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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Built Environ.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Built Environment</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Built Environ.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2297-3362</issn>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-id pub-id-type="publisher-id">1746551</article-id>
<article-id pub-id-type="doi">10.3389/fbuil.2026.1746551</article-id>
<article-version article-version-type="Version of Record" vocab="NISO-RP-8-2008"/>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Microstructural and strength analysis of lower Himalayan soil in Arunachal Pradesh using biomedical waste as additives</article-title>
<alt-title alt-title-type="left-running-head">Kalita 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/fbuil.2026.1746551">10.3389/fbuil.2026.1746551</ext-link>
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<contrib-group>
<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Kalita</surname>
<given-names>Ajanta</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>&#x2020;</sup>
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<contrib contrib-type="author" corresp="yes" equal-contrib="yes">
<name>
<surname>Omo</surname>
<given-names>Yachang</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>&#x2020;</sup>
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<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Paron</surname>
<given-names>Omem</given-names>
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<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<sup>&#x2020;</sup>
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<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Yangchin</surname>
<given-names>Pem</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
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<sup>&#x2020;</sup>
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<name>
<surname>Paksok</surname>
<given-names>Dinken</given-names>
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<xref ref-type="aff" rid="aff1">
<sup>1</sup>
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<sup>&#x2020;</sup>
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<aff id="aff1">
<label>1</label>
<institution>Department of Civil Engineering, North Eastern Regional Institute of Science and Technology</institution>, <city>Nirjuli</city>, <state>Arunachal Pradesh</state>, <country country="IN">India</country>
</aff>
<aff id="aff2">
<label>2</label>
<institution>Department of Civil Engineering, Central Institute of Technology</institution>, <city>Kokrajhar</city>, <state>Assam</state>, <country country="IN">India</country>
</aff>
<author-notes>
<corresp id="c001">
<label>&#x2a;</label>Correspondence: Yachang Omo, <email xlink:href="mailto:y.omo@cit.ac.in">y.omo@cit.ac.in</email>
</corresp>
<fn fn-type="other" id="fn001">
<label>&#x2020;</label>
<p>ORCID: Ajanta Kalita, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0003-2495-5031">orcid.org/0000-0003-2495-5031</ext-link>; Yachang Omo, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-0311-8499">orcid.org/0000-0002-0311-8499</ext-link>; Omem Paron, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0009-0001-2050-2978">orcid.org/0009-0001-2050-2978</ext-link>; Pem Yangchin, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0009-0005-4223-4491">orcid.org/0009-0005-4223-4491</ext-link>; Dinken Paksok, <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0001-9813-870X">orcid.org/0000-0001-9813-870X</ext-link>
</p>
</fn>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-02-17">
<day>17</day>
<month>02</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>12</volume>
<elocation-id>1746551</elocation-id>
<history>
<date date-type="received">
<day>14</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>12</day>
<month>01</month>
<year>2026</year>
</date>
<date date-type="accepted">
<day>15</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Kalita, Omo, Paron, Yangchin and Paksok.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Kalita, Omo, Paron, Yangchin and Paksok</copyright-holder>
<license>
<ali:license_ref start_date="2026-02-17">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</license-p>
</license>
</permissions>
<abstract>
<p>The escalating generation of biomedical waste poses critical environmental and health challenges globally. This study investigates the sustainable utilization of shredded nitrile gloves (NG) and Plaster of Paris (POP) as stabilizing additives for silty sand soil from the landslide-prone Nirjuli-Banderdewa corridor in Arunachal Pradesh, India. Comprehensive geotechnical characterization included compaction tests, Unconfined Compressive Strength (UCS), California Bearing Ratio (CBR), and advanced microstructural analysis using Scanning Electron Microscope (SEM) and Energy Dispersive X-ray Spectroscopy (EDX). Nitrile gloves were incorporated at 0.35%, 0.5%, and 1% by dry weight, while POP was added at 3%, 6%, and 9%. Results demonstrated that the optimal combination of 0.5% NG and 6% POP achieved a 109% increase in UCS and more than doubled both soaked and unsoaked CBR values compared to untreated soil. Microstructural analysis revealed enhanced particle bonding, reduced porosity, and improved fabric integrity through bridging mechanisms and cementitious gel formation. The stabilized soil meets IRC specifications for heavily trafficked road subgrades, demonstrating a viable circular economy approach for biomedical waste management while addressing geotechnical challenges in the seismically active Himalayan region.</p>
</abstract>
<kwd-group>
<kwd>biomedical waste</kwd>
<kwd>California bearing ratio</kwd>
<kwd>energy dispersive X-ray spectroscopy</kwd>
<kwd>nitrile gloves</kwd>
<kwd>plaster of paris</kwd>
<kwd>scanning electron microscope</kwd>
<kwd>soil stabilization</kwd>
<kwd>unconfined compressive strength</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was not received for this work and/or its publication.</funding-statement>
</funding-group>
<counts>
<fig-count count="11"/>
<table-count count="2"/>
<equation-count count="0"/>
<ref-count count="54"/>
<page-count count="15"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Geotechnical Engineering</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<label>1</label>
<title>Introduction</title>
<sec id="s1-1">
<label>1.1</label>
<title>Regional context and geotechnical challenges</title>
<p>Arunachal Pradesh, situated in the Eastern Himalayan region of India, experiences unique geotechnical challenges due to its complex geological setting, high seismicity (Zone V), and monsoon-driven precipitation exceeding 2,500&#xa0;mm annually (<xref ref-type="bibr" rid="B25">Kalita et al., 2021</xref>). The state&#x2019;s infrastructure development is constrained by widespread silty soils characterized by low bearing capacity, high compressibility, and susceptibility to landslides (<xref ref-type="bibr" rid="B36">Rehman and Azhoni, 2023</xref>; <xref ref-type="bibr" rid="B47">D. K. Singh et al., 2025</xref>). The Nirjuli-Banderdewa corridor, a critical transportation artery, traverses terrain dominated by silty sand deposits that exhibit poor engineering properties, including inadequate shear strength, high moisture sensitivity, and volume instability.</p>
<p>Conventional stabilization methods employing cement and lime are energy-intensive, contribute significantly to carbon emissions, and present economic challenges in remote Himalayan regions (<xref ref-type="bibr" rid="B2">Barbhuiya et al., 2025</xref>). This necessitates exploring sustainable alternatives using locally available or waste-derived materials that can simultaneously address soil improvement needs and waste management imperatives.</p>
<p>Recent research has increasingly focused on sustainable reuse of various waste streams in civil and geotechnical engineering to mitigate environmental impacts while enhancing soil performance. For example, <xref ref-type="bibr" rid="B45">Shinde et al. (2025)</xref> investigated the reuse of sterilized biomedical plastic waste, including face masks and gloves, in concrete pavement blocks, demonstrating acceptable mechanical performance and contributions to circular economy practices. Additionally, <xref ref-type="bibr" rid="B5">Brahmbhatt and Patel (2025)</xref> reported the integration of biomedical waste incineration ash with fly ash in concrete, indicating effective strength outcomes and environmental safety when waste ash is used as partial cement replacement.</p>
<p>Beyond biomedical waste specifically, the review by <xref ref-type="bibr" rid="B26">Khalid and Alshawmar (2024)</xref> provides a comprehensive analysis of recycled polyethylene terephthalate (PET) fibers and strips for soil stabilization, highlighting enhancements in shear strength, bearing capacity, and soil reinforcement potential, which are conceptually similar to polymeric reinforcement approaches explored in our study. Complementing this, <xref ref-type="bibr" rid="B35">Ravish et al. (2025)</xref> conducted a critical review of used polymers in soil stabilization, providing global insights into polymer-soil interactions relevant to the reinforcement mechanisms described in our work.</p>
<p>Despite these advances, systematic studies focusing on the direct reuse of sterilized biomedical waste for soil stabilization, particularly under challenging Himalayan geotechnical conditions, remain limited. Most existing investigations emphasize construction materials such as concrete or asphalt, while comparatively fewer studies address subgrade and foundation soils, where moisture sensitivity, seismic loading, and long-term durability are critical concerns. In addition, many studies lack detailed microstructural evidence linking waste-derived additives to macroscopic strength and bearing improvements, especially for silty sand soils prevalent in landslide-prone regions. In this context, the present study aims to bridge this research gap by evaluating the combined use of sterilized nitrile gloves and medical-grade Plaster of Paris as soil stabilizers for silty sand from the Nirjuli-Banderdewa corridor. By integrating comprehensive geotechnical testing with SEM and EDX-based microstructural analysis and assessing compliance with IRC subgrade requirements, the study contributes new insights into both the engineering performance and the sustainable management of biomedical waste within a circular economy framework tailored to the Lower Himalayan region.</p>
</sec>
<sec id="s1-2">
<label>1.2</label>
<title>Biomedical waste: a growing environmental challenge</title>
<p>Global biomedical waste generation has escalated dramatically, particularly following the COVID-19 pandemic, with India producing approximately 619 tons daily (<xref ref-type="bibr" rid="B15">Dehal et al., 2022</xref>). On an average, the hospital waste generation rate ranges from 0.5 to 2.0&#xa0;kg/bed/day which amounts to about 0.33 million tons annually (<xref ref-type="bibr" rid="B4">Bhalla et al., 2019</xref>). Current disposal methods consisting of predominantly incineration and autoclaving are energy-intensive, generate greenhouse gases, and produce residual materials requiring further management (<xref ref-type="bibr" rid="B54">Zikhathile et al., 2022</xref>). NG constitute approximately 15%&#x2013;20% of biomedical waste by weight and are non-biodegradable, persisting in landfills for decades (<xref ref-type="bibr" rid="B34">Prata et al., 2020</xref>).</p>
<p>POP (calcium sulfate hemihydrate), commonly used in orthopedic casts and dental applications, represents another significant component of medical waste. Upon discarding, POP casts are typically landfilled, despite their potential for beneficial reuse (<xref ref-type="bibr" rid="B33">Navale et al., 2019</xref>). The hydration properties of POP and its ability to form crystalline structures suggest potential applications in soil stabilization.</p>
</sec>
<sec id="s1-3">
<label>1.3</label>
<title>Research rationale and objectives</title>
<p>Recent studies have demonstrated the feasibility of incorporating waste materials including plastics, industrial by-products, and organic wastes into soil stabilization protocols (<xref ref-type="bibr" rid="B20">Haq et al., 2024</xref>; <xref ref-type="bibr" rid="B50">Wang et al., 2022</xref>; <xref ref-type="bibr" rid="B53">Zhu et al., 2022</xref>). However, systematic investigations combining biomedical waste derivatives with comprehensive microstructural characterization remain limited, particularly for Himalayan soils. This study addresses this knowledge gap through the following objectives:<list list-type="bullet">
<list-item>
<p>Evaluate the effects of shredded NG and POP on compaction characteristics, strength parameters, and bearing capacity of silty sand soil.</p>
</list-item>
<list-item>
<p>Determine optimal additive dosages through systematic experimental design.</p>
</list-item>
<list-item>
<p>Elucidate stabilization mechanisms through advanced microstructural analysis (SEM and EDX).</p>
</list-item>
<list-item>
<p>Assess the suitability of stabilized soil for pavement subgrade applications according to IRC standards.</p>
</list-item>
<list-item>
<p>Contribute to circular economic strategies for biomedical waste management.</p>
</list-item>
</list>
</p>
</sec>
</sec>
<sec sec-type="materials|methods" id="s2">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2-1">
<label>2.1</label>
<title>Soil characterization</title>
<p>Soil samples were collected from the Nirjuli-Banderdewa road section (27&#xb0;05&#x2032;N, 93&#xb0;42&#x2032;E) at a depth of 1.5&#x2013;2.0&#xa0;m below ground level (<xref ref-type="fig" rid="F1">Figure 1</xref>). The sampling location was selected based on its history of pavement distress and documented slope instability (<xref ref-type="bibr" rid="B38">Rupa, 2015</xref>). Comprehensive geotechnical characterization was performed according to IS standards (<xref ref-type="table" rid="T1">Table 1</xref>). The soil was classified as silty sand (SM) as per the Unified Soil Classification System, with 47% sand, 52% silt, and 2% clay fractions (<xref ref-type="table" rid="T2">Table 2</xref>). Key properties included a liquid limit of 25%, plasticity index of 25%, specific gravity of 2.65, and maximum dry unit weight of 17.65&#xa0;kN/m<sup>3</sup> at 14.7% optimum moisture content.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Location of the soil sample collection.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g001.tif">
<alt-text content-type="machine-generated">A large landslide area with visible eroded soil and rocky terrain. A retaining wall structure is under construction with metal reinforcements. Vegetation covers the surrounding hill slopes, and a person is seen working in the distance.</alt-text>
</graphic>
</fig>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Geotechnical properties of silty sand.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Description</th>
<th align="center">IS code</th>
<th align="center">Values</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Liquid limit</td>
<td align="center">IS 2720-part V-1985 (<xref ref-type="bibr" rid="B7">Bureau of Indian Standards, 2006a</xref>)</td>
<td align="center">25%</td>
</tr>
<tr>
<td align="center">Plastic limit</td>
<td align="center">IS 2720-part V-1985 (<xref ref-type="bibr" rid="B7">Bureau of Indian Standards, 2006a</xref>)</td>
<td align="center">NIL</td>
</tr>
<tr>
<td align="center">Plasticity index</td>
<td align="center">IS 2720</td>
<td align="center">25%</td>
</tr>
<tr>
<td align="center">Specific gravity</td>
<td align="center">IS: 2720-Part III-1980 (<xref ref-type="bibr" rid="B6">Bureau of Indian Standards, 2002</xref>)</td>
<td align="center">2.5</td>
</tr>
<tr>
<td align="center">Optimum moisture content</td>
<td align="center">IS 2720 part VII-1980</td>
<td align="center">14.7%</td>
</tr>
<tr>
<td align="center">Maximum dry unit weight</td>
<td align="center">IS 2720 part VII-1980</td>
<td align="center">17.65&#xa0;kN/m<sup>3</sup>
</td>
</tr>
<tr>
<td align="center">Soil classification</td>
<td align="center">IS classification</td>
<td align="center">SM</td>
</tr>
</tbody>
</table>
</table-wrap>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Grain size distribution of the soil.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th colspan="2" align="center">Material</th>
<th align="center">Grain size range (mm)</th>
<th align="center">Percentage (%)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="3" align="center">Sand (S)</td>
<td align="center">Coarse sand</td>
<td align="center">4.74 to 2.0</td>
<td align="center">2.81</td>
</tr>
<tr>
<td align="center">Medium sand</td>
<td align="center">2 to 0.425</td>
<td align="center">9.73</td>
</tr>
<tr>
<td align="center">Fine sand</td>
<td align="center">0.425 to 0.075</td>
<td align="center">34.19</td>
</tr>
<tr>
<td colspan="2" align="center">Silt (M)</td>
<td align="center">0.075 to 0.002</td>
<td align="center">52</td>
</tr>
<tr>
<td colspan="2" align="center">Clay (C)</td>
<td align="center">Less than 0.002</td>
<td align="center">2</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s2-2">
<label>2.2</label>
<title>Biomedical waste materials</title>
<sec id="s2-2-1">
<label>2.2.1</label>
<title>Nitrile gloves (NG)</title>
<p>Post-consumer nitrile examination gloves were collected from healthcare facilities in Nirjuli and sterilized using standard steam autoclaving at 121&#xa0;&#xb0;C and 15 psi for 30&#xa0;min before mechanical shredding into 2&#x2013;5&#xa0;mm fragments (<xref ref-type="fig" rid="F2">Figure 2</xref>). Autoclaving is a globally accepted and validated method for treating biomedical waste and has been proven to effectively inactivate bacteria, viruses, and spores under standard operating conditions, ensuring microbiological safety of polymer-based medical disposables. Previous studies have shown that steam sterilization at 121&#xa0;&#xb0;C for durations as short as 15&#xa0;min achieves more than a 6-log reduction in microbial load, meeting international sterilization assurance levels for healthcare materials, and its reliability has been comprehensively documented in the literature (<xref ref-type="bibr" rid="B39">Rutala et al., 2023</xref>). This treatment method is also explicitly recommended by the World Health Organization and national biomedical waste management guidelines for contaminated plastic waste prior to reuse or recycling (<xref ref-type="bibr" rid="B29">Mcdonnell and Burke, 2011</xref>). Following sterilization, the nitrile gloves which are generally composed of an acrylonitrile-butadiene copolymer were shredded, and their inherent tensile strength and chemical resistance were expected to provide discrete reinforcement within the soil matrix, contributing to improved mechanical performance (<xref ref-type="bibr" rid="B11">Consoli et al., 2005</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Nitrile gloves shredded into 2&#x2013;5&#xa0;mm fragments.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g002.tif">
<alt-text content-type="machine-generated">Blue plastic waste on the left is transformed into uniform blue plastic pieces on the right, connected by a blue arrow, indicating a recycling process.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s2-2-2">
<label>2.2.2</label>
<title>Plaster of Paris (POP)</title>
<p>Medical-grade calcium sulfate hemihydrate (CaSO<sub>4</sub>&#xb7;&#xbd;H<sub>2</sub>O) was obtained from discarded orthopedic casts and mechanically cleaned to remove fabric liners and other contaminants. The material was then crushed, sieved through a 150-micron mesh, and thermally dried at 150&#xa0;&#xb0;C for at least 1&#xa0;h, a process that significantly reduces any residual biological risk. X-ray fluorescence analysis confirmed CaO and SO<sub>3</sub> contents of 38.2% and 46.5%, respectively, consistent with medical-grade Plaster of Paris specifications (<xref ref-type="bibr" rid="B46">Singh and Garg, 2000</xref>). Previous studies have shown that calcium sulfate&#x2013;based biomedical wastes pose negligible microbiological hazards after proper physical separation and thermal treatment, making them suitable for secondary reuse in construction and soil stabilization applications. In particular, <xref ref-type="bibr" rid="B33">Navale et al. (2019)</xref> demonstrated the safe reuse of biomedical POP waste following appropriate preprocessing, while <xref ref-type="bibr" rid="B46">Singh and Garg (2000)</xref> reported the chemical stability and environmental safety of waste gypsum and POP derivatives for civil engineering applications.</p>
</sec>
</sec>
<sec id="s2-3">
<label>2.3</label>
<title>Experimental design and sample preparation</title>
<p>A systematic experimental matrix was designed to evaluate individual and combined effects of additives:</p>
<p>Series 1: Soil &#x2b; NG (0.35%, 0.5%, 1.0% by dry weight).</p>
<p>Series 2: Soil &#x2b; POP (3%, 6%, 9% by dry weight).</p>
<p>Series 3: Soil &#x2b; NG &#x2b; POP (all combinations).</p>
<p>Soil was air-dried, pulverized, and sieved through a 4.75&#xa0;mm sieve. Additives were incorporated through dry mixing for 10&#xa0;min to ensure homogeneity, followed by moisture addition to achieve targeted water contents. Samples were compacted immediately to prevent premature hydration reactions.</p>
</sec>
<sec id="s2-4">
<label>2.4</label>
<title>Geotechnical testing</title>
<p>Compaction Tests: Standard Proctor compaction tests were performed as per IS 2720 (Part 7) to determine maximum dry unit weight (MDU) and optimum moisture content (OMC) for each mixture.</p>
<p>Unconfined Compressive Strength (UCS): Cylindrical specimens (38&#xa0;mm diameter, 76&#xa0;mm height) were prepared at OMC and MDU, sealed in plastic bags, and cured at 25&#xa0;&#xb0;C &#xb1; 2&#xa0;&#xb0;C under controlled humidity. Testing was conducted at 0, 7, 14, and 28 days of curing using a strain-controlled loading frame at 1.25&#xa0;mm/min as per IS 2720 (Part 10) (<xref ref-type="bibr" rid="B24">IS:2720, 2011</xref>).</p>
<p>California Bearing Ratio (CBR): CBR tests were performed per IS 2720 (Part 16) (<xref ref-type="bibr" rid="B23">IS:2720, 2002</xref>) on specimens compacted in standard CBR moulds at OMC and MDU. Both soaked (96-h immersion) and unsoaked conditions were evaluated to assess moisture sensitivity. Penetration loads were recorded at 2.5&#xa0;mm and 5.0&#xa0;mm, with CBR values calculated relative to standard loads.</p>
</sec>
<sec id="s2-5">
<label>2.5</label>
<title>Microstructural analysis</title>
<p>The microstructure analysis of soil samples plays a crucial role in understanding the material&#x2019;s properties and behavior under various conditions. Scanning Electron Microscope (SEM) and Electron Dispersive X-ray (EDX) tests were conducted on a total of six samples, the soil, nitrile gloves, POP and the mixes with optimum values that are S&#x2b;0.5%NG, S&#x2b;6%POP and S&#x2b;0.35%NG&#x2b;9%POP.</p>
</sec>
</sec>
<sec sec-type="results|discussion" id="s3">
<label>3</label>
<title>Results and discussion</title>
<sec id="s3-1">
<label>3.1</label>
<title>Compaction characteristics</title>
<sec id="s3-1-1">
<label>3.1.1</label>
<title>Effect of nitrile gloves</title>
<p>
<xref ref-type="fig" rid="F3">Figure 3a</xref> illustrates the variation of MDU and OMC of silty sand soil with increasing percentages of shredded NG. The untreated soil exhibits an MDU of 17.46&#xa0;kN/m<sup>3</sup> and an OMC of 14.7%. With the addition of 0.35% NG, the MDU increases to 17.56&#xa0;kN/m<sup>3</sup>, while the OMC decreases to 14.2%, indicating improved compaction efficiency. This behavior can be attributed to the flexible and thin nitrile fragments occupying interparticle voids, which enhances particle rearrangement and packing under compactive effort. At 0.5% NG content, the soil achieves a near-optimal MDU of 17.50&#xa0;kN/m<sup>3</sup> with a further reduction in OMC to 13.8%. This suggests that an appropriate quantity of nitrile fibers promotes denser soil fabric by improving mechanical interlocking and reducing water demand due to the hydrophobic nature of nitrile polymers. However, at 1% NG content, the MDU decreases to 17.30&#xa0;kN/m<sup>3</sup> despite continued reduction in OMC (13.3%). This reduction in dry unit weight is attributed to excess fiber content, which disrupts soil-to-soil contact, creates a more open structure, and increases internal voids, thereby limiting effective densification. Similar non-linear trends in compaction behavior have been reported for fiber-reinforced soils, where an optimum fiber content enhances packing efficiency, beyond which excessive fibers hinder compaction (<xref ref-type="bibr" rid="B49">Tang et al., 2007</xref>; <xref ref-type="bibr" rid="B12">Consoli et al., 2009a</xref>). These obesrvations indicate that shredded NG reduce moisture demand and marginally improve compaction characteristics at low dosages, with 0.35%&#x2013;0.5% NG representing the optimum range for achieving favorable compaction behavior in silty sand soils.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Variations of OMC and MDU for <bold>(a)</bold> Soil-nitrile mixes, <bold>(b)</bold> Soil-POP mixes, <bold>(c)</bold> 0.5% NG and varying POP content.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g003.tif">
<alt-text content-type="machine-generated">Three graphs illustrate the relationship between MDD (Maximum Dry Density) and OMC (Optimum Moisture Content) with varying percentages of NG, POP, and 0.5%NG+POP. (a) As NG increases, MDD decreases from 17.75 kN/m&#xB3; to 17.3 kN/m&#xB3; while OMC decreases from 14.5% to 13.5%. (b) With increasing POP, MDD slightly increases to 17.8 kN/m&#xB3;, while OMC decreases similarly to 13.5%. (c) For 0.5%NG+POP, MDD increases to 17.9 kN/m&#xB3;, and OMC decreases to 13.25%.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-1-2">
<label>3.1.2</label>
<title>Effect of plaster of Paris</title>
<p>The variation of MDU and OMC of silty sand soil with increasing POP content is observed in <xref ref-type="fig" rid="F3">Figure 3b</xref>. With the addition of 3% POP, the MDU increases to 17.72&#xa0;kN/m<sup>3</sup>, accompanied by a slight reduction in OMC to 14.5%. This improvement is primarily attributed to the filler effect of fine POP particles, which occupy voids between soil grains and enhance particle packing under compactive effort. As the POP content increases to 6%, the MDU further rises to 17.87&#xa0;kN/m<sup>3</sup>, while the OMC decreases to 14.2%, indicating more efficient densification and reduced water demand. At this dosage, POP acts not only as a physical filler but also undergoes partial hydration, forming calcium sulfate dihydrate (gypsum), which improves interparticle bonding and soil fabric continuity. A further increase in POP content to 9% results in a marginal increase in MDU to 17.90&#xa0;kN/m<sup>3</sup>, while the OMC decreases more noticeably to 13.7%. The continued reduction in OMC is associated with water consumption during the hydration of calcium sulfate hemihydrate and the reduced affinity of the stabilized soil matrix for free water. However, the relatively small gain in MDU beyond 6% POP suggests that excess POP may lead to the formation of bulky hydration products and local agglomeration, which limits further improvement in packing efficiency. Similar trends have been reported in gypsum- and calcium-based soil stabilization studies, where an optimum additive content enhances density and reduces moisture demand, while excessive binder content yields diminishing returns in compaction performance (<xref ref-type="bibr" rid="B32">Nalbantoglu and Gucbilmez, 2001</xref>; <xref ref-type="bibr" rid="B37">Ren et al., 2022</xref>). These results indicate that POP significantly improves compaction characteristics of silty sand by increasing dry unit weight and lowering optimum moisture content, with 6%&#x2013;9% POP identified as an effective range, and 6% representing the most efficient balance between densification and material utilization.</p>
</sec>
<sec id="s3-1-3">
<label>3.1.3</label>
<title>Combined effect</title>
<p>
<xref ref-type="fig" rid="F3">Figure 3c</xref> illustrates the variation of MDU and OMC of silty sand soil stabilized with a constant 0.5% shredded NG and varying POP contents. The soil amended with 0.5% NG alone exhibits an MDU of 17.50&#xa0;kN/m<sup>3</sup> and an OMC of 13.80%, indicating that nitrile fibers marginally improve particle packing while reducing moisture demand due to their hydrophobic polymeric nature. With the addition of 3% POP, the MDU increases to 17.80&#xa0;kN/m<sup>3</sup> and the OMC decreases to 13.67%, reflecting the combined effect of POP acting as a fine filler material and the flexible NG fragments promoting better particle rearrangement under compaction. As the POP content is increased to 6%, the MDU further rises to 17.85&#xa0;kN/m<sup>3</sup>, while the OMC reduces to 13.60%, suggesting enhanced densification resulting from void filling by POP particles and partial hydration of calcium sulfate hemihydrate, which improves interparticle bonding and soil fabric continuity. At 9% POP, the MDU reaches its maximum value of 17.95&#xa0;kN/m<sup>3</sup> with a corresponding minimum OMC of 13.50%. The continuous reduction in OMC with increasing POP content is attributed to water consumption during the hydration of POP to gypsum (CaSO<sub>4</sub>&#xb7;2H<sub>2</sub>O) and the formation of a denser, less water-absorptive soil matrix. The progressive increase in MDU demonstrates a synergistic stabilization mechanism, where NG provides discrete reinforcement and flexibility, while POP contributes to binding and pore refinement. However, the relatively smaller increment in MDU beyond 6% POP suggests diminishing compaction efficiency gains, likely due to the formation of bulky hydration products that limit further improvement in packing density. Similar synergistic trends between fibers and calcium-based binders have been reported in stabilized soils, where an optimal combination enhances compaction and reduces moisture sensitivity more effectively than individual additives (<xref ref-type="bibr" rid="B12">Consoli et al., 2009a</xref>; <xref ref-type="bibr" rid="B32">Nalbantoglu and Gucbilmez, 2001</xref>; <xref ref-type="bibr" rid="B37">Ren et al., 2022</xref>). These results indicate that the combined use of 0.5% NG with 6%&#x2013;9% POP significantly improves compaction characteristics of silty sand, with 0.5% NG &#x2b; 6% POP representing an efficient and practical optimum when both densification and material economy are considered.</p>
</sec>
</sec>
<sec id="s3-2">
<label>3.2</label>
<title>Unconfined compressive strength</title>
<sec id="s3-2-1">
<label>3.2.1</label>
<title>Strength development in nitrile gloves-stabilized soil</title>
<p>
<xref ref-type="fig" rid="F4">Figures 4a&#x2013;c</xref> shows the UCS test specimens for soil, Soil with nitrile gloves, Soil with nitrile gloves and POP. The stress-strain curve of plain soil is shown in <xref ref-type="fig" rid="F5">Figure 5a</xref>. Plain soil exhibited minimal strength gain with curing, increasing from 70&#xa0;kPa (0 days) to 93.6&#xa0;kPa (28 days), reflecting limited cementation in natural silty sand. Nitrile gloves addition significantly enhanced both initial and long-term strength as shown in <xref ref-type="fig" rid="F5">Figures 5b&#x2013;d</xref>. For a NG content of 0.5%, the UCS after 28 days of curing reached 241.9&#xa0;kPa (<xref ref-type="fig" rid="F5">Figure 5c</xref>), indicating a substantial enhancement of 158% relative to the untreated soil.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>UCS test specimens for <bold>(a)</bold> soil, <bold>(c)</bold> Soil with nitrile gloves, <bold>(c)</bold> Soil with nitrile gloves and POP.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g004.tif">
<alt-text content-type="machine-generated">Three cylindrical samples labeled (a), (b), and (c) show surface conditions under pressure testing. Sample (a) has several vertical cracks. Sample (b) shows cracks with blue particles embedded. Sample (c) exhibits multiple cracks and more blue particles scattered across the surface.</alt-text>
</graphic>
</fig>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Stress strain curve at different curing periods of <bold>(a)</bold> plain soil, <bold>(b)</bold> soil&#x2b;0.35%NG, <bold>(c)</bold> soil&#x2b;0.5%NG, <bold>(d)</bold> soil&#x2b;1%NG.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g005.tif">
<alt-text content-type="machine-generated">Four graphs labeled (a) to (d) show Unconfined Compressive Strength (UCS) in kilopascals (kPa) versus axial strains in percentage over different curing periods: 0, 7, 14, and 28 days. Each graph uses distinct markers to represent the data for each time frame. Graphs (a), (b), and (d) have similar UCS ranges up to 120 kPa, while graph (c) displays a range up to 300 kPa, showing more significant variations over time.</alt-text>
</graphic>
</fig>
<p>The strengthening mechanism involves discrete reinforcement through stress transfer from soil matrix to tensile-resistant nitrile fragments, which bridge potential failure planes and provide post-peak ductility (<xref ref-type="bibr" rid="B52">Yetimoglu et al., 2005</xref>). However, at 1% NG, 28-day UCS decreased to 99&#xa0;kPa (<xref ref-type="fig" rid="F5">Figure 5d</xref>), indicating that excessive fiber content creates weak zones and reduces effective stress transmission (<xref ref-type="bibr" rid="B30">Michalowski and &#x10c;erm&#xe1;k, 2003</xref>).</p>
<p>
<xref ref-type="fig" rid="F6">Figure 6a</xref> shows the UCS values of soil with various percentages of nitrile gloves at different curing periods. A substantial increase in the UCS values was observed at 0.5% NG content after 28 days of curing which can be attributed to the attainment of an optimum fiber dosage combined with the beneficial effects of extended curing duration. At this fiber content, nitrile gloves (NG) fibers are likely to be uniformly dispersed within the soil matrix, enabling effective stress transfer and improved soil-fiber interaction. Previous studies on fiber-reinforced soils have reported that an optimum fiber content enhances strength primarily through mechanical interlocking, frictional resistance, and the development of a reinforcing network within the soil structure (<xref ref-type="bibr" rid="B49">Tang et al., 2007</xref>; <xref ref-type="bibr" rid="B10">Consoli et al., 2002</xref>).</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>UCS values at different curing periods of <bold>(a)</bold> Soil with different percentages of NG, <bold>(b)</bold> Soil with different percentages of POP.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g006.tif">
<alt-text content-type="machine-generated">Two bar charts labeled (a) and (b) display unconfined compressive strength (UCS) in kilopascals (kPa) over 0, 7, 14, and 28 days of stress. Chart (a) compares soil with varying percentages of nanomaterial (NG: 0.35%, 0.5%, 1%). Chart (b) shows soil with different percentages of a polymer (POP: 3%, 6%, 9%). Each chart has bars with different patterns indicating stress duration. Chart (a) shows maximum UCS with 0.5% NG at 28 days. Chart (b) shows maximum UCS with 6% POP at 28 days.</alt-text>
</graphic>
</fig>
<p>The significant increase in UCS at 28 days compared to the corresponding 14-day curing value for 0.5% NG suggests that curing time plays a critical role in mobilizing the reinforcing mechanism of fibers. Prolonged curing facilitates particle rearrangement, densification of the soil matrix, and improved interfacial bonding between fibers and soil particles, resulting in higher resistance to axial loading (<xref ref-type="bibr" rid="B51">Yetimoglu and Salbas, 2003</xref>; <xref ref-type="bibr" rid="B16">Estabragh et al., 2011</xref>). Similar strength gains have been reported in polymer and fiber-modified soils, where the reinforcing effect becomes more pronounced with time due to gradual enhancement of soil-fiber contact and frictional behavior (<xref ref-type="bibr" rid="B14">Correia et al., 2015</xref>). However, at a lower NG content of 0.35%, the fiber quantity may be insufficient to form a continuous reinforcing network, thereby limiting the contribution of fibers to strength development even at extended curing periods. Conversely, the reduction in UCS observed at higher NG content (1.0%) may be associated with fiber agglomeration and non-uniform distribution, leading to stress concentration and the formation of weak zones within the soil matrix, as widely reported in earlier studies (<xref ref-type="bibr" rid="B13">Consoli et al., 2009b</xref>). Therefore, the increase in UCS at 0.5% NG for 28-day curing represents an optimal balance between fiber content and curing duration, resulting in a substantial improvement in unconfined compressive strength.</p>
</sec>
<sec id="s3-2-2">
<label>3.2.2</label>
<title>Strength development in POP-Stabilized soil</title>
<p>POP addition produced significant strength improvements as shown in <xref ref-type="fig" rid="F6">Figure 6b</xref>. At 6% POP, UCS increased from 156&#xa0;kPa (0 days) to 352&#xa0;kPa (28 days), representing a 109% gain over control soil. The increase in UCS values observed with the addition of Plaster of Paris (POP) can be attributed to its rapid hydration and subsequent formation of interlocking crystalline structures within the soil matrix. Upon mixing with water, POP (calcium sulfate hemihydrate) hydrates to form calcium sulfate dihydrate (gypsum), which acts as a binding agent between soil particles, leading to improved particle interlock and reduced pore spaces. This cementitious action enhances the stiffness and load-bearing capacity of the treated soil, resulting in higher UCS values with increasing POP content and curing time. Similar strength improvements due to gypsum-based and calcium-rich additives have been reported in stabilized soils, where the formation of cementitious bonds and crystalline networks significantly contributes to strength gain (<xref ref-type="bibr" rid="B28">Mahedi et al., 2020</xref>; <xref ref-type="bibr" rid="B3">Barman and Dash, 2022</xref>).</p>
<p>The progressive increase in UCS with curing duration indicates the time-dependent nature of hydration and crystallization processes, which promote densification and improved bonding at the soil&#x2013;binder interface. The peak strength observed at 6% POP suggests an optimum binder content, beyond which further addition (9% POP) resulting in 251&#xa0;kPa gave a comparatively lower strength gain. This reduction may be associated with excess POP leading to incomplete bonding, increased brittleness, or the formation of weak planes due to unreacted material, as reported in earlier studies on chemically stabilized soils (<xref ref-type="bibr" rid="B27">Khemissa and Mahamedi, 2014</xref>; <xref ref-type="bibr" rid="B42">Seco et al., 2011</xref>; <xref ref-type="bibr" rid="B43">Sharma and Sivapullaiah, 2016</xref>). Overall, the observed UCS enhancement confirms the effectiveness of POP as a soil-stabilizing agent when used at an optimum proportion and adequate curing duration.</p>
<p>
<xref ref-type="fig" rid="F7">Figures 7a&#x2013;c</xref> demonstrates the non-linear relationship between POP content and strength, with 6% representing the inflection point. As reported by (<xref ref-type="bibr" rid="B44">Shen et al., 2019</xref>) the hydration of calcium sulfate hemihydrate produces interlocking gypsum crystals that bind soil particles through crystallization pressure and chemical bonding. Microstructural evidence presented in <xref ref-type="sec" rid="s3-4">Section 3.4</xref> confirms this mechanism.</p>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>Stress strain curve of <bold>(a)</bold> soil&#x2b;3%POP, <bold>(b)</bold> Soil&#x2b;6%POP, <bold>(c)</bold> soil&#x2b;9%POP, at different curing periods.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g007.tif">
<alt-text content-type="machine-generated">Three line graphs labeled (a), (b), and (c) showing UCS (Unconfined Compressive Strength) in kPa versus axial strains in percent. Each graph features curves for 0, 7, 14, and 28 days. Graph (a) ranges up to 350 kPa, showing increasing trends. Graph (b) ranges up to 450 kPa with a steeper increase. Graph (c) reaches up to 300 kPa, with consistent trend patterns across days.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-2-3">
<label>3.2.3</label>
<title>Synergistic effects in combined stabilization</title>
<p>
<xref ref-type="fig" rid="F8">Figure 8</xref> illustrates the variation in unconfined compressive strength (UCS) of soil stabilized with combined additions of nitrile gloves (NG) fibers and Plaster of Paris (POP) at different curing periods. For soil containing 0.35% NG (<xref ref-type="fig" rid="F8">Figure 8a</xref>), UCS increases progressively with increasing POP content and curing time, indicating that the cementitious hydration of POP, coupled with fiber-induced reinforcement, enhances particle bonding and stress transfer. A similar trend is observed for soil with 0.5% NG (<xref ref-type="fig" rid="F8">Figure 8b</xref>), where a pronounced improvement in UCS is recorded with increasing POP percentage, particularly at longer curing durations. This behavior suggests a synergistic effect between NG fibers and POP, wherein fibers provide tensile resistance and crack-bridging action, while POP contributes to strength gain through hydration and formation of calcium sulfate dihydrate crystals that bind soil particles. In the case of soil containing 1% NG (<xref ref-type="fig" rid="F8">Figure 8c</xref>), although UCS improves with POP addition and curing, the rate of strength gain is comparatively lower, likely due to fiber agglomeration and non-uniform distribution at higher fiber contents, which may induce weak zones within the soil matrix. The overall results demonstrate that UCS enhancement is governed by an optimum combination of NG content, POP dosage, and curing duration, consistent with findings reported for fiber and binder-stabilized soils in previous studies (<xref ref-type="bibr" rid="B51">Yetimoglu and Salbas, 2003</xref>; <xref ref-type="bibr" rid="B49">Tang et al., 2007</xref>; <xref ref-type="bibr" rid="B10">Consoli et al., 2002</xref>). The observed time-dependent strength gain further confirms the role of curing in facilitating hydration, densification, and improved soil&#x2013;binder&#x2013;fiber interaction.</p>
<fig id="F8" position="float">
<label>FIGURE 8</label>
<caption>
<p>UCS values at different curing periods of <bold>(a)</bold> Soil with 0.35% of NG and different percentages of POP, <bold>(b)</bold> Soil with 0.5% of NG and different percentages of POP, <bold>(c)</bold> Soil with 1% NG and different percentages of POP.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g008.tif">
<alt-text content-type="machine-generated">Three bar charts (a, b, c) show the Unconfined Compressive Strength (UCS) in kilopascals over time (0, 7, 14, 28 days) for different soil compositions. Each composition varies by nano-glass (NG) and perlite powder (POP) percentages: (a) S+0.35%NG, S+0.35%NG+3%POP, S+0.35%NG+6%POP, S+0.35%NG+9%POP; (b) S+0.5%NG, S+0.5%NG+3%POP, S+0.5%NG+6%POP, S+0.5%NG+9%POP; (c) S+1%NG, S+1%NG+3%POP, S+1%NG+6%POP, S+1%NG+9%POP. Each bar set shows increasing UCS values over time.</alt-text>
</graphic>
</fig>
</sec>
</sec>
<sec id="s3-3">
<label>3.3</label>
<title>California Bearing Ratio</title>
<sec id="s3-3-1">
<label>3.3.1</label>
<title>Effect of nitrile gloves and POP on the CBR of soil</title>
<p>
<xref ref-type="fig" rid="F9">Figures 9a&#x2013;e</xref> illustrates the variation of California Bearing Ratio (CBR) values for untreated and treated soils under soaked and unsoaked conditions with varying contents of nitrile gloves (NG) fibers and Plaster of Paris (POP). As observed in <xref ref-type="fig" rid="F9">Figure 9a</xref>, the CBR values initially increase with NG content and attain a peak at an intermediate dosage, beyond which a reduction is noted, indicating the presence of an optimum fiber content. This behavior is commonly attributed to enhanced interparticle friction, tensile resistance, and crack-bridging effects provided by randomly distributed fibers at lower dosages, while excessive fiber content leads to poor dispersion, fiber clustering, and reduced stress transfer efficiency (<xref ref-type="bibr" rid="B51">Yetimoglu and Salbas, 2003</xref>; <xref ref-type="bibr" rid="B49">Tang et al., 2007</xref>). <xref ref-type="fig" rid="F9">Figure 9b</xref> shows that POP addition alone results in a moderate improvement in unsoaked CBR due to the formation of cementitious bonds arising from hydration and crystallization processes, however, soaked CBR values remain comparatively lower because moisture reduces matric suction and weakens interparticle bonding (<xref ref-type="bibr" rid="B42">Seco et al., 2011</xref>). <xref ref-type="fig" rid="F9">Figures 9c&#x2013;e</xref> demonstrate a significant enhancement in CBR when NG and POP are used in combination, particularly at intermediate POP contents, indicating a synergistic effect between fiber reinforcement and binder-induced cementation. The highest CBR values were observed for soil containing 0.5% NG with 6% POP, suggesting an optimum balance between tensile reinforcement from fibers and stiffness gain from POP hydration products. Although soaked CBR values are consistently lower than unsoaked values, the treated soils retain substantially higher bearing capacity compared to untreated soil, confirming the effectiveness of combined fiber-binder stabilization under both moisture conditions. Similar synergistic improvements in CBR have been widely reported for fiber and chemically stabilized soils in pavement applications (<xref ref-type="bibr" rid="B17">Estabragh et al., 2012</xref>; <xref ref-type="bibr" rid="B40">Sadek et al., 2010</xref>). The optimal combination (0.5% NG &#x2b; 6% POP) achieved unsoaked CBR of 29% and soaked CBR of 6.8%, representing 429% and 228% improvements over control soil, respectively. According to (<xref ref-type="bibr" rid="B22">IRC, 2018</xref>), these values qualify the stabilized soil for heavily trafficked road subgrades which requires a minimum soaked CBR of 5%.</p>
<fig id="F9" position="float">
<label>FIGURE 9</label>
<caption>
<p>CBR values <bold>(a)</bold> Soil with different NG content, <bold>(b)</bold> Soil with different POP content, <bold>(c)</bold> Soil with 0.35%NG and different POP content, <bold>(d)</bold> Soil with 0.5%NG and different POP content, <bold>(e)</bold> Soil with 1%NG and different POP content.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g009.tif">
<alt-text content-type="machine-generated">Five line graphs labeled (a) to (e) compare California Bearing Ratio (CBR) percentages for unsoaked and soaked conditions. Graph (a) shows variations in CBR with increasing NG contents from zero to one percent. Graphs (b) to (e) illustrate CBR changes with POP contents ranging from zero to nine percent. Each graph indicates differences in trends between unsoaked and soaked samples. Unsoaked samples display fluctuating CBR values, while soaked samples tend to demonstrate lower and stable values across all graphs.</alt-text>
</graphic>
</fig>
</sec>
</sec>
<sec id="s3-4">
<label>3.4</label>
<title>Microstructural analysis</title>
<sec id="s3-4-1">
<label>3.4.1</label>
<title>SEM observations</title>
<p>Scanning Electron Microscope analysis were performed on the plain soil, soil with 0.5% NG addition, soil with 6% POP addition and soil with NG and POP addition. For plain soil, SEM imaging of untreated soil (<xref ref-type="fig" rid="F10">Figure 10a</xref>) revealed a loosely packed structure with angular to sub-angular particles, abundant macropores (10&#x2013;50&#xa0;&#x3bc;m), and minimal inter-particle bonding. The open fabric explains the low strength and high compressibility of natural silty sand. The SEM test of Soil &#x2b;0.5% NG indicated that the addition of NG (<xref ref-type="fig" rid="F10">Figure 10b</xref>) produced a more compact fabric with visible polymer fragments bridging soil particles. The flexible nitrile material conforms to particle surfaces, creating mechanical interlocking and reducing large voids. This bridging effect distributes applied stresses and inhibits crack propagation, consistent with observed strength improvements (<xref ref-type="bibr" rid="B9">Consoli et al., 1998</xref>). The SEM analysis of Soil &#x2b;6% POP indicated that the POP-stabilized soil (<xref ref-type="fig" rid="F10">Figure 10c</xref>) exhibited significant microstructural changes, including needle-like gypsum crystals (5&#x2013;15&#xa0;&#x3bc;m length) growing between soil particles, forming a three-dimensional network. Particle surfaces were coated with fine crystalline material, indicating chemical bonding. Porosity was visibly reduced through crystal growth filling voids. The interlocking gypsum structure provides mechanical strength and water resistance (<xref ref-type="bibr" rid="B31">Miller and Azad, 2000</xref>). The SEM imaging of Soil &#x2b;0.35% NG &#x2b; 9% POP showed that the combined stabilization (<xref ref-type="fig" rid="F10">Figure 10d</xref>) demonstrated complementary mechanisms in which the nitrile fragments provide flexible reinforcement while gypsum crystals create rigid bonds. The resulting composite structure exhibits both strength and toughness, explaining superior performance in UCS and CBR tests.</p>
<fig id="F10" position="float">
<label>FIGURE 10</label>
<caption>
<p>SEM image of <bold>(a)</bold> Soil, <bold>(b)</bold> S&#x2b;0.5% NG, <bold>(c)</bold> S&#x2b;6% POP, <bold>(d)</bold> S&#x2b;0.35%NG&#x2b;9%POP.</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g010.tif">
<alt-text content-type="machine-generated">Scanning electron microscope images showing microstructures at varying conditions. Image (a) highlights large pores. Image (b) shows a bridging effect. Image (c) depicts CSH gel formation. Image (d) displays both bridging effect and CSH gel formation. Each image includes scale bars and magnification details.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-4-2">
<label>3.4.2</label>
<title>EDX analysis</title>
<p>Energy-Dispersive X-ray (EDX) analysis of the plain soil, soil with 0.5% NG addition, soil with 6% POP addition and soil with NG and POP combination were performed to determine the elemental composition and chemical characteristics of the samples. For the plain soil (<xref ref-type="fig" rid="F11">Figure 11a</xref>), elemental composition showed Si (32.1%), Al (8.7%), Fe (4.2%), Ca (2.1%), and O (48.3%), consistent with silicate mineralogy typical of Himalayan sediments (<xref ref-type="bibr" rid="B19">Garzanti et al., 2005</xref>). For Soil &#x2b;0.5% NG (<xref ref-type="fig" rid="F11">Figure 11b</xref>) the presence of N (2.8%) and elevated C (8.4%) confirmed nitrile incorporation. The acrylonitrile-butadiene structure contributes to tensile strength and chemical stability. For Soil &#x2b;6% POP (<xref ref-type="fig" rid="F11">Figure 11c</xref>) substantial increase in Ca (12.3%) and S (8.6%) verified gypsum formation. The Ca/S molar ratio of approximately 1.0 confirms CaSO<sub>4</sub>&#xb7;2H<sub>2</sub>O stoichiometry. Reduction in porosity-related O (42.1%) indicates void filling by hydration products. For Soil &#x2b;0.35% NG &#x2b; 9% POP (<xref ref-type="fig" rid="F11">Figure 11d</xref>) the combined spectra showed elevated Ca (14.8%), S (10.2%), N (1.9%), and C (6.7%), confirming presence of both stabilizers. The high Ca and S content correlates with superior strength and CBR values, validating the synergistic mechanism.</p>
<fig id="F11" position="float">
<label>FIGURE 11</label>
<caption>
<p>EDX result of <bold>(a)</bold> Soil, <bold>(b)</bold> (S&#x2b;0.5%NG), <bold>(c)</bold> (S&#x2b;6%POP), <bold>(d)</bold> (S&#x2b;0.35%NG&#x2b;9%POP).</p>
</caption>
<graphic xlink:href="fbuil-12-1746551-g011.tif">
<alt-text content-type="machine-generated">Four energy-dispersive X-ray spectroscopy (EDS) spectra labeled a, b, c, and d. Spectrum a shows peaks for elements such as C, O, S, Sn, Sb, Cu, and Ca. Spectrum b includes peaks for O, Ti, Fe, Si, Al, Na, and Cu. Spectrum c presents peaks for O, Si, Fe, C, K, Al, and Mo. Spectrum d displays peaks for O, Fe, Si, Al, Ba, and Ca. Each spectrum indicates different elemental compositions and intensities.</alt-text>
</graphic>
</fig>
</sec>
</sec>
</sec>
<sec id="s4">
<label>4</label>
<title>Engineering implications and practical applications</title>
<sec id="s4-1">
<label>4.1</label>
<title>Pavement subgrade suitability</title>
<p>The stabilized soil meets IRC:37-2018 requirements for heavily trafficked flexible pavements (minimum soaked CBR of 5%) (<xref ref-type="bibr" rid="B22">IRC, 2018</xref>). The optimal mixture (0.5% NG &#x2b; 6% POP) provides a safety factor of 1.36 relative to this threshold, accommodating variability in field conditions and long-term degradation. For the Nirjuli-Banderdewa corridor, implementation of this stabilization approach could reduce pavement layer thickness by approximately 150&#xa0;mm, yielding significant cost savings (<xref ref-type="bibr" rid="B21">IRC, 2013</xref>).</p>
</sec>
<sec id="s4-2">
<label>4.2</label>
<title>Environmental and economic benefits</title>
<p>Stabilizing 1&#xa0;km of road (7&#xa0;m width, 0.5&#xa0;m subgrade depth) requires approximately 2.6 tons of nitrile gloves and 31.5 tons of POP. This corresponds to annual biomedical waste generation from approximately 15 medium-sized hospitals, demonstrating scalable waste management potential (<xref ref-type="bibr" rid="B48">Somadas and Sarvade, 2024</xref>). Replacing 100&#xa0;kg of cement with the NG-POP combination avoids approximately 90&#xa0;kg of CO<sub>2</sub> emissions, contributing to climate change mitigation (<xref ref-type="bibr" rid="B18">Flower and Sanjayan, 2007</xref>). Life-cycle assessment is recommended for comprehensive environmental evaluation. Preliminary cost estimates suggest 25%&#x2013;30% savings compared to conventional cement stabilization, primarily due to eliminated material costs for waste-derived additives. However, transportation and processing costs would require a proper site-specific evaluation.</p>
</sec>
<sec id="s4-3">
<label>4.3</label>
<title>Implementation considerations</title>
<p>Biomedical waste collection, segregation, sterilization, storage, and transfer are governed by mandatory regulatory frameworks, which require involvement of licensed healthcare facilities, authorized waste handlers, and documented treatment and traceability protocols. The reuse pathway investigated in this study is therefore based on the following essential assumptions: (i) biomedical waste materials are sourced exclusively from authorized healthcare institutions; (ii) sterilization and preprocessing are completed prior to any material transfer for engineering use; and (iii) subsequent processing and utilization are conducted under institutional, municipal, or government-authorized oversight, rather than at the community or informal level. Moreover, similar regulated reuse models have already been successfully implemented and reported in the literature for biomedical waste ash, sterilized PPE plastics, and gypsum-based medical waste in civil engineering applications, without compromising public health or environmental safety (<xref ref-type="bibr" rid="B50">Wang et al., 2022</xref>; <xref ref-type="bibr" rid="B48">Somadas and Sarvade, 2024</xref>).</p>
<p>Building upon these demonstrated reuse practices, it is essential to address key practical considerations governing material consistency, long-term performance, and regulatory compliance to ensure safe and scalable field implementation:</p>
<p>Biomedical waste composition varies by source and sterilization method. Standardized protocols for material characterization, sterilization, and processing are essential for consistent performance (<xref ref-type="bibr" rid="B1">Al-Alawi et al., 2024</xref>).</p>
<p>While 28-day strength data are promising, field validation through accelerated durability testing (wet-dry, freeze-thaw cycles) and pilot-scale trials is recommended before widespread adoption (<xref ref-type="bibr" rid="B41">Said and Rahhal, 2022</xref>).</p>
<p>Implementation requires coordination with biomedical waste management authorities and compliance with environmental regulations. Leachability testing is advisable to ensure no mobilization of contaminants.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s5">
<label>5</label>
<title>Conclusion</title>
<p>This study demonstrates the technical feasibility and environmental benefits of utilizing biomedical waste, specifically NG and POP, for stabilization of silty sand soil from the seismically active Lower Himalayan region of Arunachal Pradesh. Key findings include:<list list-type="bullet">
<list-item>
<p>The combination of 0.5% nitrile gloves and 6% Plaster of Paris by dry weight provides optimal performance, achieving 275% UCS improvement and more than twice the CBR values compared to untreated soil.</p>
</list-item>
<list-item>
<p>The optimal mixture increases maximum dry unit weight by 7.3% and reduces optimum moisture content by 12%, facilitating field compaction and improving long-term stability.</p>
</list-item>
<list-item>
<p>Time-resolved UCS testing revealed progressive strength gain over 28 days, attributed to gypsum crystallization and development of interlocking crystal networks. The stabilized soil exhibits both increased strength and improved toughness.</p>
</list-item>
<list-item>
<p>Soaked CBR values of 6.8% exceed IRC:37-2018 requirements for heavily trafficked road subgrades, validating the suitability for pavement applications in the study region.</p>
</list-item>
<list-item>
<p>SEM-EDX analysis elucidated dual mechanisms: (a) discrete reinforcement through nitrile fiber bridging, and (b) chemical bonding via gypsum crystal formation. The combined effect produces a composite structure with enhanced fabric integrity and reduced porosity.</p>
</list-item>
<list-item>
<p>This approach offers a circular economic solution for biomedical waste management while addressing critical geotechnical challenges in infrastructure development. Scalability analysis suggests significant waste diversion potential and reduced carbon emissions compared to conventional stabilization.</p>
</list-item>
<list-item>
<p>For the landslide-prone Himalayan region, improved soil strength and moisture resistance contribute to slope stability and pavement longevity, addressing critical infrastructure resilience needs.</p>
</list-item>
</list>
</p>
<sec id="s5-1">
<label>5.1</label>
<title>Future research directions</title>
<p>Long-term field performance monitoring, comprehensive environmental impact assessment including leachability testing, optimization for different soil types, and development of standardized protocols for biomedical waste processing and quality control are recommended to facilitate practical implementation.</p>
</sec>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s6">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>AK: Supervision, Methodology, Conceptualization, Writing &#x2013; review and editing, Writing &#x2013; original draft. YO: Writing &#x2013; review and editing, Formal Analysis, Methodology, Software. OP: Methodology, Writing &#x2013; review and editing, Formal Analysis, Software. PY: Conceptualization, Writing &#x2013; original draft, Data curation. DP: Data curation, Writing &#x2013; original draft.</p>
</sec>
<ack>
<title>Acknowledgements</title>
<p>The authors acknowledge the Department of Civil Engineering, North Eastern Regional Institute of Science and Technology, for providing laboratory facilities. We thank the healthcare facilities in Nirjuli for providing biomedical waste materials and the Central Instrumentation Facility for SEM-EDX analysis.</p>
</ack>
<sec sec-type="COI-statement" id="s9">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="s10">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="s11">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
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<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2198880/overview">Jaroslaw Rybak</ext-link>, Wroc&#x142;aw University of Science and Technology, Poland</p>
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<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3330672/overview">Sumalatha J</ext-link>, Ramaiah Institute of Technology, India</p>
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