>
<td align="left">Stickiness with silt content (<italic>r</italic> (658) &#x3d; 0.450, <italic>p</italic> &#x3c; 0.01)</td>
</tr>
<tr>
<td align="center">Coarse-grained soil</td>
<td align="center">Transitional: Rocks and debris, white color, and black color<break/>Geotechnical: Density, sand content</td>
<td align="left">&#x200b;</td>
</tr>
<tr>
<td align="center">Earthy soil</td>
<td align="center">Transitional: Earthy smell, musty smell, geotechnical: Plastic limit, and high moisture</td>
<td align="left">Earthy smell with plastic limit (<italic>r</italic> (658) &#x3d; 0.312, <italic>p</italic> &#x3c; 0.01)</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-8">
<title>Analysis of variance</title>
<p>A one-way ANOVA was conducted to examine the impact of the demographic variables (age, discipline, and education level) on the three soil types (fine-grained, coarse-grained, and earthy soils) (see <xref ref-type="table" rid="T12">Table 12</xref>).</p>
<table-wrap id="T12" position="float">
<label>TABLE 12</label>
<caption>
<p>Statistical results of ANOVA for the influence of demographic variables.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Demographic variable</th>
<th align="left">Soil type</th>
<th align="left">ANOVA result</th>
<th align="left">Post-hoc analysis</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="3" align="left">Age</td>
<td align="left">Fine-grained soil</td>
<td align="left">
<italic>F</italic> (2, 657) &#x3d; 0.761, <italic>p</italic> &#x3d; 0.51, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td align="left">Coarse-grained soil</td>
<td align="left">
<italic>F</italic> (2, 657) &#x3d; 0.761, <italic>p</italic> &#x3d; 0.41, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td align="left">Earthy soil</td>
<td align="left">
<italic>F</italic> (2,657) &#x3d; 0.500, <italic>p</italic> &#x3d; 0.61, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td rowspan="3" align="left">Discipline</td>
<td align="left">Fine-grained soil</td>
<td align="left">
<bold>
<italic>F</italic> (2, 657) &#x3d; 2.9, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
</bold>
<sup>
<bold>
<italic>2</italic>
</bold>
</sup> <bold>&#x3d; 0.01</bold>
</td>
<td align="left">CE &#x3e; ECE (<italic>p &#x3c;</italic> 0.05). CE &#x223c; CSE (<italic>p</italic> &#x3d; 0.56); CSE &#x223c; ECE (<italic>p</italic> &#x3d; 0.15)</td>
</tr>
<tr>
<td align="left">Coarse-grained soil</td>
<td align="left">
<italic>F</italic> (2, 657) &#x3d; 1.567, <italic>p</italic> &#x3d; 0.25, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td align="left">Earthy soil</td>
<td align="left">
<bold>
<italic>F</italic> (2, 657) &#x3d; 3.9, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
</bold>
<sup>
<bold>
<italic>2</italic>
</bold>
</sup> <bold>&#x3d; 0.03</bold>
</td>
<td align="left">ECE &#x3e; CE <italic>(p</italic> &#x3c; 0.05); ECE &#x3e; CSE (<italic>p</italic> &#x3c; 0.05). CE &#x223c; CSE (<italic>p</italic> &#x3d; 0.99)</td>
</tr>
<tr>
<td rowspan="3" align="left">Education level</td>
<td align="left">Fine-grained soil</td>
<td align="left">
<italic>F</italic> (2, 657) &#x3d; 1.662, <italic>p</italic> &#x3d; 0.23, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td align="left">Coarse-grained soil</td>
<td align="left">
<italic>F</italic> (2, 657) &#x3d; 0.267, <italic>p</italic> &#x3d; 0.92, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01</td>
<td align="left">&#x2014;</td>
</tr>
<tr>
<td align="left">Earthy soil</td>
<td align="left">
<bold>
<italic>F</italic> (2, 657) &#x3d; 2.892, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
</bold>
<sup>
<bold>
<italic>2</italic>
</bold>
</sup> <bold>&#x3d; 0.04</bold>
</td>
<td align="left">PG &#x3e; G (<italic>p</italic> &#x3c; 0.05); PG &#x3e; Ph.D. (<italic>p</italic> &#x3c; 0.05). Ph.D. &#x223c; G (<italic>p</italic> &#x3d; 0.89)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Bolded text indicates significant results with <italic>p &#x3c;</italic> .05., &#x2a;CE: civil engineering, &#x2a;CSE: computer science engineering, &#x2a;ECE: electronics and communication engineering, &#x2a;PG: postgraduate, &#x2a;G: graduate, &#x2a;Ph.D.: doctor of philosophy.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3-9">
<title>Effect of age</title>
<p>Age did not significantly affect soil classification across fine-grained (<italic>F</italic> (2, 657) &#x3d; 0.761, <italic>p</italic> &#x3d; 0.51, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01), coarse-grained (<italic>F</italic> (2, 657) &#x3d; 0.761, <italic>p</italic> &#x3d; 0.41, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01), or earthy soils (<italic>F</italic> (2,657) &#x3d; 0.500, <italic>p</italic> &#x3d; 0.61, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01). This suggests that soil categorization was not influenced by age differences among the experts, which is consistent with previous findings that expertise-based assessments remain consistent across age groups.</p>
</sec>
<sec id="s3-10">
<title>Effect of discipline</title>
<p>Discipline (civil engineering (CE), computer science engineering (CSE), and electronics and communication engineering (ECE)) significantly influenced fine-grained soil categorization (<italic>F</italic> (2, 657) &#x3d; 2.9, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01). Tukey&#x2019;s post hoc test (see <xref ref-type="table" rid="T10">Table 10</xref>) indicated that CE participants assigned significantly higher scores to fine-grained soils than ECE participants (CE (M &#x3d; 16.1, SD &#x3d; 2.3) &#x3e; ECE (M &#x3d; 14.3, SD &#x3d; 2.1), <italic>p</italic> &#x3c; 0.05). However, no significant differences were observed between CE and CSE (<italic>p</italic> &#x3d; 0.56) or between CSE and ECE (<italic>p</italic> &#x3d; 0.15). These findings highlight that CE participants, trained in geotechnical principles, prioritized fine-grained soils more than ECE participants, who may have placed less emphasis on soil cohesive properties. Similarly, discipline significantly influenced the classification of earthy soils (<italic>F</italic> (2, 657) &#x3d; 3.9, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.03). ECE participants rated earthy soils significantly higher than CE (ECE (M &#x3d; 9.2, SD &#x3d; 0.6) &#x3e; CE (M &#x3d; 7.3, SD &#x3d; 1.3), <italic>p</italic> &#x3c; 0.05) and CSE (ECE (M &#x3d; 9.2, SD &#x3d; 0.5) &#x3e; CSE (M &#x3d; 7.2, SD &#x3d; 1.4), <italic>p</italic> &#x3c; 0.05), whereas CE and CSE did not differ significantly (<italic>p</italic> &#x3d; 0.99). These results suggest that ECE experts may have been more inclined to consider traditional qualitative attributes, such as smell and texture, leading to a stronger emphasis on earthy soil classifications. For coarse-grained soil, no significant effect of discipline was found (<italic>F</italic> (2, 657) &#x3d; 1.567, <italic>p</italic> &#x3d; 0.25, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01), indicating that disciplinary training did not influence classification. This may be attributed to the straightforward nature of coarse-grained soils, which exhibit clear geotechnical properties, such as high permeability and low cohesion, reducing the likelihood of subjective interpretation.</p>
</sec>
<sec id="s3-11">
<title>Effect of education level</title>
<p>Education level (Ph.D., postgraduate (PG), or graduate (G)) did not significantly influence the classification of fine-grained soils (<italic>F</italic> (2, 657) &#x3d; 1.662, <italic>p</italic> &#x3d; 0.23, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01) or coarse-grained soils (<italic>F</italic> (2, 657) &#x3d; 0.267, <italic>p</italic> &#x3d; 0.92, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.01), suggesting that expertise across these levels resulted in similar assessments for these soil types. However, education level significantly affected the earthy soil classification (<italic>F</italic> (2, 657) &#x3d; 2.892, <italic>p</italic> &#x3c; 0.05, <italic>&#x3b7;</italic>
<sup>
<italic>2</italic>
</sup> &#x3d; 0.04). Post-hoc analysis (<xref ref-type="table" rid="T10">Table 10</xref>) showed that PG participants rated earthy soils significantly higher than both G (PG (M &#x3d; 9.1, SD &#x3d; 0.8) &#x3e; G (M &#x3d; 8.1, SD &#x3d; 1.3), <italic>p</italic> &#x3c; 0.05) and Ph.D. participants (PG (M &#x3d; 9.3, SD &#x3d; 0.9) &#x3e; Ph.D. (M &#x3d; 7.5, SD &#x3d; 1.3), <italic>p</italic> &#x3c; 0.05). No significant difference was found between PhD and G participants (<italic>p</italic> &#x3d; 0.89). This suggests that PG participants who are at an intermediate level of specialization may have been more open to integrating both traditional and geotechnical attributes in their assessment of earthy soils.</p>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>Discussion</title>
<p>The integration of conventional geotechnical assessments with transitional principles presents a novel framework for evaluating landslide susceptibility by bridging the gap between traditional knowledge and contemporary engineering methods. This study establishes how qualitative soil classifications based on color, texture, and smell align with quantitative geotechnical parameters, such as cohesion, permeability, and moisture content. The identified soil categories fine-grained, coarse-grained, and earthy soils demonstrate a strong convergence between the transitional principles and geotechnical findings. Fine-grained soils, described in TK as fertile and highly water-retentive, exhibit high plasticity and cohesion, but experience a significant reduction in shear strength under saturation, making them particularly prone to landslides. These characteristics align with geotechnical assessments, which consistently identify water retention and reduced permeability as the major risk factors for slope failure. The strong correlation between specific gravity and cohesion supports this relationship, highlighting that fine-grained soils exhibit higher stability when dry but are vulnerable to structural failure under wet conditions.</p>
<p>To validate the mechanical relevance of the TK-derived soil categories, factor-based classifications were compared with laboratory-measured geotechnical parameters, including cohesion, internal friction angle, plasticity index, and saturated unit weight. Fine-grained soils exhibit higher cohesion and plasticity, coarse-grained soils exhibit higher permeability and lower shear strength, and earthy soils exhibit intermediate characteristics. Field observations further confirmed that the mapped landslide zones corresponded primarily with fine-grained soil areas, supporting the mechanical validity of the TK-based classification framework.</p>
<p>In contrast, coarse-grained soils, which are categorized as arid and loosely structured in TK, exhibit high permeability and low cohesion, making them more susceptible to surface erosion than deep-seated movement. Although coarse-grained soils have been widely studied in geotechnical engineering, this study reinforces their instability under heavy rainfall conditions by correlating silt content with plasticity index. This finding supports previous studies, such as those by Roslee, which highlighted the role of particle size distribution in landslide susceptibility, particularly in tropical environments (<xref ref-type="bibr" rid="B55">Roslee, 2019</xref>). Earthy soils, classified as ordinary in TK, display instability under fluctuating moisture conditions because of their low water retention capacity, a finding that closely aligns with the geotechnical assessments of moderate cohesion and increased porosity. The significant correlation between earthy smell and water retention validated the role of smell-based soil assessments in identifying moisture-sensitive soils, thereby providing an effective preliminary indicator of landslide risk. In addition to mechanical parameters, significant correlations were observed between traditional knowledge (TK) indicators and geotechnical properties. For instance, soils with an earthy smell were positively correlated with the plastic limit (<italic>r</italic> &#x3d; 0.312, <italic>p</italic> &#x3c; 0.01), suggesting a potential link between olfactory perception and clay behavior under moisture. Musty-smelling soils were significantly associated with water retention (<italic>r</italic> &#x3d; 0.483, <italic>p</italic> &#x3c; 0.01) and moisture content (<italic>r</italic> &#x3d; 0.617, <italic>p</italic> &#x3c; 0.01), indicating that these descriptors may reflect organic-rich or fine-grained conditions that favor a high water-holding capacity. In contrast, white soils were positively correlated with silt content (<italic>r</italic> &#x3d; 0.267, <italic>p</italic> &#x3c; 0.01) and negatively correlated with gravel content (<italic>r</italic> &#x3d; &#x2212;0.202, <italic>p</italic> &#x3c; 0.01), reinforcing that color perceptions are related to soil texture. These statistically supported correlations illustrate that traditional sensory-based assessments, such as smell and color, are not merely anecdotal but are associated with measurable soil properties relevant to landslide susceptibility. These findings parallel the observations of Pardede, who demonstrated that alternating wet and dry cycles significantly affect soil cohesion and shear strength (<xref ref-type="bibr" rid="B49">Pardede, 2023</xref>).</p>
<p>By adopting the TK-based soil categorization, landslide-prone regions can benefit from a rapid, low-cost, and accessible assessment method that does not require specialized laboratory testing or expensive geotechnical equipment. The reliance on qualitative indicators such as color, texture, and smell makes this approach particularly useful for preliminary evaluations in remote or resource-limited areas. In addition, this method can serve as a first-level screening tool for identifying high-risk soil types before deploying more detailed geotechnical investigations.</p>
<p>By correlating qualitative insights from TK, such as smell, color, and texture, with measurable geotechnical parameters, such as density and moisture content, this study bridges traditional and conventional knowledge systems. The findings emphasize the value of ecological traditions in contemporary soil assessments, offering practical insights for slope management and disaster mitigation in landslide-prone regions, such as the Himalayas. Importantly, the integrated TK and geotechnical framework is not restricted to the Himalayas alone but can be adapted to other mountainous, tropical, or arid environments where soil-landscape interactions drive slope stability. This generalizability underscores its contribution to broader landscape evolution studies and enhances its relevance to global soil geomorphology research. Unlike conventional geotechnical studies, which primarily emphasize numerical thresholds for properties such as cohesion and permeability, this research demonstrates that traditional qualitative descriptors such as soil color, smell, and texture provide comparable insights into landslide susceptibility. This integration of local ecological knowledge with conventional geotechnical assessments aligns with Mali&#x2019;s findings on the importance of plasticity index and cohesion in determining landslide risk (<xref ref-type="bibr" rid="B43">Mali et al., 2022</xref>). Furthermore, although Casagli demonstrated the advantages of remote sensing for landslide detection, this study provides a complementary approach that relies on direct soil evaluation, making it more accessible in resource-limited areas (<xref ref-type="bibr" rid="B12">Casagli et al., 2023</xref>).</p>
<p>The factor analysis results further support the alignment of geotechnical attributes with traditional soil classifications. Fine-grained soils are strongly associated with high water retention, smoothness, and stickiness, corresponding to higher cohesion and plasticity index values. Coarse-grained soils, composed primarily of sand, gravel, and rocks, exhibit high permeability and low cohesion, reinforcing their propensity to surface erosion. Earthy soils, identified by their characteristic earthy smell and brown color, displayed moderate cohesion and increased porosity. The significant correlations between the traditional and geotechnical properties validate the scientific relevance of the transitional soil classification (<xref ref-type="table" rid="T3">Table 3</xref>). Dearing et al. emphasized the value of integrating local ecological knowledge into environmental management, but their study lacked quantitative validation (<xref ref-type="bibr" rid="B40">Liu et al., 2018</xref>). This study overcomes this limitation by employing statistical techniques to confirm the alignment between the traditional soil properties and conventional geotechnical parameters. Comparable advances have been reported in recent studies that employed hybrid laboratory and modelling frameworks for landslide evaluations (<xref ref-type="bibr" rid="B13">Danesh et al., 2025</xref>; <xref ref-type="bibr" rid="B1">Ab et al., 2025</xref>). For example, recent studies have examined the creep behavior in high-plasticity soils under constant shear and demonstrated GIS-based susceptibility mapping using ANN, SVM, and RF models (<xref ref-type="bibr" rid="B13">Danesh et al., 2025</xref>; <xref ref-type="bibr" rid="B1">Ab et al., 2025</xref>). These efforts align with the objective of the present study, which is to integrate diverse datasets to derive interpretable soil behavior patterns. The influence of discipline and education level on soil categorization highlights the potential biases in expert assessments. Civil engineering experts emphasize geotechnical properties, particularly for fine-grained soils, whereas experts from other engineering disciplines place greater emphasis on traditional qualitative attributes. Similarly, postgraduate participants demonstrated a greater ability to integrate both perspectives, whereas graduate and Ph.D. participants showed a tendency toward specialization, which may hinder the holistic integration of traditional and conventional frameworks. These findings align with Liu&#x2019;s work, which underscores the impact of disciplinary backgrounds on risk assessment approaches (<xref ref-type="bibr" rid="B40">Liu et al., 2018</xref>). However, this study extends these findings by demonstrating that the educational level also influences the ability to synthesize diverse classification frameworks.</p>
<p>The practical implications of this study extend to landslide risk management, in which soil classification provides key mitigation strategies. Fine-grained soils, which are prone to water saturation and reduced shear strength, require drainage systems, slope grading, and retaining walls. Coarse-grained soils, characterized by high permeability and low cohesion, require stabilization techniques such as geotextiles, vegetation cover, and terracing to mitigate surface erosion. Earthy soils, affected by wet-dry cycles, benefit from bioengineering approaches, such as vegetation-based stabilization. The findings of Machado, who demonstrated the effectiveness of vegetation cover in landslide mitigation, support this study&#x2019;s results on TK emphasis on soil fertility and stability (<xref ref-type="bibr" rid="B42">Machado et al., 2019</xref>).</p>
<p>The integrated framework developed in this study is directly applicable to local Himalayan communities, where conventional laboratory testing is often inaccessible. By translating traditional qualitative soil cues, such as color, smell, and texture, into standardized risk indicators, community members can perform rapid, low-cost evaluations of slope stability. These assessments can guide agricultural planning, construction siting, and early warning awareness. Furthermore, training local residents in the use of these descriptors for preliminary slope checks can complement institutional monitoring efforts, promoting participatory and sustainable landslide risk management.</p>
<p>This study provides a valuable framework for policymakers and practitioners involved in land-use planning and disaster mitigation. The integrated soil categorization model enables targeted interventions such as prioritizing high-risk zones for early warning systems and designing context-specific stabilization techniques (<xref ref-type="bibr" rid="B22">Froude and Petley, 2018</xref>). By incorporating traditional knowledge with conventional geotechnical assessments, policymakers can implement cost-effective strategies tailored to regional soil characteristics. For instance, fine-grained soils with high water retention can benefit from improved drainage systems, whereas coarse-grained soils require surface stabilization techniques, such as terracing and vegetation reinforcement (<xref ref-type="bibr" rid="B51">Petley, 2012</xref>; <xref ref-type="bibr" rid="B32">Huang and Fan, 2013</xref>). This hybrid approach enhances decision making, particularly in resource-limited regions, by reducing dependence on laboratory-based soil testing while offering scalable field-based assessments (<xref ref-type="bibr" rid="B16">Dearing et al., 2016</xref>). By integrating the TK soil categorization with conventional geotechnical techniques, policymakers and practitioners can develop a hybrid approach that enhances landslide risk assessment and mitigation strategies. The ability to classify soil types using traditional qualitative markers makes this framework especially valuable for disaster-prone regions, where rapid assessments are crucial. Moreover, the use of TK-based categorization in combination with early warning systems can strengthen community-based landslide preparedness and response strategies.</p>
<p>Future research should extend the TK-inspired soil categorization framework to diverse geological settings beyond the Himalayas, including arid, tropical, and coastal environments, where soil properties and landslide risks vary significantly. Longitudinal studies monitoring soil stability under changing climatic conditions will further enhance the predictive models for landslide susceptibility. Integrating modern technologies, such as machine learning and IoT-based sensors, presents exciting possibilities for refining this framework. Machine learning models trained on larger datasets can identify complex correlations between transitional soil features and geotechnical properties. Similarly, IoT-enabled sensors and remote sensing tools, such as LiDAR, can provide real-time data for landslide risk prediction and monitoring. In addition, the study did not include geochemical or mineralogical testing (e.g., clay mineralogy, ionic composition, pore structure), which are likely to underpin several of the TK indicators, such as salty or sweet taste. Future studies should integrate mineralogical and geochemical analyses to evaluate whether these sensory-based traditional descriptors reflect the deeper compositional attributes that affect slope stability.</p>
<p>Despite its contributions, this study has some limitations. For example, this study is conducted within the context of the Himalayan region, which has unique geological and environmental characteristics. While the findings offer valuable insights for similar mountainous terrains, further studies in different geographic and climatic regions are necessary to assess the broader applicability of the results. Although qualitative assessments, such as soil smell and texture, provided useful preliminary information, incorporating objective methods like laboratory analyses and IoT-based soil sensors in future research could enhance measurement accuracy. In addition, expert calibration and reliability testing may have a certain level of subjective bias in sensory interpretation, which represents an inherent limitation of expert-based traditional knowledge assessments.</p>
<p>Overall, by bridging traditional and conventional knowledge, this study lays the foundation for a holistic and adaptive soil-categorization framework with significant implications for sustainable environmental management and disaster mitigation.</p>
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<sec sec-type="data-availability" id="s5">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="sec" rid="s12">Supplementary Material</xref>, further inquiries can be directed to the corresponding author.</p>
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<sec sec-type="ethics-statement" id="s6">
<title>Ethics statement</title>
<p>The studies involving humans were approved by Institutional Ethics Committee of the Indian Institute of Technology Mandi. The studies were conducted in accordance with the local legislation and institutional requirements. The participants provided their written informed consent to participate in this study.</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>SS: Formal Analysis, Resources, Writing &#x2013; review and editing, Project administration, Software, Writing &#x2013; original draft, Methodology, Investigation, Validation, Conceptualization, Data curation, Supervision. KU: Funding acquisition, Resources, Project administration, Supervision, Writing &#x2013; review and editing, Validation. VD: Methodology, Validation, Software, Resources, Writing &#x2013; review and editing, Project administration, Supervision.</p>
</sec>
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<title>Conflict of interest</title>
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<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fenvs.2025.1730654/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fenvs.2025.1730654/full&#x23;supplementary-material</ext-link>
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<supplementary-material xlink:href="DataSheet1.pdf" id="SM1" mimetype="application/pdf" xmlns:xlink="http://www.w3.org/1999/xlink"/>
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<fn-group>
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<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/620968/overview">Gilles Colinet</ext-link>, University of Li&#xe8;ge, Belgium</p>
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<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2025858/overview">Mohammad Azarafza</ext-link>, University of Tabriz, Iran</p>
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<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3278683/overview">Bharat Lal</ext-link>, Bihar Agricultural University, India</p>
</fn>
</fn-group>
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