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<journal-id journal-id-type="publisher-id">Front. Public Health</journal-id>
<journal-title>Frontiers in Public Health</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Public Health</abbrev-journal-title>
<issn pub-type="epub">2296-2565</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fpubh.2024.1356830</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Public Health</subject>
<subj-group>
<subject>Systematic Review</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Exposure to indoor air pollution and adverse pregnancy outcomes in low and middle-income countries: a systematic review and meta-analysis</article-title>
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<name><surname>Daba</surname> <given-names>Chala</given-names></name>
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<name><surname>Asmare</surname> <given-names>Lakew</given-names></name>
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<name><surname>Demeke Bayou</surname> <given-names>Fekade</given-names></name>
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<name><surname>Mohammed</surname> <given-names>Anissa</given-names></name>
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<name><surname>Tareke</surname> <given-names>Abiyu Abadi</given-names></name>
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<name><surname>Endawkie</surname> <given-names>Abel</given-names></name>
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<name><surname>Kebede</surname> <given-names>Shimels Derso</given-names></name>
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<name><surname>Abeje</surname> <given-names>Eyob Tilahun</given-names></name>
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<name><surname>Bekele Enyew</surname> <given-names>Ermias</given-names></name>
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<aff id="aff1"><sup>1</sup><institution>Department of Environmental Health, College of Medicine and Health Sciences, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff2"><sup>2</sup><institution>Department of Epidemiology and Biostatistics School of Public Health, College of Medicine and Health Science, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff3"><sup>3</sup><institution>Department of Reproductive and Family Health, School of Public Health, College of Medicine and Health Sciences, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff4"><sup>4</sup><institution>Amref Health in Africa, West Gondar Zonal Health Department</institution>, <addr-line>Gondar</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff5"><sup>5</sup><institution>Department of Health Promotion, School of Public Health, College of Medicine and Health Sciences, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff6"><sup>6</sup><institution>Department of Health System and Management, School of Public Health, College of Medicine and Health Sciences, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<aff id="aff7"><sup>7</sup><institution>Department of Health Informatics, School of Public Health, College of Medicine and Health Sciences, Wollo University</institution>, <addr-line>Dessie</addr-line>, <country>Ethiopia</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Mohammad Javad Mohammadi, Ahvaz Jundishapur University of Medical Sciences, Iran</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Arsham Alipour Birgani, Ahvaz Jundishapur University of Medical Sciences, Iran</p>
<p>&#x000D6;zlem &#x00130;pek, Tarsus University, T&#x000FC;rkiye</p>
<p>Gabriel O. Dida, Technical University of Kenya, Kenya</p></fn>
<corresp id="c001">&#x0002A;Correspondence: Chala Daba <email>chaladaba293&#x00040;gmail.com</email></corresp>
</author-notes>
<pub-date pub-type="epub">
<day>22</day>
<month>05</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>12</volume>
<elocation-id>1356830</elocation-id>
<history>
<date date-type="received">
<day>22</day>
<month>01</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>08</day>
<month>05</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2024 Daba, Asmare, Demeke Bayou, Arefaynie, Mohammed, Tareke, Keleb, Kebede, Tsega, Endawkie, Kebede, Mesfin, Abeje and Bekele Enyew.</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Daba, Asmare, Demeke Bayou, Arefaynie, Mohammed, Tareke, Keleb, Kebede, Tsega, Endawkie, Kebede, Mesfin, Abeje and Bekele Enyew</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>Exposure to indoor air pollution such as biomass fuel and particulate matter is a significant cause of adverse pregnancy outcomes. However, there is limited information about the association between indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries. Therefore, this meta-analysis aimed to determine the association between indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries.</p>
</sec>
<sec>
<title>Methods</title>
<p>International electronic databases such as PubMed, Science Direct, Global Health, African Journals Online, HINARI, Semantic Scholar, and Google and Google Scholar were used to search for relevant articles. The study was conducted according to the updated Preferred Reporting Items for Systematic Reviews and Meta-Analysis (PRISMA) guidelines. A random effect model at a 95% confidence interval was used to determine the association between indoor air pollution exposure and adverse pregnancy outcomes using STATA version 14. Funnel plot and Higgs I<sup>2</sup> statistics were used to determine the publication bias and heterogeneity of the included studies, respectively.</p>
</sec>
<sec>
<title>Results</title>
<p>A total of 30 articles with 2,120,228 study participants were included in this meta-analysis. The pooled association between indoor air pollution exposure and at least one adverse pregnancy outcome was 15.5% (95%CI: 12.6&#x02013;18.5), with significant heterogeneity (I<sup>2</sup> = 100%; <italic>p</italic> &#x0003C; 0.001). Exposure to indoor air pollution increased the risk of small for gestational age by 23.7% (95%CI: 8.2&#x02013;39.3) followed by low birth weight (17.7%; 95%CI: 12.9&#x02013;22.5). Exposure to biomass fuel (OR = 1.16; 95%CI: 1.12&#x02013;1.2), particulate matter (OR = 1.28; 95%CI: 1.25&#x02013;1.31), and kerosene (OR = 1.38; 95%CI: 1.09&#x02013;1.66) were factors associated with developing at least one adverse pregnancy outcomes.</p>
</sec>
<sec>
<title>Conclusions</title>
<p>We found that more than one in seven pregnant women exposed to indoor air pollution had at least one adverse pregnancy outcome. Specifically, exposure to particulate matter, biomass fuel, and kerosene were determinant factors for developing at least one adverse pregnancy outcome. Therefore, urgent comprehensive health intervention should be implemented in the area to reduce adverse pregnancy outcomes.</p>
</sec></abstract>
<kwd-group>
<kwd>adverse pregnancy outcomes</kwd>
<kwd>low birth weight</kwd>
<kwd>preterm birth</kwd>
<kwd>small for gestational age</kwd>
<kwd>stillbirth</kwd>
<kwd>biomass fuel</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="4"/>
<equation-count count="0"/>
<ref-count count="72"/>
<page-count count="13"/>
<word-count count="7971"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Environmental health and Exposome</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<title>Introduction</title>
<p>Exposure to indoor air pollution is a persistent public health problem in the 21st century globally. The World Health Organization (WHO) released a report in 2022 indicating that around 3.2 million people die each year as a result of exposure to indoor air pollution. Of this death, more than 237,000 of them were under five children age (<xref ref-type="bibr" rid="B1">1</xref>). Exposure to indoor air pollution continues to be the leading cause of adverse pregnancy outcomes such as low birth weight, preterm birth, stillbirth, and neonatal mortality, which could need urgent intervention (<xref ref-type="bibr" rid="B2">2</xref>). According to the WHO report of 2019, about 20 million infants were born with low birth weight (LBW) whereas 15 million infants were preterm birth (<xref ref-type="bibr" rid="B3">3</xref>).</p>
<p>The magnitudes of adverse pregnancy outcomes are more prevalent in low-income countries because the majority of communities rely on biomass fuel for cooking and heating (<xref ref-type="bibr" rid="B4">4</xref>). Evidence from the recent global burden disease released in 2017 indicates that 60.9 million disability-adjusted life years were reported in low and middle-income countries as a result of exposure to air pollution (<xref ref-type="bibr" rid="B5">5</xref>). For instance, the odds of stillbirth adverse pregnancy outcomes were 23 times higher among low-income countries than high-income countries (<xref ref-type="bibr" rid="B6">6</xref>), which highlights urgent interventions needed. Beyond adverse pregnancy outcomes, exposure to indoor air pollution has a significant effect on cognitive and economic status; which was lost 6.1% of Gross Domestic Product (GDP) in 2022 alone (<xref ref-type="bibr" rid="B7">7</xref>).</p>
<p>Various studies have investigated the association between exposure to indoor air pollution and adverse pregnancy outcomes in different parts of the country (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B8">8</xref>&#x02013;<xref ref-type="bibr" rid="B17">17</xref>). However, the findings from these studies have been inconclusive and varied, which could hinder the implementation of effective intervention strategies to reduce adverse pregnancy outcomes. For instance, studies conducted in Ethiopia (<xref ref-type="bibr" rid="B18">18</xref>), Peru (<xref ref-type="bibr" rid="B19">19</xref>), and Zambia (<xref ref-type="bibr" rid="B20">20</xref>) showed that exposure to indoor air pollution increased the risk of small for gestational age, stillbirth, and miscarriages whereas a non-significant association with neonatal death (<xref ref-type="bibr" rid="B18">18</xref>). However, studies conducted in India (<xref ref-type="bibr" rid="B13">13</xref>) Indonesia (<xref ref-type="bibr" rid="B21">21</xref>) and Bangladesh (<xref ref-type="bibr" rid="B22">22</xref>) also showed that there is a significant association between exposure to indoor air pollution and neonatal death and low birth weight.</p>
<p>Moreover, exposure to indoor air pollution and all types of adverse pregnancy outcomes were not pertinently investigated in low and middle-income countries. In addition to this, the previous systematic reviews and meta-analyses on exposure to indoor air pollution did not assess exposures to biomass fuel and particulate matter (PM<sub>10</sub> and PM<sub>2.5</sub>) together, which could underestimate the magnitude of adverse pregnancy outcomes (<xref ref-type="bibr" rid="B23">23</xref>&#x02013;<xref ref-type="bibr" rid="B25">25</xref>). Therefore, the objective of this systematic review and meta-analysis aimed to determine the pooled prevalence of adverse pregnancy outcomes among pregnancy women exposure to indoor air pollution in low and middle-income countries. The results from this meta-analysis will provide essential evidence that can inform adverse pregnancy outcomes control program planners, policymakers, and healthcare providers. This evidence will be valuable in designing and implementing evidence-based interventions aimed at reducing the burden of stillbirth, low birth weight, small gestational age, and preterm birth, neonatal and prenatal mortality.</p>
</sec>
<sec id="s2">
<title>Methods and materials</title>
<p><bold>Registration:</bold> This systematic review and meta-analysis is registered in PRESPERO under the registration number CRD42023432239.</p>
<sec>
<title>Study selection, search strategy, and study period</title>
<p>This meta-analysis followed the Preferred Reporting Items for Systematic Reviews and Meta-Analysis Protocols (PRISMA) guidelines (<xref ref-type="bibr" rid="B26">26</xref>). To retrieve relevant articles, international electronic databases such as PubMed, Science Direct, Global Health, African Journals Online, HINARI, Semantic Scholar, and Google and Google Scholar searches were used. Gray literature was also identified from different university&#x00027;s digital libraries. The following key terms were used to search the studies: Indoor air pollution&#x0201D;, &#x0201C;household air pollution&#x0201D;, biofuels OR &#x0201C;household fuel&#x0201D; &#x0201C;biomass&#x0201D;, &#x0201C;domestic fuel&#x0201D;, &#x0201C;coal&#x0201D;, &#x0201C;cooking fuel&#x0201D;, &#x0201C;wood&#x0201D;, &#x0201C;cooking smoke&#x0201D;, &#x0201C;charcoal&#x0201D;, &#x0201C;solid fuel&#x0201D;, &#x0201C;cooking firewood&#x0201D;, &#x0201C;biomass fuel&#x0201D;, &#x0201C;biomass smoke&#x0201D;, &#x0201C;wood fuel&#x0201D;, &#x0201C;wood smoke&#x0201D;, &#x0201C;charcoal smoke&#x0201D;, &#x0201C;Air pollution&#x0201D;, &#x0201C;Particulate matter&#x0201D;, &#x0201C;PM<sub>10</sub>&#x0201D;, &#x0201C;PM<sub>2.5</sub>&#x0201D;, &#x0201C;ozone&#x0201D;, &#x0201C;nitrogen dioxide&#x0201D;, &#x0201C;sulfur dioxide&#x0201D;, &#x0201C;carbon monoxide&#x0201D; &#x0201C;Polycyclic Hydrocarbons&#x0201D;, &#x0201C;Pregnancy outcome&#x0201D;, &#x0201C;birth weight&#x0201D;, &#x0201C;low birth weight&#x0201D;, &#x0201C;low birthweight&#x0201D;, &#x0201C;premature birth&#x0201D;, &#x0201C;premature infant&#x0201D;, &#x0201C;fetal growth retardation&#x0201D;, &#x0201C;fetal development&#x0201D;, &#x0201C;gestational age&#x0201D;, &#x0201C;small for gestational age&#x0201D;, &#x0201C;small gestational age&#x0201D;, &#x0201C;fetal mortality&#x0201D;, &#x0201C;fetal death&#x0201D;, &#x0201C;perinatal mortality&#x0201D;, &#x0201C;stillbirth&#x0201D;, &#x0201C;embryo loss&#x0201D;, &#x0201C;spontaneous abortion&#x0201D;, &#x0201C;congenital abnormalities&#x0201D;, &#x0201C;neural tube defects&#x0201D;, &#x0201C;low and middle income country&#x0201D;, &#x0201C;low income country&#x0201D;, &#x0201C;middle income country&#x0201D;, low and middle income countries&#x0201D;. All key terms were combined using the Boolean operators &#x0201C;AND&#x0201D; or &#x0201C;OR&#x0201D; as appropriate. The search was carried out up to December 1, 2023, by four authors independently (CD, YS, AE, and SDK).</p>
</sec>
<sec>
<title>Inclusion and exclusion criteria</title>
<p>In this meta-analysis, we included observational studies (cross-sectional, case-control, and cohort studies) on indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries. Studies published between 2000 and December 1, 2023, were included in the meta-analysis. However, qualitative studies, unretrievable studies, editorial letters, studies with poor methodological quality, and studies that did not report the outcome of interest were excluded from the meta-analysis.</p>
</sec>
<sec>
<title>Outcome assessment</title>
<p>The primary outcome of the study was to estimate the pooled association between indoor pollution exposure and adverse pregnancy outcomes in low and middle-income countries, calculated by dividing the number of adverse pregnancy outcomes by the total sample size and multiplying by 100.</p>
</sec>
<sec>
<title>Data extraction and quality assessment</title>
<p>After all searched articles were exported into the Endnote X20 version, and duplicate articles were removed, data was extracted by using a standard data extraction template by four authors (CD, KM, ET, and EB). The standard data extraction template consists of the author&#x00027;s name, country, publication year, exposure assessment, study design, prevalence, type of adverse pregnancy outcome, and sample size. Five reviewers (LA, CD, FD, MA, and AM) screened the relevant articles for eligibility, and the quality of each article was evaluated using the Joana Brigg Institute (JBI) critical appraisal checklist (<xref ref-type="bibr" rid="B27">27</xref>). The quality of each study was independently assessed by the four authors (CD, AAT, AK, and NK), with scores measured on a scale of 100%. A quality score of &#x0003C;50% was used to include articles for further analysis (<xref ref-type="bibr" rid="B28">28</xref>, <xref ref-type="bibr" rid="B29">29</xref>). In the case of any discrepancies encountered during the quality assessment, the mean score was computed from the evaluations of all reviewers to address and resolve any differences.</p>
</sec>
<sec>
<title>Statistical analysis and synthesis</title>
<p>DerSimonian and Liard&#x00027;s method of random effect model was used to determine the pooled association between indoor air pollution exposure and adverse pregnancy outcomes using STATA 14 (<xref ref-type="bibr" rid="B30">30</xref>). The Higgs I<sup>2</sup> statistic model was used to determine the heterogeneity of the included studies, with values of 25%, 50%, and 75% indicating low, moderate, and high heterogeneity, respectively (<xref ref-type="bibr" rid="B31">31</xref>). A <italic>p</italic>-value of less than 0.05 was considered indicative of the presence of heterogeneity. The publication bias was assessed using a funnel plot and Egger&#x00027;s test with a <italic>p</italic>-value less than 0.05 suggesting a publication bias (<xref ref-type="bibr" rid="B32">32</xref>).</p>
<p>Subgroup analysis was carried out based on various study characteristics such as sample size (large or small), year of publication (2020 and after or before 2020), quality of the study (high or low quality), and study setting (nationwide, healthcare facility or community level). Moreover, a sensitivity analysis was also performed to assess the influence of a single study on the pooled prevalence estimates.</p>
</sec>
<sec>
<title>Operational definition</title>
<p><bold>Low birth weight</bold>: a birth weight of &#x0003C;2,500 g (<xref ref-type="bibr" rid="B33">33</xref>).</p>
<p><bold>Stillbirth</bold>: &#x0201C;a baby who dies after 28 weeks of pregnancy but before or during birth&#x0201D;(<xref ref-type="bibr" rid="B34">34</xref>).</p>
<p><bold>Neonatal death</bold>: &#x0201C;deaths among live births during the first 28 completed days of life&#x0201D; (<xref ref-type="bibr" rid="B35">35</xref>).</p>
<p><bold>Preterm birth</bold>: &#x0201C;babies born alive before 37 weeks of pregnancy&#x0201D; (<xref ref-type="bibr" rid="B36">36</xref>).</p>
<p><bold>Small for gestational age</bold>: those smaller in size than normal for their gestational age, most commonly defined as a weight below the 10th percentile for the gestational age (<xref ref-type="bibr" rid="B37">37</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>Results</title>
<sec>
<title>Study selection</title>
<p>Using an international electronic database, a total of 2,002 articles was identified. Out of these, 296 duplicate articles were excluded using the Endnote reference manager and 817 articles were excluded based on their titles and abstracts. Besides, 10 articles were also excluded based on the quality assessment and outcomes of the interest. Finally, 30 full-text articles were eligible for this meta-analysis (<xref ref-type="fig" rid="F1">Figure 1</xref>).</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p>PRISMA flow diagram of the included studies for the systematic review and meta-analysis of exposure to indoor air pollution and adverse pregnancy outcomes in low and middle-income countries, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0001.tif"/>
</fig>
</sec>
<sec>
<title>Characteristics of the included studies</title>
<p>A total of 30 articles (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B15">15</xref>&#x02013;<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B20">20</xref>&#x02013;<xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B38">38</xref>&#x02013;<xref ref-type="bibr" rid="B57">57</xref>) were included to determine the association between exposure to indoor air pollution and adverse pregnancy outcomes in low and middle-income countries. In this meta-analysis, a total 2,120,228 of study participants were included. From the included studies, Pakistan had the highest at least one adverse pregnancy outcome (35.4%) (<xref ref-type="bibr" rid="B38">38</xref>), and the lowest adverse pregnancy outcome was reported in India (1.7%) (<xref ref-type="bibr" rid="B44">44</xref>). Regarding the study setting, 12 studies were conducted in healthcare facilities (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B16">16</xref>, <xref ref-type="bibr" rid="B21">21</xref>, <xref ref-type="bibr" rid="B38">38</xref>&#x02013;<xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B43">43</xref>, <xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B46">46</xref>, <xref ref-type="bibr" rid="B50">50</xref>), 14 in nationwide (country level) (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B16">16</xref>, <xref ref-type="bibr" rid="B21">21</xref>, <xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B38">38</xref>&#x02013;<xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B43">43</xref>, <xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B46">46</xref>, <xref ref-type="bibr" rid="B50">50</xref>, <xref ref-type="bibr" rid="B52">52</xref>), and four in community level (<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B47">47</xref>, <xref ref-type="bibr" rid="B51">51</xref>, <xref ref-type="bibr" rid="B54">54</xref>). Likewise, 28 studies had scored 75% and more of JBI the quality assessment (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B15">15</xref>&#x02013;<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B20">20</xref>, <xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B38">38</xref>&#x02013;<xref ref-type="bibr" rid="B57">57</xref>), while two studies scored 62.5% (<xref ref-type="bibr" rid="B21">21</xref>, <xref ref-type="bibr" rid="B51">51</xref>). Nine studies were carried out in India (<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B16">16</xref>, <xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B47">47</xref>, <xref ref-type="bibr" rid="B52">52</xref>&#x02013;<xref ref-type="bibr" rid="B54">54</xref>, <xref ref-type="bibr" rid="B57">57</xref>), three in China (<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B45">45</xref>, <xref ref-type="bibr" rid="B48">48</xref>), three in Bangladesh (<xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B43">43</xref>), three in Ghana (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B15">15</xref>, <xref ref-type="bibr" rid="B56">56</xref>), two in Pakistan (<xref ref-type="bibr" rid="B38">38</xref>, <xref ref-type="bibr" rid="B51">51</xref>), one each in Ethiopia (<xref ref-type="bibr" rid="B4">4</xref>), Zimbabwe (<xref ref-type="bibr" rid="B46">46</xref>), Nepal (<xref ref-type="bibr" rid="B42">42</xref>), Zambia (<xref ref-type="bibr" rid="B20">20</xref>), five African countries (India, Pakistan, Guatemala, Kenya, and Zambia) (<xref ref-type="bibr" rid="B49">49</xref>), fifteen African countries (<xref ref-type="bibr" rid="B39">39</xref>), Nigeria (<xref ref-type="bibr" rid="B50">50</xref>), Uganda (<xref ref-type="bibr" rid="B40">40</xref>), Indonesia (<xref ref-type="bibr" rid="B21">21</xref>), and Sri Lanka (<xref ref-type="bibr" rid="B55">55</xref>) (<xref ref-type="table" rid="T1">Table 1</xref>).</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>Descriptive summary of 30 studies included in meta-analysis to estimate the association between exposure to indoor air pollution and adverse pregnancy outcomes in low and middle-income countries, 2023.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left"><bold>References</bold></th>
<th valign="top" align="left"><bold>Country</bold></th>
<th valign="top" align="left"><bold>Study setting</bold></th>
<th valign="top" align="left"><bold>Exposure assessment</bold></th>
<th valign="top" align="left"><bold>Outcome</bold></th>
<th valign="top" align="center"><bold>Sample size</bold></th>
<th valign="top" align="center"><bold>Prevalence (%)</bold></th>
<th valign="top" align="center"><bold>Quality score (%)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Epuitai et al. (<xref ref-type="bibr" rid="B40">40</xref>)</td>
<td valign="top" align="left">Uganda</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass and Kerosene</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">15,270</td>
<td valign="top" align="center">9.6</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Epstein et al. (<xref ref-type="bibr" rid="B13">13</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass, coal, kerosene</td>
<td valign="top" align="left">LBW, neonatal death</td>
<td valign="top" align="center">36,529</td>
<td valign="top" align="center">16.5</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Bachwenkizi et al. (<xref ref-type="bibr" rid="B39">39</xref>)</td>
<td valign="top" align="left">15 Africa country</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">particulate matter</td>
<td valign="top" align="left">LBW, PTB</td>
<td valign="top" align="center">31,594</td>
<td valign="top" align="center">10</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Ahmed et al. (<xref ref-type="bibr" rid="B38">38</xref>)</td>
<td valign="top" align="left">Pakistan</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">102,060</td>
<td valign="top" align="center">35.4</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Amegah et al. (<xref ref-type="bibr" rid="B9">9</xref>)</td>
<td valign="top" align="left">Ghana</td>
<td valign="top" align="left">Hospital</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">647</td>
<td valign="top" align="center">18.1</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Siddiqui et al. (<xref ref-type="bibr" rid="B51">51</xref>)</td>
<td valign="top" align="left">Pakistan</td>
<td valign="top" align="left">Community</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">366</td>
<td valign="top" align="center">22.7</td>
<td valign="top" align="center">62.5</td>
</tr> <tr>
<td valign="top" align="left">Anil K. C. et al. (<xref ref-type="bibr" rid="B42">42</xref>)</td>
<td valign="top" align="left">Nepal</td>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="left">Firewood and Kerosene, LPG, and Bio Gas</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">369</td>
<td valign="top" align="center">NR</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Balakrishnan et al. (<xref ref-type="bibr" rid="B10">10</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="left">particulate matter (PM<sub>2.5</sub>)</td>
<td valign="top" align="left">Birth weight</td>
<td valign="top" align="center">1,285</td>
<td valign="top" align="center">16.06</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Li et al. (<xref ref-type="bibr" rid="B45">45</xref>)</td>
<td valign="top" align="left">China</td>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="left">Particulate matter</td>
<td valign="top" align="left">PTB</td>
<td valign="top" align="center">1,280,524</td>
<td valign="top" align="center">8.1</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Sreeramareddy et al. (<xref ref-type="bibr" rid="B52">52</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">109,041</td>
<td valign="top" align="center">41</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Haider et al. (<xref ref-type="bibr" rid="B41">41</xref>)</td>
<td valign="top" align="left">Bangladesh</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">8,753</td>
<td valign="top" align="center">17.6</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Hussein et al. (<xref ref-type="bibr" rid="B15">15</xref>)</td>
<td valign="top" align="left">Ghana</td>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, PTB, Neonatal death</td>
<td valign="top" align="center">1,626</td>
<td valign="top" align="center">5.5</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Tielsch et al. (<xref ref-type="bibr" rid="B54">54</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Community</td>
<td valign="top" align="left">Biomass fuel and tobacco smoke</td>
<td valign="top" align="left">LBW, PTB, SGA</td>
<td valign="top" align="center">11,728</td>
<td valign="top" align="center">34.07</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Jiang et al. (<xref ref-type="bibr" rid="B17">17</xref>)</td>
<td valign="top" align="left">China</td>
<td valign="top" align="left">Community</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, PTB, SGA</td>
<td valign="top" align="center">9,895</td>
<td valign="top" align="center">6.5</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Kanno et al. (<xref ref-type="bibr" rid="B4">4</xref>)</td>
<td valign="top" align="left">Ethiopia</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">10,014</td>
<td valign="top" align="center">26.2</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Khan et al. (<xref ref-type="bibr" rid="B43">43</xref>)</td>
<td valign="top" align="left">Bangladesh</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, Stillbirth, neonatal and infant mortality</td>
<td valign="top" align="center">22,789</td>
<td valign="top" align="center">17.7</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Islam et al. (<xref ref-type="bibr" rid="B16">16</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW &#x00026; birth size</td>
<td valign="top" align="center">119,537</td>
<td valign="top" align="center">16.5</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Lakshmi et al. (<xref ref-type="bibr" rid="B44">44</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">Stillbirth</td>
<td valign="top" align="center">188,917</td>
<td valign="top" align="center">1.7</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Sunnay et al. (<xref ref-type="bibr" rid="B53">53</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="left">NR</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">90</td>
<td valign="top" align="center">NR</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Mishra et al. (<xref ref-type="bibr" rid="B46">46</xref>)</td>
<td valign="top" align="left">Zimbabwe</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass smoke</td>
<td valign="top" align="left">LBW</td>
<td valign="top" align="center">6,369</td>
<td valign="top" align="center">8.46</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Mukherjee et al. (<xref ref-type="bibr" rid="B47">47</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Community</td>
<td valign="top" align="left">Biomass, Particulate matter</td>
<td valign="top" align="left">LBW, spontaneous abortion, stillbirth</td>
<td valign="top" align="center">404</td>
<td valign="top" align="center">19.6</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Mulenga et al. (<xref ref-type="bibr" rid="B20">20</xref>)</td>
<td valign="top" align="left">Zambia</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Particulate and VOC</td>
<td valign="top" align="left">LBW, PTB, SGA</td>
<td valign="top" align="center">1,170</td>
<td valign="top" align="center">24.8</td>
<td valign="top" align="center">75</td>
</tr> <tr>
<td valign="top" align="left">Nisha et al. (<xref ref-type="bibr" rid="B22">22</xref>)</td>
<td valign="top" align="left">Bangladesh</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass fuel, agricultural products</td>
<td valign="top" align="left">Stillbirth and neonatal mortality</td>
<td valign="top" align="center">27,237</td>
<td valign="top" align="center">2.8</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Pan et al. (<xref ref-type="bibr" rid="B48">48</xref>)</td>
<td valign="top" align="left">China</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, PTB, Stillbirth</td>
<td valign="top" align="center">9,505</td>
<td valign="top" align="center">5.5</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Patel et al. (<xref ref-type="bibr" rid="B49">49</xref>)</td>
<td valign="top" align="left">India, Pakistan, Guatemala, Kenya, Zambia</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Cooking fuel</td>
<td valign="top" align="left">Stillbirth, prenatal and neonatal mortality</td>
<td valign="top" align="center">65,912</td>
<td valign="top" align="center">2.6</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Roberman et al. (<xref ref-type="bibr" rid="B50">50</xref>)</td>
<td valign="top" align="left">Nigeria</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass/unclean cooking fuel</td>
<td valign="top" align="left">LBW, stillbirth and PTB</td>
<td valign="top" align="center">41,821</td>
<td valign="top" align="center">14.9</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Suryadhi et al. (<xref ref-type="bibr" rid="B21">21</xref>)</td>
<td valign="top" align="left">Indonesia</td>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="left">Biomass, kerosene, biogas, electricity</td>
<td valign="top" align="left">LBW, neonatal, and infant death</td>
<td valign="top" align="center">14,475</td>
<td valign="top" align="center">6.6</td>
<td valign="top" align="center">62.5</td>
</tr> <tr>
<td valign="top" align="left">Vakalopoulos et al. (<xref ref-type="bibr" rid="B55">55</xref>)</td>
<td valign="top" align="left">Sri Lanka</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, SGA</td>
<td valign="top" align="center">385</td>
<td valign="top" align="center">13</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Weber et al. (<xref ref-type="bibr" rid="B56">56</xref>)</td>
<td valign="top" align="left">Ghana</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Biomass fuel, Liquid Petroleum Gas, Kerosene</td>
<td valign="top" align="left">LBW, SGA, PTB, perinatal mortality</td>
<td valign="top" align="center">772</td>
<td valign="top" align="center">11.1</td>
<td valign="top" align="center">87.5</td>
</tr> <tr>
<td valign="top" align="left">Wylie et al. (<xref ref-type="bibr" rid="B57">57</xref>)</td>
<td valign="top" align="left">India</td>
<td valign="top" align="left">Healthcare</td>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="left">LBW, stillbirth, SGA and PTB</td>
<td valign="top" align="center">1,199</td>
<td valign="top" align="center">23.9</td>
<td valign="top" align="center">75</td>
</tr></tbody>
</table>
<table-wrap-foot>
<p>NR, not reported; PTB, preterm birth; LBW, low birth weight; SGA, small for gestational age.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec>
<title>Association between indoor air pollution exposure and adverse pregnancy outcomes</title>
<p>Our analysis of the 30 included studies revealed significant heterogeneity among them (I<sup>2</sup> = 100%; <italic>p</italic> &#x0003C; 0.001). Hence, DerSimonian and Liard&#x00027;s method of random effect model was carried out to estimate the pooled association between exposure to indoor air pollution and adverse pregnancy outcomes. The results of the random effect model indicated the pooled prevalence of at least one adverse pregnancy outcome was 15.55% (95% CI: 12.61&#x02013;18.49) (<xref ref-type="fig" rid="F2">Figure 2</xref>).</p>
<fig id="F2" position="float">
<label>Figure 2</label>
<caption><p>Forest plot of the pooled association between indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0002.tif"/>
</fig>
<p>Meta-analysis showed that there is a significant association between indoor air pollution exposure and adverse pregnancy outcomes. The high pooled prevalence of adverse pregnancy outcomes was small for gestational age (23.77%) followed by low birth weight (17.74%). The pooled prevalence of preterm birth among pregnant women exposed to indoor air pollution was 16.56%. Likewise, there is a significant association between indoor air pollution exposure and stillbirth (6.11%) (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
<table-wrap position="float" id="T2">
<label>Table 2</label>
<caption><p>Pooled adverse pregnancy outcomes among pregnancy women exposed to indoor air pollution in low and middle-income countries, 2023.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left"><bold>Type of adverse effect</bold></th>
<th valign="top" align="center"><bold>Number of studies</bold></th>
<th valign="top" align="center"><bold>Pooled adverse pregnancy outcome (95% CI)</bold></th>
<th valign="top" align="center" colspan="2"><bold>Heterogeneity</bold></th>
</tr>
</thead>
<tbody>
<tr style="background-color:#919498;color:#ffffff">
<td/>
<td/>
<td/>
<td valign="top" align="center"><bold>I</bold><sup>2</sup></td>
<td valign="top" align="center"><italic><bold>p</bold></italic><bold>-value</bold></td>
</tr>
<tr>
<td valign="top" align="left">Low birth weight</td>
<td valign="top" align="center">25</td>
<td valign="top" align="center">17.74 (12.97&#x02013;22.52)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Small for gestational age</td>
<td valign="top" align="center">7</td>
<td valign="top" align="center">23.77 (8.25&#x02013;39.30)</td>
<td valign="top" align="center">99.9%</td>
<td valign="top" align="center">&#x0003C; 0.000</td>
</tr>
<tr>
<td valign="top" align="left">Preterm birth</td>
<td valign="top" align="center">9</td>
<td valign="top" align="center">16.56 (11.51&#x02013;21.60)</td>
<td valign="top" align="center">99.9%</td>
<td valign="top" align="center">&#x0003C; 0.000</td>
</tr>
<tr>
<td valign="top" align="left">Neonatal death</td>
<td valign="top" align="center">6</td>
<td valign="top" align="center">2.48 (1.37&#x02013;3.60)</td>
<td valign="top" align="center">99.6%</td>
<td valign="top" align="center">&#x0003C; 0.000</td>
</tr>
<tr>
<td valign="top" align="left">Stillbirth</td>
<td valign="top" align="center">7</td>
<td valign="top" align="center">6.11 (3.58&#x02013;8.65)</td>
<td valign="top" align="center">99.9%</td>
<td valign="top" align="center">&#x0003C; 0.000</td>
</tr></tbody>
</table>
</table-wrap>
</sec>
<sec>
<title>Publication bias assessment</title>
<p>A funnel plot was used to determine the publication bias, revealing an asymmetric distribution that strongly indicated the presence of publication bias (<xref ref-type="fig" rid="F3">Figure 3</xref>). Further, statistical analysis employing the Egger regression test verified the absence of publication bias (<italic>p</italic> = 0.159). Similarly, the publication bias was also carried out using a funnel plot and statistical Egger test for low birth weight. The finding showed there was an asymmetric distribution that strongly indicated the presence of publication bias (<xref ref-type="fig" rid="F4">Figure 4</xref>). However, the Egger regression test confirmed the absence of publication bias (<italic>p</italic> = 0.191).</p>
<fig id="F3" position="float">
<label>Figure 3</label>
<caption><p>Funnel plot of the pooled prevalence of at least one adverse pregnancy outcomes in low and middle-income countries, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0003.tif"/>
</fig>
<fig id="F4" position="float">
<label>Figure 4</label>
<caption><p>Funnel plot of the pooled association between indoor air pollution exposure and low birth weight in low and middle-income countries, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0004.tif"/>
</fig>
<p>Besides, the publication bias was also determined for small gestational age, preterm birth, and neonatal death using a funnel plot (<xref ref-type="supplementary-material" rid="SM1">Supplementary material 1</xref>). The Egger regression test confirmed the absence of publication bias among included studies for small gestational age (<italic>p</italic> = 0929) and preterm birth (<italic>p</italic> = 0.891), neonatal death (<italic>p</italic> = 0.322).</p>
</sec>
<sec>
<title>Subgroup analysis</title>
<p>To pinpoint the source of heterogeneity among included studies (I<sup>2</sup> = 100%, <italic>p</italic> &#x0003C; 0.001), subgroup analysis was conducted based on study setting (nationwide, healthcare facility or community), sample size (small or large), quality of the study (high or low) and year of publication (2020 and after or before 2020). The study conducted at the community level had higher pooled adverse pregnancy outcomes (20.71%), with extreme heterogeneity among included studies (I<sup>2</sup> = 99.9%, <italic>p</italic> &#x0003C; 001) followed nationwide (16.06%) (<xref ref-type="table" rid="T3">Table 3</xref>). Regarding the year of publication, the highest pooled prevalence of adverse pregnancy outcomes was observed among studies conducted before 2020 (17.01%; 95%CI: 13.39&#x02013;29.63) than studies conducted after 2020 (12.48%; 95% CI: 9.15&#x02013;15.80). In addition, the high pooled prevalence of adverse pregnancy outcomes was observed among small sample size studies (16.71%; 95%CI: 12.46&#x02013;20.96) as compared to studies conducted with large sample size (15.28%; 95%CI: 12.04&#x02013;18.52) (<xref ref-type="table" rid="T3">Table 3</xref>).</p>
<table-wrap position="float" id="T3">
<label>Table 3</label>
<caption><p>Subgroup analysis of the pooled prevalence of adverse pregnancy outcomes among pregnant women exposed to indoor air pollution in low and middle-income countries, 2023.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left"><bold>Variables</bold></th>
<th valign="top" align="center"><bold>Number of studies</bold></th>
<th valign="top" align="center"><bold>OR (95% CI)</bold></th>
<th valign="top" align="center" colspan="2"><bold>Heterogeneity</bold></th>
</tr>
<tr style="background-color:#919498;color:#ffffff">
<th/>
<th/>
<th/>
<th valign="top" align="center"><bold>I<sup>2</sup></bold></th>
<th valign="top" align="center"><bold><italic>p</italic>-value</bold></th>
</tr>
</thead>
<tbody>
<tr style="background-color:#dee1e1">
<td valign="top" align="left" colspan="5"><bold>Study setting</bold></td>
</tr>
<tr>
<td valign="top" align="left">Nationwide</td>
<td valign="top" align="center">14</td>
<td valign="top" align="center">16.06 (9.0&#x02013;23.13)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Healthcare facilities</td>
<td valign="top" align="center">10</td>
<td valign="top" align="center">12.51 (10.09&#x02013;15.04)</td>
<td valign="top" align="center">99.9%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Communities</td>
<td valign="top" align="center">4</td>
<td valign="top" align="center">20.71 (2.32&#x02013;39.11)</td>
<td valign="top" align="center">99.9%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr style="background-color:#dee1e1">
<td valign="top" align="left" colspan="5"><bold>Sample size</bold></td>
</tr>
<tr>
<td valign="top" align="left">Small</td>
<td valign="top" align="center">5</td>
<td valign="top" align="center">16.71 (12.46&#x02013;20.96)</td>
<td valign="top" align="center">88.5%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Large</td>
<td valign="top" align="center">23</td>
<td valign="top" align="center">15.28 (12.04&#x02013;18.52)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr style="background-color:#dee1e1">
<td valign="top" align="left" colspan="5"><bold>Quality of the study</bold></td>
</tr>
<tr>
<td valign="top" align="left">High</td>
<td valign="top" align="center">17</td>
<td valign="top" align="center">10.86 (8.57&#x02013;13.51)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Low</td>
<td valign="top" align="center">11</td>
<td valign="top" align="center">22.79 (13.96&#x02013;31.62)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr style="background-color:#dee1e1">
<td valign="top" align="left" colspan="5"><bold>Year of publication</bold></td>
</tr>
<tr>
<td valign="top" align="left">2020 and after</td>
<td valign="top" align="center">9</td>
<td valign="top" align="center">12.48 (9.15&#x02013;15.80)</td>
<td valign="top" align="center">99.8%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Before 2020</td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">17.01 (13.39&#x02013;29.63)</td>
<td valign="top" align="center">100%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr></tbody>
</table>
</table-wrap>
</sec>
<sec>
<title>Sensitivity analysis</title>
<p>A sensitivity analysis was performed to evaluate the impact of individual studies on the overall pooled estimate of adverse pregnancy outcomes, and the results indicated that no single study exerted a significant effect (<xref ref-type="fig" rid="F5">Figure 5</xref>). Similarly, we also evaluate the impact of individual studies on the overall pooled estimate of low birth weight, small for gestational age, preterm birth, neonatal death, and stillbirth, and the findings suggest that there is no evidence of a single study&#x00027;s effect on the overall pooled prevalence (<xref ref-type="supplementary-material" rid="SM1">Supplementary material 2</xref>).</p>
<fig id="F5" position="float">
<label>Figure 5</label>
<caption><p>Sensitivity analysis of the pooled association between indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0005.tif"/>
</fig>
</sec>
<sec>
<title>Factors associated with adverse pregnancy outcomes</title>
<p>Exposure to indoor air pollution, such as biomass fuel, particulate matter, and kerosene was statistically significantly associated with adverse pregnancy outcomes. Twenty-three studies were included to determine the association between biomass fuel exposure and adverse pregnancy outcomes (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B15">15</xref>&#x02013;<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B21">21</xref>, <xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B40">40</xref>&#x02013;<xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B48">48</xref>&#x02013;<xref ref-type="bibr" rid="B52">52</xref>, <xref ref-type="bibr" rid="B54">54</xref>&#x02013;<xref ref-type="bibr" rid="B57">57</xref>). Thirteen of the included studies had a positive association (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B21">21</xref>, <xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B43">43</xref>, <xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B48">48</xref>&#x02013;<xref ref-type="bibr" rid="B51">51</xref>, <xref ref-type="bibr" rid="B54">54</xref>, <xref ref-type="bibr" rid="B55">55</xref>), while negative association in 10 studies. The pooled results from random effect analysis showed that exposure to biomass fuel would increase the risk of adverse pregnancy outcomes by 1.16 (OR = 1.16; 95% CI: 1.12&#x02013;1.20), with significant heterogeneity (I<sup>2</sup> = 88.8%; <italic>p</italic> &#x0003C; 0.001) (<xref ref-type="fig" rid="F6">Figure 6</xref>).</p>
<fig id="F6" position="float">
<label>Figure 6</label>
<caption><p>Forest plot of odds ratio for the association between biomass fuel exposure and adverse pregnancy outcome, 2023.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1356830-g0006.tif"/>
</fig>
<p>The association between particulate matter exposure and adverse pregnancy outcomes was determined based on four studies (<xref ref-type="bibr" rid="B20">20</xref>, <xref ref-type="bibr" rid="B39">39</xref>, <xref ref-type="bibr" rid="B47">47</xref>, <xref ref-type="bibr" rid="B56">56</xref>). Two of the included studies had a positive association (<xref ref-type="bibr" rid="B39">39</xref>, <xref ref-type="bibr" rid="B47">47</xref>), while negative association in the remaining two studies (<xref ref-type="bibr" rid="B20">20</xref>, <xref ref-type="bibr" rid="B56">56</xref>). The odds of adverse pregnancy outcomes were 1.28 times higher among pregnant women who had particulate matter exposure than those who had no exposure (OR = 1.28; 95% CI: 1.25&#x02013;1.31), with significant heterogeneity (I<sup>2</sup>= 70.1%; <italic>p</italic> = 0.018) (<xref ref-type="table" rid="T4">Table 4</xref>).</p>
<table-wrap position="float" id="T4">
<label>Table 4</label>
<caption><p>The pooled factors associated with at least one adverse pregnancy outcome in low and middle-income countries, 2023.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left"><bold>Variables</bold></th>
<th valign="top" align="center"><bold>Number of studies</bold></th>
<th valign="top" align="center"><bold>OR (95% CI)</bold></th>
<th valign="top" align="center" colspan="2"><bold>Heterogeneity</bold></th>
</tr>
</thead>
<tbody>
<tr style="background-color:#919498;color:#ffffff">
<td/>
<td/>
<td/>
<td valign="top" align="center"><bold>I</bold><sup>2</sup></td>
<td valign="top" align="center"><italic><bold>P</bold></italic><bold>-value</bold></td>
</tr>
<tr>
<td valign="top" align="left">Biomass fuel</td>
<td valign="top" align="center">23</td>
<td valign="top" align="center">1.16 (1.12&#x02013;1.20)</td>
<td valign="top" align="center">88.8%</td>
<td valign="top" align="center">&#x0003C; 0.001</td>
</tr>
<tr>
<td valign="top" align="left">Particulate matter</td>
<td valign="top" align="center">4</td>
<td valign="top" align="center">1.28 (1.25&#x02013;1.31)</td>
<td valign="top" align="center">70.1%</td>
<td valign="top" align="center">0.018</td>
</tr>
<tr>
<td valign="top" align="left">Kerosene</td>
<td valign="top" align="center">2</td>
<td valign="top" align="center">1.38 (1.09&#x02013;1.66)</td>
<td valign="top" align="center">0.0%</td>
<td valign="top" align="center">&#x0003C; 0.000</td>
</tr></tbody>
</table>
</table-wrap>
<p>Similarly, the association between kerosene exposure and adverse pregnancy outcomes was determined based on the finding of two studies (<xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B44">44</xref>). There is a significant association in one study (<xref ref-type="bibr" rid="B44">44</xref>) and a non-significant in another study (<xref ref-type="bibr" rid="B13">13</xref>). Meta-analysis showed that the pregnant women who had kerosene exposure were 37% times more likely to have adverse pregnancy outcomes than counterparts (OR = 1.37; 95%CI: 1.09&#x02013;1.66) (<xref ref-type="table" rid="T4">Table 4</xref>).</p>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>Discussion</title>
<p>This systematic review and meta-analysis aimed to determine the association between indoor air pollution exposure and adverse pregnancy outcomes in low and middle-income countries. The overall pooled prevalence of at least one adverse pregnancy outcome was found to be 15.5% (95% CI: 12.61&#x02013;18.49); with extreme heterogeneity among included studies (I<sup>2</sup> = 100; <italic>p</italic> &#x0003C; 0.001). Specifically, exposure to indoor air pollution increased the risk of small gestational age by 23.7% (95%CI: 8.25&#x02013;39.3), stillbirth (6.11%; 95%CI: 3.58&#x02013;8.65), and neonatal mortality (2.48%; 95%CI: 1.37&#x02013;3.60). This finding is corroborated by recent systematic reviews and meta-analyses (<xref ref-type="bibr" rid="B5">5</xref>, <xref ref-type="bibr" rid="B58">58</xref>, <xref ref-type="bibr" rid="B59">59</xref>). This is mainly due to exposure to carbon monoxide, particulate matter, and highly polluting biomass fuel could enhance the burden of adverse pregnancy outcomes (<xref ref-type="bibr" rid="B55">55</xref>).</p>
<p>There seems to be evidence that exposure to indoor air pollution has a significant contribution to stillbirth outcomes (<xref ref-type="bibr" rid="B2">2</xref>), which is consistent with the current meta-analysis. Similarly, our finding was supported by a recent study conducted in Ethiopia (<xref ref-type="bibr" rid="B18">18</xref>), which indicates that there is an association between exposure to indoor pollution and stillbirth. This might be due to the pregnant women being exposed to high-polluting indoor air pollution, which could contribute to a significant association with adverse pregnancy outcomes (stillbirth) (<xref ref-type="bibr" rid="B18">18</xref>).</p>
<p>The current meta-analysis showed that one in six neonates could experience low birth weight (17.7%; 95%CI: 12.97&#x02013;22.52), which is consistent with previous study conducted in Sub-Saharan Africa (14%) (<xref ref-type="bibr" rid="B60">60</xref>). The current finding was also supported by the previous meta-regression analysis of 204 countries (<xref ref-type="bibr" rid="B25">25</xref>), which indicates that exposure to ambient and household indoor air pollution PM<sub>2.5</sub> increased the risk of all low birth weight by 15.6%. This is mainly due to exposure to high polluting air pollution especially, anthropogenic particulates (PM<sub>2.5</sub>) harmful to child health and growth, leading to low birth weight.</p>
<p>The odds of at least one adverse pregnancy outcome were 1.16 times higher among women who used high-polluting biomass fuel than those who used non-polluting biomass. Pregnant women exposed to highly polluting biomass fuels (namely, firewood and kerosene) have statistically significant factors for infants with low birth weight showing that low birth weight infants were sixteen percent times as likely to be born mothers exposed to high polluting biomass fuel than counterparts; which is consistent with the recent studies conducted by Kadam et al. (<xref ref-type="bibr" rid="B61">61</xref>). Increased exposure time to indoor air pollutants such as particulate matter, carbon monoxide, and sulfur dioxide has a significant impact on the growth and development of the fetus and subsequently low birth weight (<xref ref-type="bibr" rid="B62">62</xref>). The association between exposure to indoor air pollution and low birth weight is also established study done in developing countries (<xref ref-type="bibr" rid="B62">62</xref>). Therefore, mitigation measures such as cooking outdoors, decreasing exposure time, and improving the ventilation system with chimneys might play a significant role in decreasing adverse pregnancy outcomes (<xref ref-type="bibr" rid="B63">63</xref>).</p>
<p>The pooled prevalence of preterm birth was found to be 16.56%; these high pregnancy outcomes might be due to the exposure to highly polluting biomass fuel than non-polluting fuel; which is supported by a study conducted in East India (<xref ref-type="bibr" rid="B57">57</xref>). The odds of at least adverse pregnancy outcomes were 1.28 times higher among pregnant women exposed to particulate matter than those not exposed to particulate matter. The current finding was also consistent with a study conducted in Ohio, which indicates that pregnancy women exposure to high particulate matter (PM<sub>2.5</sub>) could increase the risk of preterm by 1.19 (<xref ref-type="bibr" rid="B64">64</xref>). A recent meta-analysis also confirmed that exposure to particulate matter (PM<sub>2.5</sub>) could increase the risk of preterm birth by 1.10 (<xref ref-type="bibr" rid="B65">65</xref>). This is mainly because cooking with highly polluting biomass fuel in poorly ventilated homes generates high concentrations of particulate matter (<xref ref-type="bibr" rid="B10">10</xref>). Hence, it is important to reduce exposure time to household air pollution may be crucial for the reduction of adverse pregnancy outcomes.</p>
<p>In this meta-analysis, we found that there is a significant association between exposure to indoor air pollution and neonatal mortality. The pooled prevalence of neonatal mortality was found to be 2.48%, with extreme heterogeneity (I<sup>2</sup> = 99.9%; <italic>p</italic> &#x0003C; 0.001). This finding was in line with studies conducted in Bangladesh (<xref ref-type="bibr" rid="B43">43</xref>) and Pakistan (<xref ref-type="bibr" rid="B66">66</xref>). This finding was also supported by a study conducted in five world regions (<xref ref-type="bibr" rid="B67">67</xref>), which indicates that exposure to indoor air pollution increased the risk of neonatal mortality by 1.24 (95% CI: 1.14&#x02013;1.34). This is mainly due to exposure to air pollution, which entails potential hazards for their neonates like lower birth weight, preterm birth, and lung developmental defects causing onset of respiratory diseases and reduced lung function in children (<xref ref-type="bibr" rid="B68">68</xref>&#x02013;<xref ref-type="bibr" rid="B70">70</xref>). Because neonates need more air intake for survival and therefore inhale excessive oxygen as compared to children; air polluted with unwanted contaminants enters their lungs and provokes consequent deaths (<xref ref-type="bibr" rid="B70">70</xref>). It is also well documented that exposure to air pollution has a significant and positive association with neonatal mortality, particularly in low and middle-income countries (<xref ref-type="bibr" rid="B71">71</xref>).</p>
<sec>
<title>Limitations and strengths of the study</title>
<p>The study followed the updated preferred reporting items for systematic review and meta-analysis. In this meta-analysis, all types of adverse pregnancy outcomes as a result of exposure to indoor air pollution were pertinently assessed. One of the limitations of this meta-analysis was that it did not establish causality between independent and dependent variables since the majority of the included studies were cross-sectional and case-control study designs.</p>
</sec>
</sec>
<sec sec-type="conclusions" id="s5">
<title>Conclusions</title>
<p>We found that there was a significant association between indoor air pollution exposure and adverse pregnancy outcomes. The pooled adverse pregnancy outcomes among women exposed to indoor air pollution were found to be high; which calls for urgent interventions, particularly in low and middle-income countries, where cooking with biomass fuels is common. Therefore, the Ministry of Health, healthcare workers, and other concerned bodies should provide comprehensive public health intervention to reduce adverse pregnancy outcomes. Besides, mechanistic studies are needed to understand the underlying mechanisms of association between exposure to indoor air pollution and adverse pregnancy outcomes. Further studies on the toxicological effect on indoor air pollution (particulate matter, biomass fuel, kerosene) are needed to verify these findings.</p>
</sec>
<sec sec-type="data-availability" id="s6">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="SM1">Supplementary material</xref>, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>CD: Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Visualization, Writing&#x02014;original draft, Writing&#x02014;review &#x00026; editing. LA: Conceptualization, Investigation, Methodology, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. FD: Conceptualization, Investigation, Resources, Software, Supervision, Validation, Writing&#x02014;review &#x00026; editing. MA: Conceptualization, Data curation, Formal analysis, Investigation, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. AM: Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. AT: Investigation, Methodology, Project administration, Resources, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. AK: Data curation, Formal analysis, Investigation, Resources, Software, Supervision, Validation, Writing&#x02014;review &#x00026; editing. NK: Conceptualization, Data curation, Methodology, Resources, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. YT: Data curation, Funding acquisition, Investigation, Methodology, Resources, Software, Visualization, Writing&#x02014;review &#x00026; editing. AE: Data curation, Investigation, Methodology, Resources, Software, Supervision, Validation, Visualization, Writing&#x02014;review &#x00026; editing. SK: Conceptualization, Data curation, Investigation, Methodology, Project administration, Resources, Validation, Visualization, Writing&#x02014;review &#x00026; editing. KM: Conceptualization, Funding acquisition, Investigation, Methodology, Project administration, Validation, Visualization, Writing&#x02014;review &#x00026; editing. EA: Data curation, Formal Analysis, Investigation, Methodology, Project administration, Software, Supervision, Validation, Writing&#x02014;review &#x00026; editing. EB: Conceptualization, Formal Analysis, Investigation, Methodology, Software, Validation, Visualization, Writing&#x02014;review &#x00026; editing.</p>
</sec>
</body>
<back>
<sec sec-type="funding-information" id="s8">
<title>Funding</title>
<p>The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.</p>
</sec>
<sec sec-type="COI-statement" id="conf1">
<title>Conflict of interest</title>
<p>The authors declare 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="disclaimer" id="s9">
<title>Publisher&#x00027;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec><sec sec-type="supplementary-material" id="s10">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fpubh.2024.1356830/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fpubh.2024.1356830/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Table_1.DOCX" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_2.DOCX" id="SM2" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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