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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Built Environ.</journal-id>
<journal-title>Frontiers in Built Environment</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Built Environ.</abbrev-journal-title>
<issn pub-type="epub">2297-3362</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">1626770</article-id>
<article-id pub-id-type="doi">10.3389/fbuil.2025.1626770</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Built Environment</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Sustainable indoor air purification using treated puffed rice waste: a functional and structural material evaluation</article-title>
<alt-title alt-title-type="left-running-head">Saleh 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.2025.1626770">10.3389/fbuil.2025.1626770</ext-link>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Dar Saleh</surname>
<given-names>Abeer</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/3160582/overview"/>
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<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
<role content-type="https://credit.niso.org/contributor-roles/Writing - review &#x26; editing/"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Khoukhi</surname>
<given-names>Maatouk</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<uri xlink:href="https://loop.frontiersin.org/people/3061175/overview"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Mohammad</surname>
<given-names>Ameera</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/resources/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Al Marzouqi</surname>
<given-names>Ali</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/resources/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Bessadok-Jemai</surname>
<given-names>Abdelbasset</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
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<aff id="aff1">
<sup>1</sup>College of Engineering, <institution>UAE University</institution>, <addr-line>Al-Ain</addr-line>, <country>United Arab Emirates</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>King Saud University</institution>, <addr-line>Riyadh</addr-line>, <country>Saudi Arabia</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/188350/overview">Hazim Bashir Awbi</ext-link>, University of Reading, United Kingdom</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3079458/overview">Marwa Fahmy</ext-link>, Helwan University, Egypt</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3082229/overview">Nicola Pisacane</ext-link>, University of Campania Luigi Vanvitelli, Italy</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Maatouk Khoukhi, <email>mkhoukhi@uaeu.ac.ae</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>14</day>
<month>08</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>11</volume>
<elocation-id>1626770</elocation-id>
<history>
<date date-type="received">
<day>13</day>
<month>05</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>07</day>
<month>07</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Dar Saleh, Khoukhi, Mohammad, Al Marzouqi and Bessadok-Jemai.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Dar Saleh, Khoukhi, Mohammad, Al Marzouqi and Bessadok-Jemai</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). 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.</p>
</license>
</permissions>
<abstract>
<sec>
<title>Introduction</title>
<p>The study addresses IAQ and rice waste management with a bio-based material for CO&#x2082; capture.</p>
</sec>
<sec>
<title>Methods</title>
<p>Rice was thermally puffed and treated with NaOH. Characterization and performance evaluation were conducted.</p>
</sec>
<sec>
<title>Results</title>
<p>Achieved 38% CO&#x2082; removal at 2 M NaOH treatment, with enhanced porosity confirmed.</p>
</sec>
<sec>
<title>Discussion</title>
<p>The material provides a sustainable IAQ solution, suitable for architectural integration.</p>
</sec>
</abstract>
<kwd-group>
<kwd>bio-based purification material</kwd>
<kwd>carbon capture</kwd>
<kwd>environmental sustainability</kwd>
<kwd>indoor pollutants</kwd>
<kwd>energy saving</kwd>
</kwd-group>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Indoor Environment</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>Indoor environments are complex ecosystems influenced by outdoor conditions, building design, and occupant activities. These factors contribute to the presence of various indoor pollutants, including chemical gases such as carbon monoxide (CO), carbon dioxide (CO<sub>2</sub>), ozone (O<sub>3</sub>), and volatile organic compounds (VOCs), as well as biological contaminants and particulate matter (PM) (<xref ref-type="bibr" rid="B23">Levin, 2003</xref>). Among these, CO<sub>2</sub> has received increasing attention due to its adverse effects on human health and cognitive function at elevated concentrations (<xref ref-type="bibr" rid="B27">Mewomo et al., 2023</xref>). While strategies such as improved ventilation and the deployment of purification technologies have been widely studied, the growing emphasis on sustainable construction introduces additional challenges: the use of recycled or waste-based materials, although environmentally beneficial, can sometimes exacerbate IAQ issues (<xref ref-type="bibr" rid="B10">Choe et al., 2022</xref>).</p>
<p>The importance of IAQ is amplified by the fact that individuals spend up to 90% of their time indoors (<xref ref-type="bibr" rid="B12">Du et al., 2011</xref>). Poor IAQ is linked to a variety of health outcomes, from short-term symptoms like headaches and dizziness to long-term respiratory and cardiovascular diseases (<xref ref-type="bibr" rid="B48">Yang et al., 2004</xref>). Furthermore, insufficient ventilation and elevated indoor CO<sub>2</sub> levels are contributing factors to Sick Building Syndrome (SBS), particularly in educational and occupational settings (<xref ref-type="bibr" rid="B9">Burge, 2004</xref>; <xref ref-type="bibr" rid="B25">L&#xf3;pez et al., 2023</xref>). Long-term exposure to CO<sub>2</sub> concentrations exceeding typical indoor baselines (e.g., 1,000&#x2013;2,000 ppm) has been shown to impair productivity and well-being (<xref ref-type="bibr" rid="B3">Alharthi et al., 2022</xref>), and recent studies have used CO<sub>2</sub> levels as proxies for assessing airborne infection risks in poorly ventilated areas (<xref ref-type="bibr" rid="B40">Tang et al., 2022</xref>).</p>
<p>In the United Arab Emirates (UAE), these concerns are compounded by another pressing issue: food waste. Nearly 40% of imported rice is discarded annually, posing significant environmental and economic burdens (<xref ref-type="bibr" rid="B22">Kuo, 2013</xref>). This not only exacerbates landfill expansion but also contributes to national CO<sub>2</sub> emissions (<xref ref-type="bibr" rid="B21">Koul et al., 2022</xref>). Existing air purification technologies often rely on costly materials, require high energy inputs, or lack the flexibility for passive deployment in architectural applications. Moreover, there is a notable disconnect between the domains of waste management and indoor environmental control&#x2014;two areas that urgently require integration for sustainable development (<xref ref-type="bibr" rid="B34">Reza et al., 2020</xref>).</p>
<p>This study responds to these interrelated challenges by proposing a novel, bio-based indoor purification material derived from waste rice. The material is produced through thermal puffing to enhance internal porosity and then chemically activated using sodium hydroxide (NaOH) to increase the density of surface hydroxyl groups essential for CO<sub>2</sub> adsorption. The final product is a flexible, moldable medium suitable for integration into ceiling and wall surfaces without reliance on mechanical systems.</p>
<p>The material&#x2019;s efficacy is evaluated through laboratory-scale CO<sub>2</sub> capture experiments, as well as structural and chemical characterization using Fourier Transform Infrared Spectroscopy (FTIR), X-ray Diffraction (XRD), Scanning Electron Microscopy (SEM), and Thermogravimetric Analysis (TGA). The dual physical&#x2013;chemical activation ensures a high surface area and thermal stability while preserving the material&#x2019;s ecological footprint. Compared to conventional methods, the proposed solution is both cost-effective and environmentally sustainable. The current landscape of indoor CO<sub>2</sub> mitigation strategies is summarized in <xref ref-type="table" rid="T1">Table 1</xref>, providing a comparative context for evaluating the strengths and limitations of the new material.</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Survey of existing solutions and their limitations versus the new proposed modified solution.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Method</th>
<th align="left">Benefits</th>
<th align="left">Drawbacks</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Physical Methods</td>
<td align="left">Effective CO<sub>2</sub> capture</td>
<td align="left">Cost-related challenges</td>
</tr>
<tr>
<td align="left">Chemical Methods</td>
<td align="left">Effective CO<sub>2</sub> capture</td>
<td align="left">Energy-intensive, costly, operational issues</td>
</tr>
<tr>
<td align="left">Biological Methods</td>
<td align="left">Environmental friendliness</td>
<td align="left">Space and maintenance limitations</td>
</tr>
<tr>
<td align="left">Wet Sequestration</td>
<td align="left">Effective CO<sub>2</sub> capture</td>
<td align="left">Regeneration challenges, high energy consumption</td>
</tr>
<tr>
<td align="left">Membrane Technology</td>
<td align="left">Controllable diameter, high surface area</td>
<td align="left">High costs, limited lifespan</td>
</tr>
<tr>
<td align="left">Proposed Puffed Rice</td>
<td align="left">Cost-effective, environmentally friendly, effective CO<sub>2</sub> capture</td>
<td align="left">limited durability</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>By transforming rice waste into a value-added purification material, this research offers a practical and scalable solution to two urgent environmental problems: reducing food waste and enhancing indoor air quality. Its modular, low-energy design supports implementation in sustainable building systems and aligns with broader goals of the circular economy and climate resilience.</p>
</sec>
<sec id="s2">
<title>2 Literature review</title>
<p>The intensification of industrial activity, urbanization, and energy demands over the past decades has contributed significantly to the rise in greenhouse gas (GHG) emissions, particularly carbon dioxide (CO<sub>2</sub>), which is predominantly released through the combustion of fossil fuels such as coal, oil, and natural gas (<xref ref-type="bibr" rid="B2">Ahmed et al., 2018</xref>). These emissions, while temporarily reduced during the COVID-19 pandemic due to economic slowdown, continue to exhibit an overall upward trajectory as economies rebound and energy consumption patterns return to pre-pandemic levels (<xref ref-type="bibr" rid="B38">Shafawi et al., 2021</xref>).</p>
<p>The importance of IAQ has grown significantly in recent decades as individuals now spend approximately 80%&#x2013;90% of their time within enclosed environments (<xref ref-type="bibr" rid="B16">Hu et al., 2016</xref>). Numerous studies have established that IAQ exerts a profound influence on human health and productivity, often exceeding the risks posed by outdoor air pollution (<xref ref-type="bibr" rid="B35">Ros&#xe1;rio Filho et al., 2021</xref>; <xref ref-type="bibr" rid="B41">Vil&#x2c7;cekov&#xe1; et al., 2017</xref>). High indoor pollutant concentrations, especially of CO<sub>2</sub>, have been linked to impaired cognitive function, reduced productivity, and adverse health outcomes such as respiratory disorders and fatigue (<xref ref-type="bibr" rid="B47">Yang et al., 2024</xref>; <xref ref-type="bibr" rid="B31">Pang et al., 2021</xref>; <xref ref-type="bibr" rid="B36">Satish et al., 2012</xref>).</p>
<p>CO<sub>2</sub> in indoor environments primarily originates from human respiration, with emissions estimated at approximately 37 g/h per person (<xref ref-type="bibr" rid="B20">Kotol et al., 2014</xref>). Poorly ventilated spaces often exhibit CO<sub>2</sub> concentrations exceeding 1,000 ppm, which can significantly impair cognitive performance and general well-being (<xref ref-type="bibr" rid="B7">Bluyssen et al., 2016</xref>; <xref ref-type="bibr" rid="B4">Al Horr et al., 2016</xref>). Traditional CO<sub>2</sub> capture technologies, while effective in industrial contexts, are generally unsuitable for indoor use due to their operational and infrastructural demands. This limitation underscores the urgent need for innovative materials and passive purification systems tailored for indoor environments (<xref ref-type="bibr" rid="B43">Wang et al., 2020b</xref>).</p>
<p>Recent research into bio-based adsorbents has demonstrated considerable promise for indoor CO<sub>2</sub> mitigation. Biomass-derived materials, particularly those sourced from agricultural by-products, offer a sustainable and cost-effective alternative to conventional purification media due to their inherent porosity and surface functional groups that facilitate gas adsorption (<xref ref-type="bibr" rid="B24">Li et al., 2021</xref>; <xref ref-type="bibr" rid="B49">Yue et al., 2021</xref>; <xref ref-type="bibr" rid="B33">Quan et al., 2023</xref>). These materials not only support CO<sub>2</sub> capture through physical adsorption but also align with principles of circular economy by utilizing waste and reducing landfill dependency (<xref ref-type="bibr" rid="B17">Karimi et al., 2021</xref>; <xref ref-type="bibr" rid="B11">Danish and Ahmad, 2018</xref>). Once expended, such materials can naturally degrade, minimizing environmental impact and contributing to soil enrichment.</p>
<p>The dual functionality of biomass-based adsorbents&#x2014;carbon sequestration and environmental remediation&#x2014;has been increasingly recognized in recent studies advocating for low-carbon construction materials and sustainable building strategies (<xref ref-type="bibr" rid="B26">Makepa and Chihobo, 2024</xref>). This is particularly relevant in regions facing high volumes of agricultural waste, such as the UAE, where rice waste presents a viable feedstock for purification material development.</p>
<p>Furthermore, IAQ is critically determined by several environmental and operational parameters including temperature, relative humidity, and pollutant concentration. Optimal IAQ conditions are typically achieved by maintaining temperatures between 20&#xb0;C and 24&#xb0;C, relative humidity between 30% and 50%, and pollutant concentrations within established thresholds (<xref ref-type="bibr" rid="B8">Branco et al., 2024</xref>). Deviation from these parameters can result in microbial proliferation, occupant discomfort, and compromised ventilation efficiency (<xref ref-type="bibr" rid="B32">Persily, 2015</xref>).</p>
<p>Despite efforts by organizations such as the World Health Organization (WHO) and the American Society of Heating, Refrigerating, and Air-Conditioning Engineers (ASHRAE), gaps remain in standardizing IAQ metrics for residential and educational settings. CO<sub>2</sub> remains a principal indicator due to its correlation with occupancy and ventilation rates, with recommended indoor levels not exceeding 1,000 ppm to avoid adverse health effects (<xref ref-type="bibr" rid="B45">World Health Organization, 2021</xref>; <xref ref-type="bibr" rid="B5">ASHRAE, 2016</xref>).</p>
<p>Emerging literature emphasizes the critical role of educational environments in IAQ discourse. Classrooms often exhibit higher occupant densities and prolonged exposure durations, leading to elevated CO<sub>2</sub> levels and greater vulnerability among children to indoor pollutants (<xref ref-type="bibr" rid="B6">Benka-Coker et al., 2021</xref>). Studies have consistently reported suboptimal air quality in schools across diverse geographic regions, with CO<sub>2</sub> concentrations frequently surpassing the 1,000 ppm threshold due to inadequate ventilation systems (<xref ref-type="bibr" rid="B42">Vouriot et al., 2021</xref>).</p>
<p>These findings substantiate the necessity for targeted IAQ interventions within educational settings, particularly those that are cost-effective, sustainable, and passive in operation. Integrating bio-based CO<sub>2</sub> adsorbents into architectural components such as ceilings and walls offers a promising avenue for continuous, low-maintenance air purification in classrooms and other indoor spaces. Such strategies align with global sustainability agendas and have the potential to significantly improve health outcomes and cognitive performance among occupants.</p>
<sec id="s2-1">
<title>2.1 Overview of sustainable/bio air purification materials</title>
<p>Sustainable and bio-based air purification materials have emerged as a compelling response to the growing demand for environmentally responsible solutions to indoor air pollution. These materials are derived from renewable resources, exhibit low energy requirements during production, and are often biodegradable or recyclable at the end of their lifecycle. Their integration into building systems not only reduces environmental impacts but also enhances the quality of indoor air.</p>
<p>Examplesinclude activated carbon produced from agricultural residues, biochar, and plant-based media such as moss and bamboo, which exhibit natural capabilities for capturing and degrading pollutants (<xref ref-type="bibr" rid="B37">Schripp et al., 2017</xref>). Such materials support passive purification by harnessing biological processes such as biofiltration and phytoremediation, allowing for the removal of volatile organic compounds (VOCs), carbon dioxide (CO<sub>2</sub>), and particulate matter.</p>
<p>The increasing demand for energy-efficient buildings has further stimulated interest in air purification materials that complement sustainable architectural practices. These materials offer the dual benefits of reducing pollutant levels and supporting global objectives for emission reduction and environmental health (<xref ref-type="bibr" rid="B30">Pal et al., 2020</xref>). Their use aligns with contemporary green building frameworks and represents a significant shift towards passive, self-sustaining air purification mechanisms in the built environment.</p>
</sec>
<sec id="s2-2">
<title>2.2 The role of sustainable/bio air purification materials in IAQ</title>
<p>IAQ plays a fundamental role in determining the health, comfort, and productivity of building occupants. Conventional air purification systems, which rely heavily on mechanical filtration and synthetic media, may not be energy-efficient or sustainable in the long term. In contrast, bio-based materials provide a natural, low-energy alternative that continuously filters air without intensive maintenance or power consumption.</p>
<p>Biological air purification systems&#x2014;including green walls and bioactive indoor plants&#x2014;function through natural absorption and metabolic degradation of pollutants such as CO<sub>2</sub>, formaldehyde, and benzene (<xref ref-type="bibr" rid="B44">Wang et al., 2014</xref>). These systems not only improve air quality but also regulate indoor humidity, thereby contributing to thermal comfort and health. For instance, moss- or algae-based purification systems have demonstrated potential in absorbing substantial amounts of CO<sub>2</sub> while operating autonomously, with minimal energy input. Additionally, biofilters integrated into HVAC systems use biological agents&#x2014;typically microorganisms like bacteria and fungi&#x2014;to metabolize airborne pollutants. These systems are effective in decomposing VOCs, ammonia, and other common indoor contaminants (<xref ref-type="bibr" rid="B15">Gull&#xf3;n et al., 2017</xref>). Incorporating such purification strategies into architectural elements (e.g., walls, ceilings, ventilation ducts) enables a consistent and passive purification process, reducing reliance on synthetic filters and chemical agents.</p>
<p>Thus, sustainable and bio-based materials present a transformative approach to IAQ management, with implications for public health, energy-building performance, and environmental impact. Their scalability, cost-effectiveness, and ability to work under typical indoor conditions make them highly attractive for contemporary architectural applications.</p>
</sec>
<sec id="s2-3">
<title>2.3 Challenges and opportunities in using sustainable/bio air purification materials in buildings</title>
<p>Despite their potential, the adoption of sustainable and bio-based purification materials in buildings is accompanied by several technical and logistical challenges. These include high initial production and installation costs, variability in performance across environmental conditions, and concerns about long-term durability&#x2014;particularly in living or biologically active systems. Furthermore, scalability remains a concern, as most bio-based solutions are still under pilot or small-scale applications, lacking integration into mainstream construction practices.</p>
<p>Nevertheless, these challenges are counterbalanced by a number of emerging opportunities. Advances in bioengineering and nanomaterials have enabled the design of more robust, high-performing bio-based adsorbents (<xref ref-type="bibr" rid="B39">Soreanu et al., 2013</xref>). Simultaneously, global demand for healthier indoor environments and greater occupant well-being has fueled investment in nature-based solutions. Policies promoting green construction and incentives tied to certification systems such as LEED and WELL have further supported this trend (<xref ref-type="bibr" rid="B13">Geng et al., 2019</xref>).</p>
<p>Importantly, the use of renewable and waste-derived feedstocks contributes to circular economy objectives and waste valorization strategies in construction (<xref ref-type="bibr" rid="B29">Nanda et al., 2016</xref>). <xref ref-type="table" rid="T2">Table 2</xref> summarizes the principal challenges and opportunities associated with the use of bio-based purification materials in architectural contexts.</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Summary of challenges and opportunities associated with sustainable air purification.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Challenges</th>
<th align="left">Opportunities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">High initial costs of bio-based materials</td>
<td align="left">Advancements in bioengineering and nanomaterials (<xref ref-type="bibr" rid="B39">Soreanu et al., 2013</xref>)</td>
</tr>
<tr>
<td align="left">Performance variability due to environmental conditions</td>
<td align="left">Integration with green building certification systems like LEED and WELL (Kibert, 2016)</td>
</tr>
<tr>
<td align="left">Maintenance demands and degradation risk in living systems</td>
<td align="left">Growing consumer demand for healthier indoor environments (<xref ref-type="bibr" rid="B13">Geng et al., 2019</xref>)</td>
</tr>
<tr>
<td align="left">Limited availability and scalability for large-scale construction</td>
<td align="left">Use of renewable/waste-derived resources promotes a circular economy (<xref ref-type="bibr" rid="B29">Nanda et al., 2016</xref>)</td>
</tr>
<tr>
<td align="left">Absence of standardized testing and certification frameworks</td>
<td align="left">Policy incentives and increased investment in sustainable construction materials</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
</sec>
<sec sec-type="materials|methods" id="s3">
<title>3 Materials and methods</title>
<p>This study employs a multi-phase experimental methodology to develop and assess a novel bio-based air purification medium derived from puffed rice waste. The approach integrates systematic physical and chemical treatments to enhance the CO<sub>2</sub> adsorption capacity of puffed rice, followed by structural and performance evaluations under controlled laboratory conditions (<xref ref-type="fig" rid="F1">Figure 1</xref>) (<xref ref-type="bibr" rid="B28">Mohammad et al., 2022</xref>; <xref ref-type="bibr" rid="B18">Khoukhi et al., 2021</xref>; <xref ref-type="bibr" rid="B19">Khoukhi et al., 2022</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Integrated framework for novel rice-based purification materials: Sequential Analysis and testing process.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g001.tif">
<alt-text content-type="machine-generated">Flowchart with three main sections: Optimization, Functionalization, and Evaluation. Optimization includes parameters like buffed rice structure, moisture content (12%-16%), temperature (18%-20%), pressure, puffing time, and grain size. Functionalization involves CO2 capture efficiency and concentration (0.5%-2.5%) comparing treated versus untreated rice structure. Evaluation entails comprehensive testing, physical structure assessment, morphological properties assessment, and techniques like FTIR, TGA, and XRD.</alt-text>
</graphic>
</fig>
<sec id="s3-1">
<title>3.1 Phase 1: physical activation and structural optimization of puffed rice</title>
<p>The first phase of this study focuses on the structural enhancement of puffed rice to serve as the primary substrate for bio-based air purification applications. The objective of this phase is to optimize the physical characteristics of the rice media&#x2014;specifically porosity, surface area, and mechanical integrity&#x2014;to facilitate efficient CO<sub>2</sub> adsorption in indoor environments.</p>
<p>Puffed rice, sourced from puffed waste rice, underwent a series of standardized pre-treatment and thermal activation procedures. The process draws upon conventional biomass activation techniques and is adapted to improve the performance of the material under ambient conditions (<xref ref-type="bibr" rid="B21">Koul et al., 2022</xref>; <xref ref-type="bibr" rid="B34">Reza et al., 2020</xref>; <xref ref-type="bibr" rid="B2">Ahmed et al., 2018</xref>).</p>
<p>The activation protocol consisted of the following sequential steps.<list list-type="simple">
<list-item>
<p>&#x2022; <bold>Moisture Reduction:</bold> The cleaned rice was air-dried at ambient temperature until moisture content was reduced to below 16%. Maintaining controlled moisture levels was essential to facilitate uniform expansion and effective pore development during heating.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>Thermal Activation:</bold> Dried samples were subjected to controlled heating in a buffing chamber at temperatures between 240&#xb0;C and 280&#xb0;C. This carbonization step promoted the expansion of rice grains and initiated the formation of micro- and mesopores critical for gas-phase adsorption.</p>
</list-item>
</list>
</p>
<p>The outcome of Phase 1 established the optimal thermal processing parameters necessary to yield a structurally robust and porous substrate, ensuring high suitability for subsequent hydroxylation treatments aimed at enhancing CO<sub>2</sub> adsorption efficiency.</p>
</sec>
<sec id="s3-2">
<title>3.2 Phase 2: chemical functionalization with hydroxyl groups for enhanced CO<sub>2</sub> capture</title>
<p>The second phase of the methodology involved chemical activation of the puffed rice media to improve its physicochemical properties&#x2014;specifically pore volume, surface area, and functional group availability&#x2014;all essential for optimizing gas-phase CO<sub>2</sub> adsorption. Alkaline activation was employed due to its well-established capacity to enhance adsorption potential through surface modification (<xref ref-type="bibr" rid="B50">Zhao et al., 2013</xref>).</p>
<p>Chemical activation processes are broadly classified as single-stage or dual-stage, depending on whether thermal carbonization precedes the chemical treatment (<xref ref-type="bibr" rid="B14">Gonz&#xe1;lez-Mart&#xed;n et al., 2021</xref>). In this study, a single-stage activation approach was adopted, in which pre-expanded puffed rice samples were directly immersed in aqueous solutions of sodium hydroxide (NaOH). This choice was motivated by the objective of maintaining moderate processing conditions compatible with sustainable, low-energy material fabrication. To establish an alkaline surface environment favorable for CO<sub>2</sub> interaction&#x2014;given its acidic molecular nature&#x2014;the puffed rice samples were functionalized with hydroxyl groups. Sodium hydroxide solutions of varying molar concentrations (0.25 M&#x2013;2.5 M) were prepared in 500 mL batches. Circular-shaped samples of puffed rice (8&#x2013;10 cm diameter; 1.2 cm thickness) were immersed in each solution using a customized immersion apparatus that ensured consistent exposure and saturation (<xref ref-type="fig" rid="F2">Figure 2</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Functionalization of puffed rice media using the NaOH spray system.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g002.tif">
<alt-text content-type="machine-generated">Apparatus with labeled components: &#x22;Spray Hoses&#x22; directing liquid over cylindrical &#x22;Puffed Rice Media&#x22; arranged on shelves, and &#x22;NaOH Containers&#x22; positioned at the base.</alt-text>
</graphic>
</fig>
<p>Following the immersion treatment, the samples were rinsed and air-dried. Both treated and untreated samples were subjected to comparative characterization to quantify the chemical activation&#x2019;s effectiveness.<list list-type="simple">
<list-item>
<p>&#x2022; <bold>Fourier Transform Infrared Spectroscopy (FTIR)</bold>: Conducted using an IRTracer-100 spectrometer (Shimadzu, Japan), FTIR analysis was used to identify changes in functional groups post-treatment, particularly the incorporation of hydroxyl (-OH) and carboxyl functionalities.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>Thermogravimetric Analysis (TGA)</bold>: Using a Q500 analyzer (TA Instruments), thermal degradation patterns and material stability were assessed under a nitrogen atmosphere with a controlled heating rate of 15&#xb0;C/min.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>X-ray Diffraction (XRD)</bold>: Structural and crystallinity changes were examined using Cu K&#x3b1; radiation (&#x3bb; &#x3d; 1.54 &#xc5;), operated at 30 mA and 40 kV, with a 2&#x3b8; scan range from 5&#xb0; to 70&#xb0;, advancing at 2&#xb0;/min.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>Scanning Electron Microscopy (SEM)</bold>: The microstructural evolution of the treated surfaces was examined using SEM imaging at various magnifications to reveal pore structure, surface roughness, and morphological uniformity.</p>
</list-item>
</list>
</p>
</sec>
<sec id="s3-3">
<title>3.3 Phase 3: laboratory evaluation of CO<sub>2</sub> capture efficiency</title>
<p>To determine the functional performance of the treated puffed rice media, a series of controlled experiments were conducted using a laboratory-scale CO<sub>2</sub> contactor system. This phase aimed to quantify the adsorption capacity of the bio-based material under standardized conditions simulating indoor air quality environments. The testing apparatus consisted of a transparent plexiglass column designed to facilitate vertical gas flow through a packed bed of the adsorbent material as shown in <xref ref-type="fig" rid="F3">Figure 3</xref>.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>The experimental column setup employed to test the material&#x2019;s efficiency in capturing CO<sub>2</sub>.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g003.tif">
<alt-text content-type="machine-generated">Diagram showing two columns for gas flow experiments. Left column features a pressure gauge, control panel, and puffed rice media. Right column has a plexiglass column with gas inlet and outlet. Both columns have structural supports.</alt-text>
</graphic>
</fig>
<p>A pre-mixed gas containing 10% CO<sub>2</sub> by volume was introduced at a constant flow rate from a certified pressurized cylinder. The puffed rice medium&#x2014;either untreated or chemically functionalized with NaOH&#x2014;was packed into the column to a height of 20 cm, accounting for approximately 20% of the total column volume. Each experimental run lasted 6 h, during which the concentration of CO<sub>2</sub> at the column outlet was continuously monitored using a calibrated infrared CO<sub>2</sub> gas analyzer. Separate tests were performed for each variant of NaOH-treated samples (0.25 M&#x2013;2.5 M), along with untreated control samples. The objective was to evaluate the relationship between hydroxylation level and CO<sub>2</sub> adsorption capacity.</p>
<p>This phase enabled direct performance comparison across various treatment levels, confirming the effectiveness of chemical functionalization in enhancing the CO<sub>2</sub> capture capacity of the puffed rice-based purification medium under realistic environmental conditions.</p>
</sec>
<sec id="s3-4">
<title>3.4 Phase 4: comparative analysis with existing activated bio-based materials</title>
<p>To contextualize the performance and applicability of the developed puffed rice-based purification media, a comparative evaluation is undertaken against a range of benchmark activated bio-based materials widely utilized for carbon dioxide (CO<sub>2</sub>) adsorption in indoor air quality enhancement. This analysis emphasizes a suite of physicochemical and operational metrics, including specific surface area, adsorption capacity, activation conditions, and sustainability considerations.</p>
<p>The critical parameters examined encompass.<list list-type="simple">
<list-item>
<p>&#x2022; <bold>Surface Area (m</bold>
<sup>
<bold>2</bold>
</sup>
<bold>/g):</bold> A primary determinant of adsorption performance, as higher surface areas facilitate greater pollutant contact and retention.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>CO</bold>
<sub>
<bold>2</bold>
</sub> <bold>Adsorption Capacity:</bold> Typically expressed in mmol/g or as a percentage reduction in CO<sub>2</sub> levels, this metric offers a direct indicator of material efficacy.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>Activation Techniques:</bold> Both thermal and chemical activation methods impact pore structure and surface functionality, thereby influencing performance.</p>
</list-item>
<list-item>
<p>&#x2022; <bold>Sustainability and Form Factor Adaptability:</bold> Parameters such as feedstock renewability, biodegradability, and material geometry determine the practical and environmental feasibility of deployment in building applications.</p>
</list-item>
</list>
</p>
<p>
<xref ref-type="table" rid="T3">Table 3</xref> presents a summary of typical performance ranges for these indicators among high-performing bio-based materials.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Key performance indicators for bio-based CO<sub>2</sub> adsorption materials.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Property</th>
<th align="center">Typical range/Importance</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">Surface Area</td>
<td align="center">600&#x2013;1,300 m<sup>2</sup>/g &#x2013; Higher surface area enhances CO<sub>2</sub> adsorption potential</td>
</tr>
<tr>
<td align="center">CO<sub>2</sub> adsorption capacity</td>
<td align="center">2.5&#x2013;6 mmol/g or equivalent % reduction &#x2013; Direct measure of purification performance</td>
</tr>
<tr>
<td align="center">Activation temperature</td>
<td align="center">500&#xb0;C&#x2013;900&#xb0;C &#x2013; Higher temperatures improve porosity but increase energy cost</td>
</tr>
<tr>
<td align="center">Chemical activation agents</td>
<td align="center">NaOH, KOH, ZnCl<sub>2</sub>, H<sub>3</sub>PO<sub>4</sub> &#x2013; Commonly used to enhance pore structure and functional group density</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
</sec>
<sec sec-type="results|discussion" id="s4">
<title>4 Results and discussion</title>
<sec id="s4-1">
<title>4.1 Effects of moisture content and temperature on material porosity</title>
<p>This section examines the impact of moisture content and thermal activation on the porosity and puffing efficiency of the treated puffed rice media, a crucial precursor for CO<sub>2</sub> adsorption in indoor air purification. Porosity&#x2014;quantified here by the puffing percentage (i.e., thickness expansion)&#x2014;directly influences the surface area and the availability of active adsorption sites, which are fundamental for enhancing gas uptake performance.</p>
<p>The experimental matrix consisted of five moisture content levels (12%, 14%, 16%, 18%, and 20%) across four thermal activation conditions (200&#xb0;C, 220&#xb0;C, 240&#xb0;C, and 260&#xb0;C). Puffing thickness (cm) was recorded as an indicator of porosity development (<xref ref-type="fig" rid="F4">Figure 4</xref>). visualizes the distribution of puffing percentages for different moisture contents and temperatures.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Influence of moisture content and temperature on puffing percentage of puffed rice media.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g004.tif">
<alt-text content-type="machine-generated">Line graph showing the relationship between moisture content and puffing percentage at four temperatures: 200, 220, 240, and 260 degrees Celsius. Puffing percentage increases with moisture content and varies by temperature, with higher temperatures resulting in greater puffing.</alt-text>
</graphic>
</fig>
<p>To derive a systematic ranking of optimal conditions, a Multi-Criteria Decision Making (MCDM) approach was employed. The criteria weights were equally distributed across all temperature conditions. <xref ref-type="table" rid="T4">Table 4</xref> summarizes the normalized puffing responses and resulting MCDM scores. The moisture content of 18% emerged as the optimal condition, achieving the highest aggregate ranking across all thermal levels.</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>MCDM evaluation of moisture content on puffing performance across thermal conditions.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Moisture content (%) and temperature</th>
<th colspan="4" align="center">Puffing (thickness cm)</th>
<th rowspan="2" align="center">MCDM score</th>
<th rowspan="2" align="center">Rank</th>
</tr>
<tr>
<th align="center">200&#xb0;C</th>
<th align="center">220&#xb0;C</th>
<th align="center">240&#xb0;C</th>
<th align="center">260&#xb0;C</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="center">12</td>
<td align="center">0.30</td>
<td align="center">0.50</td>
<td align="center">0.50</td>
<td align="center">0.60</td>
<td align="center">0.125</td>
<td align="center">5</td>
</tr>
<tr>
<td align="center">14</td>
<td align="center">0.60</td>
<td align="center">0.70</td>
<td align="center">0.70</td>
<td align="center">0.90</td>
<td align="center">0.375</td>
<td align="center">3</td>
</tr>
<tr>
<td align="center">16</td>
<td align="center">0.80</td>
<td align="center">0.85</td>
<td align="center">0.85</td>
<td align="center">1.00</td>
<td align="center">0.625</td>
<td align="center">2</td>
</tr>
<tr>
<td align="center">18</td>
<td align="center">1.00</td>
<td align="center">1.10</td>
<td align="center">1.10</td>
<td align="center">1.20</td>
<td align="center">1.000</td>
<td align="center">1</td>
</tr>
<tr>
<td align="center">20</td>
<td align="center">0.50</td>
<td align="center">0.50</td>
<td align="center">0.60</td>
<td align="center">0.50</td>
<td align="center">0.250</td>
<td align="center">4</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>The results demonstrate a strong interaction between moisture content and thermal treatment in governing the material&#x2019;s expansion behavior. Moisture levels below 14% yielded suboptimal puffing due to insufficient internal vapor pressure for expansion, while levels above 18% caused structural collapse post-threshold, reducing porosity. At 260&#xb0;C, the puffing effect was maximized for 18% moisture, reaching 1.2 cm in thickness. This analysis confirms that 18% moisture content at 260&#xb0;C offers optimal structural porosity, thereby enhancing the material&#x2019;s theoretical capacity for CO<sub>2</sub> adsorption. These findings form the basis for subsequent chemical functionalization and CO<sub>2</sub> capture evaluation phases presented in the following sections.</p>
</sec>
<sec id="s4-2">
<title>4.2 Sodium hydroxide treatment</title>
<p>Following the physical activation phase, the optimal sample&#x2014;identified based on its superior puffing percentage, structural integrity, and porosity&#x2014;was selected for chemical functionalization. This sample exhibited the most favorable characteristics for adsorption applications and was therefore used in all subsequent chemical activation experiments.</p>
<p>To enhance the CO<sub>2</sub> adsorption potential of the media, chemical activation was carried out using aqueous NaOH solutions at varying concentrations: 0.25 M, 0.5 M, 1 M, 1.25 M, 2 M, and 2.5 M. Each unit of puffed rice media absorbed approximately 18&#x2013;22 mL of NaOH solution. After 24 h of air drying under ambient conditions, the treated samples underwent noticeable physical changes: they darkened in color and adopted a pliable, rubber-like texture. These changes indicate successful surface modification and enhanced reactivity. The introduction of hydroxyl functional groups through NaOH treatment promoted both the physisorption and chemisorption of acidic gases such as CO<sub>2</sub>, thereby improving the material&#x2019;s overall capture efficiency. The next section details the structural and morphological characterization of the material before and after functionalization to explain the impact of NaOH treatment on its performance attributes.</p>
<sec id="s4-2-1">
<title>4.2.1 Structural characterization</title>
<p>These techniques provide information about chemical bonds, crystallinity, thermal behavior, and molecular composition, which reflect the internal structure of the material.</p>
<p>FTIR analysis of untreated and treated samples, shown in <xref ref-type="fig" rid="F5">Figure 5</xref>, identified functional groups. Both samples exhibited peaks for aromatic asymmetric stretching (C&#x3d;C) at 1,250&#x2013;1,500 cm&#x2212;1 and the C&#x3d;O acetyl group at 1,500&#x2013;1,700 cm&#x2212;1, though with reduced intensity in the treated sample. The absorption band at 911&#x2013;1,011 cm&#x2212;1 remained unchanged after sodium hydroxide treatment. However, an expanded absorption range was observed at 3,250&#x2013;3,500 cm&#x2212;1 in the NaOH-treated sample, indicating increased exposure to hydroxyl groups, which likely enhances its reactivity with CO<sub>2</sub> during the absorption/adsorption process.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>FTIR Spectra Comparison for the puffed rice without treatment <bold>(a)</bold> and after modification with sodium hydroxide <bold>(b)</bold>.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g005.tif">
<alt-text content-type="machine-generated">Two graphs displaying transmittance percentages against wavenumber in centimeters inverse. Graph (a) has a purple line, showing transmittance mainly between 75 and 100 percent, with notable dips around 1000 and 3000 wavenumbers. Graph (b) uses a green line, with transmittance also primarily between 75 and 100 percent, featuring significant drops around 900 and 3000 wavenumbers. Both graphs range from 400 to 4000 wavenumbers on the x-axis.</alt-text>
</graphic>
</fig>
<p>The TGA analysis on the untreated and treated puffed media using a Q500 analyzer tracked mass loss during thermal decomposition. DTG curves showed faster mass loss in untreated samples beyond 243.5&#xb0;C (<xref ref-type="fig" rid="F6">Figure 6a</xref>) compared to treated ones (<xref ref-type="fig" rid="F6">Figure 6b</xref>). Between 21&#xb0;C and 309&#xb0;C, untreated media lost 2.3% mass, linked to moisture evaporation (<xref ref-type="fig" rid="F6">Figure 6c</xref>), while treated samples showed a smaller 1.6% reduction (<xref ref-type="fig" rid="F6">Figure 6d</xref>), indicating improved thermal stability. The results suggest that sodium hydroxide-treated media has enhanced stability and potential for effective CO<sub>2</sub> capture below 200&#xb0;C.</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>
<bold>(a)</bold> TGA curve of untreated puffed rice media; <bold>(b)</bold> TGA curve of NaOH-treated puffed rice media; <bold>(c)</bold> DTG curve of untreated media; <bold>(d)</bold> DTG curve of NaOH-treated media.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g006.tif">
<alt-text content-type="machine-generated">Four-panel graph showing thermogravimetric analysis. Panel (a) shows weight percentage versus temperature, decreasing sharply around 350 degrees Celsius. Panel (b) has a similar trend. Panel (c) shows derived weight change percentage peaking around 350 degrees. Panel (d) has a peak around 200 degrees, followed by another smaller peak near 350 degrees.</alt-text>
</graphic>
</fig>
<p>In the XRD test, the untreated sample displayed an A-type diffraction pattern with a peak at 2&#x3b8; &#x3d; 20.3&#xb0;. Sodium hydroxide-treated samples showed a V-type pattern with peaks at 2&#x3b8; &#x3d; 17.2&#xb0; and 20.3&#xb0;, indicating the formation of hydroxide bonds (<xref ref-type="fig" rid="F7">Figure 7</xref>).</p>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>XRD analysis of <bold>(a)</bold> untreated rice media and <bold>(b)</bold> rice media modified with sodium hydroxide.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g007.tif">
<alt-text content-type="machine-generated">Two line graphs labeled (a) and (b). Both graphs plot intensity against 2&#x3B8; degrees. Graph (a) uses a teal line with peaks near 20 degrees, indicated by an orange bar. Graph (b) features a dark blue line with similar peaks, also marked by an orange bar. Intensity ranges from 0 to 250 on both graphs.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s4-2-2">
<title>4.2.2 Morphological characterization</title>
<p>The SEM images revealed structural differences between untreated and treated sample cross-sections (<xref ref-type="fig" rid="F8">Figure 8</xref>). Untreated samples showed a porous arrangement with varying cavity sizes, featuring both empty spaces and solid sections. In treated samples, voids and hollow spaces were notably enlarged, enhancing porosity. This increased porosity improves CO<sub>2</sub> removal efficiency by refining adsorption and absorption, consistent with previous research suggesting that such modifications can boost gas permeability (<xref ref-type="bibr" rid="B39">Soreanu et al., 2013</xref>).</p>
<fig id="F8" position="float">
<label>FIGURE 8</label>
<caption>
<p>Porous Evolution: Changes in Sample Structure Pre <bold>(a)</bold>, and post-treatment <bold>(b)</bold>.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g008.tif">
<alt-text content-type="machine-generated">Scanning electron microscope images show two surfaces with rough, layered textures. In image (a), two yellow squares highlight specific areas on a jagged surface. Image (b) displays similar rough textures with two highlighted squares focusing on different sections.</alt-text>
</graphic>
</fig>
</sec>
</sec>
<sec id="s4-3">
<title>4.3 Effect of NaOH concentration on CO<sub>2</sub> adsorption</title>
<p>A series of laboratory-scale evaluations were conducted to assess the CO<sub>2</sub> capture performance of NaOH-treated puffed rice media under controlled conditions. The experimental setup comprised vertically layered media samples (8 cm in diameter and 1&#x2013;1.2 cm in thickness), occupying 20% of the contactor reactor volume. These media layers were exposed to varying NaOH concentrations ranging from 0.5 M to 2.5 M, while a simulated gas stream with an initial CO<sub>2</sub> concentration of 10% was continuously passed through the column. Under optimized conditions, the system achieved a maximum CO<sub>2</sub> removal of 0.37 moles, reducing the CO<sub>2</sub> concentration in the effluent stream to approximately 6.2%.</p>
<p>As illustrated in <xref ref-type="fig" rid="F9">Figure 9</xref>, a pronounced enhancement in CO<sub>2</sub> uptake was observed with increasing NaOH concentration, with peak adsorption occurring at 2.0 M. The untreated puffed rice media exhibited a baseline adsorption efficiency of 22.4%. Treatment with 2.0 M NaOH elevated this efficiency to 38.0%, corresponding to an improvement of approximately 84% compared to the untreated control.</p>
<fig id="F9" position="float">
<label>FIGURE 9</label>
<caption>
<p>CO<sub>2</sub> loading as a function of the molarity of sodium hydroxide solution.</p>
</caption>
<graphic xlink:href="fbuil-11-1626770-g009.tif">
<alt-text content-type="machine-generated">Graph showing moles of CO2 loaded per square decimeter of treated rice against NaOH solution molarity. The curve starts low, increases moderately, dips around 1.5 molarity, then peaks near 2.1 molarity before decreasing.</alt-text>
</graphic>
</fig>
<p>This increase in CO<sub>2</sub> capture capacity is primarily attributed to the chemical functionalization process, wherein hydroxyl groups introduced by NaOH treatment enhanced the material&#x2019;s affinity toward acidic CO<sub>2</sub> molecules. This mechanism is in line with previous findings that highlight the role of alkaline functional groups in promoting acid-base interactions on bio-adsorbent surfaces. However, a decline in adsorption efficiency was noted at 2.5 M NaOH (0.3 moles), which may be ascribed to over-functionalization effects. Excessive chemical loading can obstruct micropores or induce partial structural collapse, thereby restricting the accessibility of active sites and hindering gas diffusion pathways. Similar effects have been reported in chemically over-activated biochars and carbon-based adsorbents.</p>
</sec>
<sec id="s4-4">
<title>4.4 Comparative evaluation of CO<sub>2</sub> adsorption performance</title>
<p>To evaluate the practical efficacy of the developed puffed rice-based purification media, a comparative assessment was conducted against selected state-of-the-art bio-based and activated carbon materials widely reported in the literature for CO<sub>2</sub> adsorption. This comparison considered not only adsorption capacity, but also activation temperature, processing complexity, sustainability, and potential for architectural integration. Such multi-dimensional benchmarking is essential to ascertain the innovative contribution and applied value of the proposed material.</p>
<p>As summarized in <xref ref-type="table" rid="T5">Table 5</xref>, materials such as coconut shell activated carbon, bamboo-derived activated carbon, and agricultural biochar represent common standards in the field of low-cost CO<sub>2</sub> sorbents. Coconut-shell activated carbon, for instance, achieves a high adsorption range (4.5&#x2013;6.2 mmol/g) due to its well-developed microporous structure, but requires high-energy thermal activation exceeding 900&#xb0;C and often relies on chemical activation with KOH, which may introduce corrosivity concerns and post-treatment waste challenges (<xref ref-type="bibr" rid="B46">Yang et al., 2010</xref>).</p>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>Comparative characteristics of selected bio-based materials for CO<sub>2</sub> adsorption.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Material</th>
<th align="left">Activation process</th>
<th align="left">CO<sub>2</sub> adsorption capacity (% or mmol/g)</th>
<th align="left">Key features and application potential</th>
<th align="left">Reference</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<bold>Coconut Shell AC</bold>
</td>
<td align="left">Physical &#x2b; KOH at &#x3e;900&#xb0;C</td>
<td align="left">4.5&#x2013;6.2 mmol/g</td>
<td align="left">High microporosity, energy-intensive production</td>
<td align="left">
<xref ref-type="bibr" rid="B46">Yang et al. (2010)</xref>
</td>
</tr>
<tr>
<td align="left">
<bold>Bamboo Biochar</bold>
</td>
<td align="left">Physical &#x2b; KOH at 800&#xb0;C&#x2013;1,000&#xb0;C</td>
<td align="left">&#x223c;4.0 mmol/g</td>
<td align="left">Sustainable, granular form limits integration</td>
<td align="left">
<xref ref-type="bibr" rid="B1">Ahmad et al. (2007)</xref>
</td>
</tr>
<tr>
<td align="left">
<bold>Agricultural Biochar</bold>
</td>
<td align="left">Pyrolysis at 500&#xb0;C&#x2013;700&#xb0;C</td>
<td align="left">&#x223c;2.5&#x2013;3.5 mmol/g</td>
<td align="left">Low cost, eco-friendly, limited reactivity without chemical treatment</td>
<td align="left">
<xref ref-type="bibr" rid="B38">Shafawi et al. (2021)</xref>
</td>
</tr>
<tr>
<td align="left">
<bold>Puffed Rice Media (2.0 M NaOH)</bold>
</td>
<td align="left">Physical &#x2b; NaOH (260&#xb0;C)</td>
<td align="left">4.6 mmol/g</td>
<td align="left">Low-temperature activation, lightweight, integrable into interiors</td>
<td align="left"/>
</tr>
</tbody>
</table>
</table-wrap>
<p>Similarly, bamboo-based biochar activated at temperatures above 800&#xb0;C offers a moderate adsorption performance (&#x223c;4.0 mmol/g), but its granular or powder form limits practical deployment in interior systems without additional binding or encapsulation technologies (<xref ref-type="bibr" rid="B1">Ahmad et al., 2007</xref>). Agricultural waste-derived biochars, while sustainable and low-cost, typically exhibit lower CO<sub>2</sub> uptake (&#x223c;2.5&#x2013;3.5 mmol/g) unless enhanced through chemical activation, and their morphology often lacks the structural uniformity required for systematic deployment (<xref ref-type="bibr" rid="B38">Shafawi et al., 2021</xref>).</p>
<p>In contrast, the proposed puffed rice media activated through a two-step process&#x2014;thermal expansion at 260&#xb0;C followed by chemical functionalization with 2.0 M NaOH&#x2014;demonstrated a CO<sub>2</sub> adsorption capacity of approximately 4.6 mmol/g (equivalent to 38% CO<sub>2</sub> removal under test conditions and the material mass). This performance is comparable to high-end bio-adsorbents, with the added advantages of lower thermal processing energy, material biodegradability, and ease of geometric adaptation into indoor paneling systems.</p>
<p>The lightweight nature (&#x223c;8 g per unit), moldability, and passive operation potential of the treated puffed rice panels suggest their high suitability for integration into indoor air purification strategies&#x2014;particularly in resource-constrained or retrofit scenarios. Additionally, the material supports modular deployment without reliance on electricity or auxiliary equipment, aligning with current sustainability targets and net-zero emission goals in the built environment sector.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s5">
<title>5 Conclusion</title>
<p>This study offers a novel solution to two pressing environmental issues: food waste management and the development of sustainable, eco-friendly construction materials. By repurposing waste rice grains, the research presents an innovative material with significant potential for improving IAQ through CO<sub>2</sub> capture.</p>
<p>Experimental findings emphasized the critical role of moisture content and temperature in optimizing the puffing and expansion process of rice. The material achieved maximum thickness and porosity at 18% moisture content and a temperature of 260&#xb0;C, resulting in an enhanced internal structure essential for CO<sub>2</sub> absorption. After treatment with NaOH, the puffed rice media demonstrated improved flexibility and adaptability to various molds and designs, highlighting its suitability for diverse architectural applications.</p>
<p>The NaOH treatment not only improved the structural properties of the material but also significantly increased its CO<sub>2</sub> capture efficiency. This enhancement is attributed to the formation of additional hydroxyl groups on the material&#x2019;s surface, which facilitated CO<sub>2</sub> absorption and adsorption mechanisms. These findings were corroborated by various analytical techniques, including FTIR, XRD, SEM, and TGA.</p>
<p>Laboratory-scale tests further validated the practical application of the treated rice media, demonstrating its ability to remove 38% of CO<sub>2</sub> from a controlled gas mixture. This substantial reduction in CO<sub>2</sub> levels underscores the material&#x2019;s potential for real-world applications, particularly in passive air purification systems for buildings. Its ability to function without energy-intensive mechanical systems positions it as a promising candidate for improving IAQ in sustainable architecture.</p>
<p>Future research should focus on using advanced simulation tools to model the material&#x2019;s performance in real-life conditions, such as different room sizes, airflow rates, and CO<sub>2</sub> concentrations. These simulations will help refine the material&#x2019;s design, optimizing parameters like thickness, surface area, and placement within indoor spaces. Additionally, investigating the material&#x2019;s lifecycle, including durability and recyclability, will be crucial for assessing its overall environmental impact. Long-term performance, especially in high-humidity environments, remains another key area for further exploration to ensure the material&#x2019;s viability and sustainability over time.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s6">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>AD: Conceptualization, Data curation, Formal analysis, Methodology, Writing &#x2013; original draft, Writing &#x2013; review and editing. MK: Funding acquisition, Project administration, Supervision, Writing &#x2013; review and editing. AM: Resources, Supervision, Writing &#x2013; original draft. AA: Resources, Supervision, Writing &#x2013; original draft. AB-J: Resources, Supervision, Writing &#x2013; original draft.</p>
</sec>
<sec sec-type="funding-information" id="s8">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research and/or publication of this article. This work was supported by AUA-UAEU Joint Research (Grant Code: G00004224).</p>
</sec>
<sec sec-type="COI-statement" id="s9">
<title>Conflict of interest</title>
<p>The authors declares that the research 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) declare that no Generative AI was used in the creation of this manuscript.</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>
<ref-list>
<title>References</title>
<ref id="B1">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ahmad</surname>
<given-names>A. L.</given-names>
</name>
<name>
<surname>Loh</surname>
<given-names>M. M.</given-names>
</name>
<name>
<surname>Aziz</surname>
<given-names>J. A.</given-names>
</name>
</person-group> (<year>2007</year>). <article-title>Preparation and characterization of activated carbon from bamboo by microwave-induced KOH activation</article-title>. <source>Carbon</source> <volume>45</volume> (<issue>3</issue>), <fpage>568</fpage>&#x2013;<lpage>575</lpage>. <pub-id pub-id-type="doi">10.1016/j.carbon.2006.10.029</pub-id>
</citation>
</ref>
<ref id="B2">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ahmed</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Bakar</surname>
<given-names>M. S. A.</given-names>
</name>
<name>
<surname>Azad</surname>
<given-names>A. K.</given-names>
</name>
<name>
<surname>Sukri</surname>
<given-names>R. S.</given-names>
</name>
<name>
<surname>Mahlia</surname>
<given-names>T. M. I.</given-names>
</name>
</person-group> (<year>2018</year>). <article-title>Potential thermochemical conversion of bioenergy from Acacia species in Brunei Darussalam: a review</article-title>. <source>Renew. Sustain. Energy Rev.</source> <volume>82</volume>, <fpage>3060</fpage>&#x2013;<lpage>3076</lpage>. <pub-id pub-id-type="doi">10.1016/j.rser.2017.10.032</pub-id>
</citation>
</ref>
<ref id="B3">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Alharthi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Hanif</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Alamoudi</surname>
<given-names>H.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Impact of environmental pollution on human health and financial status of households in MENA countries: future of using renewable energy to eliminate the environmental pollution</article-title>. <source>Renew. Energy</source> <volume>190</volume>, <fpage>338</fpage>&#x2013;<lpage>346</lpage>. <pub-id pub-id-type="doi">10.1016/j.renene.2022.03.118</pub-id>
</citation>
</ref>
<ref id="B4">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Al Horr</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Arif</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Kaushik</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Mazroei</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Katafygiotou</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Elsarrag</surname>
<given-names>E.</given-names>
</name>
</person-group> (<year>2016</year>). <article-title>Occupant productivity and office indoor environment quality: a review of the literature</article-title>. <source>Build. Environ.</source> <volume>105</volume>, <fpage>369</fpage>&#x2013;<lpage>389</lpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2016.06.001</pub-id>
</citation>
</ref>
<ref id="B5">
<citation citation-type="book">
<collab>ASHRAE</collab> (<year>2016</year>). <source>Standard 62.1&#x2013;2016 ventilation for acceptable indoor air quality</source>. <publisher-loc>Corners, GA</publisher-loc>: <publisher-name>ASHRAE</publisher-name>.</citation>
</ref>
<ref id="B6">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Benka-Coker</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Young</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Oliver</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Schaeffer</surname>
<given-names>J. W.</given-names>
</name>
<name>
<surname>Manning</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Suter</surname>
<given-names>J.</given-names>
</name>
<etal/>
</person-group> (<year>2021</year>). <article-title>Sociodemographic variations in the association between indoor environmental quality in school buildings and student performance</article-title>. <source>Build. Environ.</source> <volume>206</volume>, <fpage>108390</fpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2021.108390</pub-id>
</citation>
</ref>
<ref id="B7">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Bluyssen</surname>
<given-names>P. M.</given-names>
</name>
<name>
<surname>Roda</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Mandin</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Fossati</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Carrer</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>de Kluizenaar</surname>
<given-names>Y.</given-names>
</name>
<etal/>
</person-group> (<year>2016</year>). <article-title>Self-reported health and comfort in &#x2018;modern&#x2019; office buildings: first results from the European OFFICAIR study</article-title>. <source>Indoor Air</source> <volume>26</volume>, <fpage>298</fpage>&#x2013;<lpage>317</lpage>. <pub-id pub-id-type="doi">10.1111/ina.12196</pub-id>
</citation>
</ref>
<ref id="B8">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Branco</surname>
<given-names>P. T.</given-names>
</name>
<name>
<surname>Sousa</surname>
<given-names>S. I.</given-names>
</name>
<name>
<surname>Dudzi&#x144;ska</surname>
<given-names>M. R.</given-names>
</name>
<name>
<surname>Ruzgar</surname>
<given-names>D. G.</given-names>
</name>
<name>
<surname>Mutlu</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Panaras</surname>
<given-names>G.</given-names>
</name>
<etal/>
</person-group> (<year>2024</year>). <article-title>A review of relevant parameters for assessing indoor air quality in educational facilities</article-title>. <source>Environ. Res.</source> <volume>261</volume>, <fpage>119713</fpage>. <pub-id pub-id-type="doi">10.1016/j.envres.2024.119713</pub-id>
</citation>
</ref>
<ref id="B9">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Burge</surname>
<given-names>P. S.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Sick building syndrome: Figure 1</article-title>. <source>Occup. Environ. Med.</source> <volume>61</volume>, <fpage>185</fpage>&#x2013;<lpage>190</lpage>. <pub-id pub-id-type="doi">10.1136/oem.2003.008813</pub-id>
</citation>
</ref>
<ref id="B10">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Choe</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Shin</surname>
<given-names>J.-S</given-names>
</name>
<name>
<surname>Park</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Kim</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Oh</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Min</surname>
<given-names>K.</given-names>
</name>
<etal/>
</person-group> (<year>2022</year>). <article-title>Inadequacy of air purifier for indoor air quality improvement in classrooms without external ventilation</article-title>. <source>Build. Environ.</source> <volume>207</volume>, <fpage>108450</fpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2021.108450</pub-id>
</citation>
</ref>
<ref id="B11">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Danish</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Ahmad</surname>
<given-names>T.</given-names>
</name>
</person-group> (<year>2018</year>). <article-title>A review on utilization of wood biomass as a sustainable precursor for activated carbon production and application</article-title>. <source>Renew. Sustain. Energy Rev.</source> <volume>87</volume>, <fpage>1</fpage>&#x2013;<lpage>21</lpage>. <pub-id pub-id-type="doi">10.1016/j.rser.2018.02.003</pub-id>
</citation>
</ref>
<ref id="B12">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Du</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Batterman</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Parker</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Godwin</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Chin</surname>
<given-names>J. Y.</given-names>
</name>
<name>
<surname>O&#x27;Toole</surname>
<given-names>A.</given-names>
</name>
<etal/>
</person-group> (<year>2011</year>). <article-title>Particle concentrations and effectiveness of free-standing air filters in bedrooms of children with asthma in Detroit, Michigan</article-title>. <source>Build. Environ.</source> <volume>46</volume> (<issue>11</issue>), <fpage>2303</fpage>&#x2013;<lpage>2313</lpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2011.05.012</pub-id>
</citation>
</ref>
<ref id="B13">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Geng</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Sarkis</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Ulgiati</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Circular economy approaches in the construction industry</article-title>. <source>Resour. Conservation Recycl.</source> <volume>136</volume>, <fpage>11</fpage>&#x2013;<lpage>21</lpage>. <pub-id pub-id-type="doi">10.1016/j.resconrec.2018.04.022</pub-id>
</citation>
</ref>
<ref id="B14">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gonz&#xe1;lez-Mart&#xed;n</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Kraakman</surname>
<given-names>N. J. R.</given-names>
</name>
<name>
<surname>P&#xe9;rez</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Lebrero</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Mu&#xf1;oz</surname>
<given-names>R.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>A state&#x2013;of&#x2013;the-art review on indoor air pollution and strategies for indoor air pollution control</article-title>. <source>Chemosphere</source> <volume>262</volume>, <fpage>128376</fpage>. <pub-id pub-id-type="doi">10.1016/j.chemosphere.2020.128376</pub-id>
</citation>
</ref>
<ref id="B15">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gull&#xf3;n</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>L&#xfa;-Chau</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Moreira</surname>
<given-names>M. T.</given-names>
</name>
<name>
<surname>Lema</surname>
<given-names>J. M.</given-names>
</name>
<name>
<surname>Eibes</surname>
<given-names>G.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Biofiltration of volatile organic compounds: an effective air purification technology</article-title>. <source>Appl. Microbiol. Biotechnol.</source> <volume>101</volume> (<issue>2</issue>), <fpage>2763</fpage>&#x2013;<lpage>2777</lpage>. <pub-id pub-id-type="doi">10.1007/s00253-017-8194-1</pub-id>
</citation>
</ref>
<ref id="B16">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Hu</surname>
<given-names>S. C.</given-names>
</name>
<name>
<surname>Shiue</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Chang</surname>
<given-names>S. M.</given-names>
</name>
<name>
<surname>Chang</surname>
<given-names>Y. T.</given-names>
</name>
<name>
<surname>Tseng</surname>
<given-names>C. H.</given-names>
</name>
<name>
<surname>Mao</surname>
<given-names>C. C.</given-names>
</name>
<etal/>
</person-group> (<year>2016</year>). <article-title>Removal of carbon dioxide in the indoor environment with sorption-type air filters</article-title>. <source>Int. J. LowCarbon Tec.</source> <volume>12</volume>, <fpage>330</fpage>&#x2013;<lpage>334</lpage>. <pub-id pub-id-type="doi">10.1093/ijlct/ctw014</pub-id>
</citation>
</ref>
<ref id="B17">
<citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname>Karimi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Rodrigues</surname>
<given-names>A. E.</given-names>
</name>
<name>
<surname>Silva</surname>
<given-names>J. A.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Biomass as a source of adsorbents for CO2 capture</article-title>. In: <source>Advances in bioenergy and microfluidic applications</source>. <publisher-loc>Amsterdam, Netherlands</publisher-loc>: <publisher-name>Elsevier</publisher-name>. p. <fpage>255</fpage>&#x2013;<lpage>274</lpage>.</citation>
</ref>
<ref id="B18">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Khoukhi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Abeer</surname>
<given-names>D. S.</given-names>
</name>
<name>
<surname>Ahmed</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Abdelbaqi</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Thermal characterization of a new bio-based insulation material containing puffed rice</article-title>. <source>Energies</source> <volume>14</volume> (<issue>18</issue>), <fpage>5700</fpage>. <pub-id pub-id-type="doi">10.3390/en14185700</pub-id>
</citation>
</ref>
<ref id="B19">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Khoukhi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Dar Saleh</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Mohammad</surname>
<given-names>A. F.</given-names>
</name>
<name>
<surname>Hassan</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Abdelbaqi</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Thermal performance and statistical analysis of a new bio-based insulation material produced using grain puffing technique</article-title>. <source>Constr. Build. Mater.</source> <volume>345</volume>, <fpage>128311</fpage>. <pub-id pub-id-type="doi">10.1016/j.conbuildmat.2022.128311</pub-id>
</citation>
</ref>
<ref id="B20">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Kotol</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Rode</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Clausen</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Nielsen</surname>
<given-names>T. R.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Indoor environment in bedrooms in 79 Greenlandic households</article-title>. <source>Build. Environ.</source> <volume>81</volume>, <fpage>29</fpage>&#x2013;<lpage>36</lpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2014.05.016</pub-id>
</citation>
</ref>
<ref id="B21">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Koul</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Yakoob</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Shah</surname>
<given-names>M. P.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Agricultural waste management strategies for environmental sustainability</article-title>. <source>Environ. Res.</source> <volume>206</volume>, <fpage>112285</fpage>. <pub-id pub-id-type="doi">10.1016/j.envres.2021.112285</pub-id>
</citation>
</ref>
<ref id="B22">
<citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname>Kuo</surname>
<given-names>L.</given-names>
</name>
</person-group> (<year>2013</year>). <source>Wasted rice in asia emits over 600 million tonnes of greenhouse gases a year</source>. <publisher-loc>New York, NY</publisher-loc>: <publisher-name>QUARTZ</publisher-name>. <comment>Available online at: <ext-link ext-link-type="uri" xlink:href="https://qz.com/123456/wasted-rice-in-asia-emits-over-600-million-tonnes-of-greenhouse-gases-a-year/">https://qz.com/123456/wasted-rice-in-asia-emits-over-600-million-tonnes-of-greenhouse-gases-a-year/</ext-link>(Accessed July 8, 2024)</comment>.</citation>
</ref>
<ref id="B23">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Levin</surname>
<given-names>H.</given-names>
</name>
</person-group> (<year>2003</year>). <article-title>Indoor air pollutants. Part 1: general description of pollutants, levels and standards</article-title>. <source>Vent. Inf. Pap.</source> <volume>2</volume>, <fpage>12</fpage>.</citation>
</ref>
<ref id="B24">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Li</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Yuan</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Deng</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Zhao</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Lee</surname>
<given-names>K. B.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>A review on biomass-derived CO2 adsorption capture: adsorbent, adsorber, adsorption, and advice</article-title>. <source>Renew. Sustain. Energy Rev.</source> <volume>152</volume>, <fpage>111708</fpage>. <pub-id pub-id-type="doi">10.1016/j.rser.2021.111708</pub-id>
</citation>
</ref>
<ref id="B25">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>L&#xf3;pez</surname>
<given-names>L. R.</given-names>
</name>
<name>
<surname>Dess&#xec;</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Cabrera-Codony</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Rocha-Melogno</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Kraakman</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Naddeo</surname>
<given-names>V.</given-names>
</name>
<etal/>
</person-group> (<year>2023</year>). <article-title>CO2 in indoor environments: from environmental and health risk to potential renewable carbon source</article-title>. <source>Sci. Total Environ.</source> <volume>856</volume>, <fpage>159088</fpage>. <pub-id pub-id-type="doi">10.1016/j.scitotenv.2022.159088</pub-id>
</citation>
</ref>
<ref id="B26">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Makepa</surname>
<given-names>D. C.</given-names>
</name>
<name>
<surname>Chihobo</surname>
<given-names>C. H.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Sustainable pathways for biomass production and utilization in carbon capture and storage&#x2014;a review</article-title>. <source>Biomass Convers. Biorefinery</source> <volume>15</volume>, <fpage>11397</fpage>&#x2013;<lpage>11419</lpage>. <pub-id pub-id-type="doi">10.1007/s13399-024-06010-5</pub-id>
</citation>
</ref>
<ref id="B27">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mewomo</surname>
<given-names>M. C.</given-names>
</name>
<name>
<surname>Toyin</surname>
<given-names>J. O.</given-names>
</name>
<name>
<surname>Iyiola</surname>
<given-names>C. O.</given-names>
</name>
<name>
<surname>Aluko</surname>
<given-names>O. R.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Synthesis of critical factors influencing indoor environmental quality and their impacts on building occupant&#x2019;s health and productivity</article-title>. <source>J. Eng. Des. Technol.</source> <volume>21</volume> (<issue>2</issue>), <fpage>619</fpage>&#x2013;<lpage>634</lpage>. <pub-id pub-id-type="doi">10.1108/jedt-10-2021-0595</pub-id>
</citation>
</ref>
<ref id="B28">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mohammad</surname>
<given-names>A. F.</given-names>
</name>
<name>
<surname>Dar Saleh</surname>
<given-names>A. F.</given-names>
</name>
<name>
<surname>Khoukhi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Ali</surname>
<given-names>H. A.-M.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>A New method for capturing CO2 from effluent gases using a rice-based product</article-title>. <source>Energies</source> <volume>15</volume> (<issue>6</issue>), <fpage>2287</fpage>. <pub-id pub-id-type="doi">10.3390/en15062287</pub-id>
</citation>
</ref>
<ref id="B29">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Nanda</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Dalai</surname>
<given-names>A. K.</given-names>
</name>
<name>
<surname>Kozinski</surname>
<given-names>J. A.</given-names>
</name>
</person-group> (<year>2016</year>). <article-title>Biocarbon production from biomass: advances in green air purification materials</article-title>. <source>Environ. Chem. Lett.</source> <volume>14</volume> (<issue>2</issue>), <fpage>195</fpage>&#x2013;<lpage>207</lpage>. <pub-id pub-id-type="doi">10.1007/s10311-016-0551-0</pub-id>
</citation>
</ref>
<ref id="B30">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Pal</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Patidar</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Jain</surname>
<given-names>R.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>Bio-based air purification systems: role in improving indoor air quality</article-title>. <source>J. Environ. Sci. Technol.</source> <volume>14</volume> (<issue>4</issue>), <fpage>451</fpage>&#x2013;<lpage>461</lpage>. <pub-id pub-id-type="doi">10.3923/jest.2020.451.461</pub-id>
</citation>
</ref>
<ref id="B31">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Pang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Cao</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Liang</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>L.</given-names>
</name>
<etal/>
</person-group> (<year>2021</year>). <article-title>The effects of carbon dioxide exposure concentrations on human vigilance and sentiment in an enclosed workplace environment</article-title>. <source>Indoor air</source> <volume>31</volume> (<issue>2</issue>), <fpage>467</fpage>&#x2013;<lpage>479</lpage>. <pub-id pub-id-type="doi">10.1111/ina.12746</pub-id>
</citation>
</ref>
<ref id="B32">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Persily</surname>
<given-names>A.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>Challenges in developing ventilation and indoor air quality standards: the story of ASHRAE Standard 62</article-title>. <source>Build. Environ.</source> <volume>91</volume>, <fpage>61</fpage>&#x2013;<lpage>69</lpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2015.02.026</pub-id>
</citation>
</ref>
<ref id="B33">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Quan</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Zhou</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Wu</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Gao</surname>
<given-names>N.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Biomass-based carbon materials for CO2 capture: a review</article-title>. <source>J. CO2 Util.</source> <volume>68</volume>, <fpage>102373</fpage>. <pub-id pub-id-type="doi">10.1016/j.jcou.2022.102373</pub-id>
</citation>
</ref>
<ref id="B34">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Reza</surname>
<given-names>M. S.</given-names>
</name>
<name>
<surname>Yun</surname>
<given-names>C. S.</given-names>
</name>
<name>
<surname>Afroze</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Radenahmad</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Bakar</surname>
<given-names>M. S. A.</given-names>
</name>
<name>
<surname>Saidur</surname>
<given-names>R.</given-names>
</name>
<etal/>
</person-group> (<year>2020</year>). <article-title>Preparation of activated carbon from biomass and its&#x2019; applications in water and gas purification, a review</article-title>. <source>Arab J. Basic Appl. Sci.</source> <volume>27</volume> (<issue>1</issue>), <fpage>208</fpage>&#x2013;<lpage>238</lpage>. <pub-id pub-id-type="doi">10.1080/25765299.2020.1766799</pub-id>
</citation>
</ref>
<ref id="B35">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ros&#xe1;rio Filho</surname>
<given-names>N. A.</given-names>
</name>
<name>
<surname>Urrutia-Pereira</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>d&#x27;Amato</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Cecchi</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Ansotegui</surname>
<given-names>I. J.</given-names>
</name>
<name>
<surname>Gal&#xe1;n</surname>
<given-names>C.</given-names>
</name>
<etal/>
</person-group> (<year>2021</year>). <article-title>Air pollution and indoor settings</article-title>. <source>World Allergy Organ. J.</source> <volume>14</volume> (<issue>1</issue>), <fpage>100499</fpage>. <pub-id pub-id-type="doi">10.1016/j.waojou.2020.100499</pub-id>
</citation>
</ref>
<ref id="B36">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Satish</surname>
<given-names>U.</given-names>
</name>
<name>
<surname>Mendell</surname>
<given-names>M. J.</given-names>
</name>
<name>
<surname>Shekhar</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Hotchi</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Sullivan</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Streufert</surname>
<given-names>S.</given-names>
</name>
<etal/>
</person-group> (<year>2012</year>). <article-title>Is CO2 an indoor pollutant? Direct effects of low-to-moderate CO2 concentrations on human decision-making performance</article-title>. <source>Environ. Health Perspect.</source> <volume>120</volume>, <fpage>1671</fpage>&#x2013;<lpage>1677</lpage>. <pub-id pub-id-type="doi">10.1289/ehp.1104789</pub-id>
</citation>
</ref>
<ref id="B37">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Schripp</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Salge</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Salthammer</surname>
<given-names>T.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Bio-based air purification materials: reducing indoor VOC levels through sustainable solutions</article-title>. <source>Atmos. Environ.</source> <volume>168</volume>, <fpage>78</fpage>&#x2013;<lpage>84</lpage>. <pub-id pub-id-type="doi">10.1016/j.atmosenv.2017.08.059</pub-id>
</citation>
</ref>
<ref id="B38">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Shafawi</surname>
<given-names>A. N.</given-names>
</name>
<name>
<surname>Mohamed</surname>
<given-names>A. R.</given-names>
</name>
<name>
<surname>Lahijani</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Mohammadi</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Recent advances in developing engineered biochar for CO2 capture: an insight into the biochar modification approaches</article-title>. <source>J. Environ. Chem. Eng.</source> <volume>9</volume> (<issue>6</issue>), <fpage>106869</fpage>. <pub-id pub-id-type="doi">10.1016/j.jece.2021.106869</pub-id>
</citation>
</ref>
<ref id="B39">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Soreanu</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Dixon</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Darlington</surname>
<given-names>A.</given-names>
</name>
</person-group> (<year>2013</year>). <article-title>Plant-based air purification systems: engineering biotechnologies for indoor air quality improvement</article-title>. <source>Biotechnol. Adv.</source> <volume>31</volume> (<issue>2</issue>), <fpage>136</fpage>&#x2013;<lpage>142</lpage>. <pub-id pub-id-type="doi">10.1016/j.biotechadv.2012.09.005</pub-id>
</citation>
</ref>
<ref id="B40">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Tang</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Pan</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>C.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Tempo-spatial infection risk assessment of airborne virus via CO2 concentration field monitoring in built environment</article-title>. <source>Build. Environ.</source> <volume>217</volume>, <fpage>109067</fpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2022.109067</pub-id>
</citation>
</ref>
<ref id="B41">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Vil&#x10d;ekov&#xe1;</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Apostoloski</surname>
<given-names>I. Z.</given-names>
</name>
<name>
<surname>Me&#x10d;iarov&#xe1;</surname>
<given-names>L&#x2019;.</given-names>
</name>
<name>
<surname>Burdov&#xe1;</surname>
<given-names>E. K.</given-names>
</name>
<name>
<surname>Kisel&#x2019;&#xe1;k</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Investigation of indoor air quality in houses of Macedonia</article-title>. <source>Int. J. Environ. Res. Public Health</source> <volume>14</volume>, <fpage>37</fpage>. <pub-id pub-id-type="doi">10.3390/ijerph14010037</pub-id>
</citation>
</ref>
<ref id="B42">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Vouriot</surname>
<given-names>C. V.</given-names>
</name>
<name>
<surname>Burridge</surname>
<given-names>H. C.</given-names>
</name>
<name>
<surname>Noakes</surname>
<given-names>C. J.</given-names>
</name>
<name>
<surname>Linden</surname>
<given-names>P. F.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Seasonal variation in airborne infection risk in schools due to changes in ventilation inferred from monitored carbon dioxide</article-title>. <source>Indoor air</source> <volume>31</volume> (<issue>4</issue>), <fpage>1154</fpage>&#x2013;<lpage>1163</lpage>. <pub-id pub-id-type="doi">10.1111/ina.12818</pub-id>
</citation>
</ref>
<ref id="B43">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname>
<given-names>W. J.</given-names>
</name>
<name>
<surname>Liu</surname>
<given-names>F. L.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Q. X.</given-names>
</name>
<name>
<surname>Yu</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Deng</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2020b</year>). <article-title>Efficient removal of CO2 from indoor air using a polyethyleneimine-impregnated resin and its low-temperature regeneration</article-title>. <source>Chem. Eng. J.</source> <volume>399</volume>, <fpage>125734</fpage>. <pub-id pub-id-type="doi">10.1016/j.cej.2020.125734</pub-id>
</citation>
</ref>
<ref id="B44">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>J. S.</given-names>
</name>
<name>
<surname>Wei</surname>
<given-names>W.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Performance of biofiltration for removing volatile organic compounds in indoor air</article-title>. <source>J. Hazard. Mater.</source> <volume>278</volume>, <fpage>437</fpage>&#x2013;<lpage>444</lpage>. <pub-id pub-id-type="doi">10.1016/j.jhazmat.2014.06.021</pub-id>
</citation>
</ref>
<ref id="B45">
<citation citation-type="book">
<collab>World Health Organization</collab> (<year>2021</year>). <source>WHO global air quality guidelines: particulate matter (PM2.5 and PM10), ozone, nitrogen dioxide, sulfur dioxide and carbon monoxide</source>. <publisher-loc>Geneva, Switzerland</publisher-loc>: <publisher-name>World Health Organization</publisher-name>.</citation>
</ref>
<ref id="B46">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yang</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Peng</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Srinivasakannan</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Xia</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Duan</surname>
<given-names>X.</given-names>
</name>
</person-group> (<year>2010</year>). <article-title>Preparation of high surface area activated carbon from coconut shells using microwave heating</article-title>. <source>Bioresour. Technol.</source> <volume>101</volume> (<issue>15</issue>), <fpage>6163</fpage>&#x2013;<lpage>6169</lpage>. <pub-id pub-id-type="doi">10.1016/j.biortech.2010.03.001</pub-id>
</citation>
</ref>
<ref id="B47">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Yang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Chen</surname>
<given-names>L.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Effects of high carbon dioxide concentration on emotional processing: based on multimodal evidence</article-title>. <source>Build. Environ.</source> <volume>256</volume>, <fpage>111434</fpage>. <pub-id pub-id-type="doi">10.1016/j.buildenv.2024.111434</pub-id>
</citation>
</ref>
<ref id="B48">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yang</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Lee</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Chung</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Characterization of indoor air quality using multiple measurements of nitrogen dioxide</article-title>. <source>Indoor Air</source> <volume>14</volume>, <fpage>105</fpage>&#x2013;<lpage>111</lpage>. <pub-id pub-id-type="doi">10.1046/j.1600-0668.2003.00216.x</pub-id>
</citation>
</ref>
<ref id="B49">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yue</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Ma</surname>
<given-names>N. L.</given-names>
</name>
<name>
<surname>Sonne</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Guan</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Lam</surname>
<given-names>S. S.</given-names>
</name>
<name>
<surname>Van Le</surname>
<given-names>Q.</given-names>
</name>
<etal/>
</person-group> (<year>2021</year>). <article-title>Mitigation of indoor air pollution: a review of recent advances in adsorption materials and catalytic oxidation</article-title>. <source>J. Hazard. Mater.</source> <volume>405</volume>, <fpage>124138</fpage>. <pub-id pub-id-type="doi">10.1016/j.jhazmat.2020.124138</pub-id>
</citation>
</ref>
<ref id="B50">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhao</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>Yang</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Ma</surname>
<given-names>L.</given-names>
</name>
</person-group> (<year>2013</year>). <article-title>Preparation and characterization of activated carbon from rice husks with KOH activation</article-title>. <source>Industrial Crops Prod.</source> <volume>42</volume>, <fpage>451</fpage>&#x2013;<lpage>456</lpage>. <pub-id pub-id-type="doi">10.1016/j.indcrop.2012.06.036</pub-id>
</citation>
</ref>
</ref-list>
</back>
</article>