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<article article-type="review-article" dtd-version="2.3" xml:lang="EN" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Int J Public Health</journal-id>
<journal-title>International Journal of Public Health</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Int J Public Health</abbrev-journal-title>
<issn pub-type="epub">1661-8564</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">1606226</article-id>
<article-id pub-id-type="doi">10.3389/ijph.2023.1606226</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Public Health Archive</subject>
<subj-group>
<subject>Review</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Relationship Between Outdoor Air Pollutant Exposure and Premature Delivery in China- Systematic Review and Meta-Analysis</article-title>
<alt-title alt-title-type="left-running-head">Wang et al.</alt-title>
<alt-title alt-title-type="right-running-head">Air Pollutants and Premature Delivery</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Wang</surname>
<given-names>Xue</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn1">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2319972/overview"/>
</contrib>
<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Wang</surname>
<given-names>Xin</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="author-notes" rid="fn1">
<sup>&#x2020;</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Gao</surname>
<given-names>Chenghua</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Xu</surname>
<given-names>Xiaoqian</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Li</surname>
<given-names>Lehui</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Liu</surname>
<given-names>Yan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Li</surname>
<given-names>Zichao</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Xia</surname>
<given-names>Yuan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Fang</surname>
<given-names>Xin</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>School of Public Health of Inner Mongolia Medical University</institution>, <addr-line>Hohhot</addr-line>, <country>China</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Division of Molecular Signaling</institution>, <institution>Department of the Advanced Biomedical Research</institution>, <institution>Interdisciplinary Graduate School of Medicine</institution>, <institution>University of Yamanashi</institution>, <addr-line>Kofu</addr-line>, <country>Japan</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/1002545/overview">Gabriel Gulis</ext-link>, University of Southern Denmark, Denmark</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/1041394/overview">Santu Ghosh</ext-link>, St John&#x2019;s Medical College, India</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Xin Fang, <email>18686066179@163.com</email>
</corresp>
<fn fn-type="equal" id="fn1">
<label>
<sup>&#x2020;</sup>
</label>
<p>These authors have contributed equally to this work</p>
</fn>
<fn id="fn001" fn-type="other">
<p>This Review is part of the IJPH Special Issue &#x201c;Public Health and Primary Care, is 1 &#x2b; 1 &#x3d; 1?&#x201d;</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>09</day>
<month>10</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>68</volume>
<elocation-id>1606226</elocation-id>
<history>
<date date-type="received">
<day>22</day>
<month>05</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>28</day>
<month>09</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Wang, Wang, Gao, Xu, Li, Liu, Li, Xia and Fang.</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Wang, Wang, Gao, Xu, Li, Liu, Li, Xia and Fang</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>
<p>
<bold>Objective:</bold> Preterm birth (PTB) is considered as a public health problem and one of the main risk factors related to the global disease burden. The purpose of this study aims to explore the influence of exposure to major air pollutants at different pregnancies on PTB.</p>
<p>
<bold>Methods:</bold> The relationship between air pollutants and PTB in China was collected from cohort studies and case-control studies published before 30 April 2022. Meta-analysis was carried out with STATA 15.0 software.</p>
<p>
<bold>Results:</bold> A total of 2,115 papers were retrieved, of which 18 papers met the inclusion criteria. The comprehensive effect of pollutant exposure and PTB were calculated. PM<sub>2.5</sub> during entire pregnancy and O<sub>3</sub> exposure during third trimester were positively associated with preterm birth. Every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the average concentration of PM<sub>2.5</sub> during the whole pregnancy will increase the risk of premature delivery by 4%, and every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the average concentration of O<sub>3</sub> in the third trimester will increase the risk of premature delivery by 1%.</p>
<p>
<bold>Conclusion:</bold> Exposure to PM<sub>2.5</sub> entire prenatal pregnancy and O<sub>3</sub> in third trimester is associated with an increased risk of preterm birth occurrence.</p>
</abstract>
<kwd-group>
<kwd>atmospheric pollutants</kwd>
<kwd>preterm birth</kwd>
<kwd>meta-analysis</kwd>
<kwd>China</kwd>
<kwd>adverse pregnancy outcome</kwd>
</kwd-group>
</article-meta>
</front>
<body>
<sec id="s1">
<title>Introduction</title>
<p>Preterm birth (PTB) is defined as delivery before 37&#xa0;weeks of pregnancy, which has long-term negative impacts on the development of newborns and may lead to stunting. PTB is becoming more and more common in developing and even some developed countries [<xref ref-type="bibr" rid="B1">1</xref>], although the underlying causes are still unknown. Premature delivery is a common adverse pregnancy outcome. Because of its serious impact on life and health, it brings a great burden on families and society, leading to perinatal and early neonatal death (especially in developing countries) and immature organ development, which leads to physical disability or mental disorders [<xref ref-type="bibr" rid="B2">2</xref>, <xref ref-type="bibr" rid="B3">3</xref>]. PTB is regarded as a public health issue and one of the key risk factors contributing to the Global Burden of Disease. As a result, there is an urgent need to investigate PTB risk factors in order to reduce the occurrence of PTB and thus improve human health.</p>
<p>PTB has been linked to a variety of factors, including social and economic status, race, genetic influences, medical conditions, mental disorders, and environmental exposures [<xref ref-type="bibr" rid="B4">4</xref>]. Air pollution is a major component of environmental pollution, and it is considered as a risk factor of many diseases. According to the latest estimate of the World Health Organization, about 90% of the world&#x2019;s population breathes air with high concentrations of pollutants, and as many as 7 million people die every year due to environmental and indoor air pollution [<xref ref-type="bibr" rid="B5">5</xref>]. The impact of air pollution on health has become a global public health problem (<xref ref-type="bibr" rid="B6">6</xref>). In addition to causing respiratory [<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B8">8</xref>] and cardiovascular diseases [<xref ref-type="bibr" rid="B9">9</xref>], more and more studies have investigated the influence of air pollution on premature delivery, including China [<xref ref-type="bibr" rid="B10">10</xref>], South Korea [<xref ref-type="bibr" rid="B11">11</xref>], Japan [<xref ref-type="bibr" rid="B12">12</xref>] and the United States [<xref ref-type="bibr" rid="B13">13</xref>]. Although most published studies have reported that various air pollutants are related to PTB, the nature of the pollutants studied and the related pregnancy outcomes are different. At present, there is a lack of toxicological data to guide pregnant women to choose the most relevant vulnerable exposure window [<xref ref-type="bibr" rid="B14">14</xref>]. Previous surveys have used a wide range of exposure windows (i.e., weeks, months and 3&#xa0;months) to determine the time relationship between air pollution and adverse pregnancy outcomes [<xref ref-type="bibr" rid="B15">15</xref>]. Some studies have reported that exposure in the first trimester of pregnancy is associated with an increased risk of PTB [<xref ref-type="bibr" rid="B16">16</xref>]. Other studies have shown that exposure in the third trimester has a greater impact [<xref ref-type="bibr" rid="B17">17</xref>]. Therefore, the relationship between different pollutants exposure and different adverse pregnancy outcomes is complicated, and different periods of pollutant exposure during pregnancy have different effects on pregnancy outcomes [<xref ref-type="bibr" rid="B18">18</xref>]. Some previous studies have discussed the effect of air pollution on PTB [<xref ref-type="bibr" rid="B19">19</xref>&#x2013;<xref ref-type="bibr" rid="B21">21</xref>], but they are mainly carried out in developed countries. Although the level of air pollution in Asian countries is usually higher, there has been a lack of research in these countries [<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B22">22</xref>]. Fetuses are particularly sensitive to environmental hazards because cell proliferation, differentiation and organ development accelerate during pregnancy, which may directly damage the fetus or interfere with placental function [<xref ref-type="bibr" rid="B23">23</xref>]. Several possible biological approaches have been put forward in previous studies. On the one hand, placental DNA adducts produced by air pollution are more common in mothers exposed to high levels of air pollution [<xref ref-type="bibr" rid="B24">24</xref>]. The high expression of fetal DNA adducts may reduce the ability of DNA repair and detoxification enzymes [<xref ref-type="bibr" rid="B25">25</xref>]. In previous studies, DNA adducts were associated with shortened pregnancy [<xref ref-type="bibr" rid="B26">26</xref>]. On the other hand, its mechanism may be related to hematological factors. The increase of blood viscosity caused by exposure to air pollution and hematological factors may be related to insufficient placental perfusion, which leads to PTB(24). Animal studies also support the finding that exposure to urban air pollution during pregnancy will inhibit fetal growth, which is closely related to the risk of premature delivery [<xref ref-type="bibr" rid="B27">27</xref>]. Therefore, this paper plans to collect the previous cohort and case-control studies, effectively increasing the sample size, and further improving the evidence level by including only the studies with high Newcastle-Ottawa Quality Score (NOS) and discussing the effects of air pollution exposure during different pregnancies on PTB.</p>
</sec>
<sec sec-type="methods" id="s2">
<title>Methods</title>
<sec id="s2-1">
<title>Literature Search</title>
<p>Inclusion criteria: 1) published before 31 April 2022, the contents of the literature were all independent epidemiological findings; 2) the study was about the effect of atmospheric pollutants on preterm birth in China; 3) all studies defined delivery at less than 37&#xa0;weeks of gestational age as preterm birth according to WHO criteria; and defined the 3 gestational window periods in the following way, namely: the first 3&#xa0;months of pregnancy (before the end of 12&#xa0;weeks of gestation) as early gestation, second trimester at the end of 13&#x2013;27&#xa0;weeks of gestation, and third trimester after 28&#xa0;weeks of gestation; 4) the risk factors studied included air pollutants; 5) the results of each literature is the quantitative dose-response relationships between air pollution and premature delivery, including parameter estimation and 95% CI of the risk of premature delivery with the increase in air pollutant concentration of 10&#xa0;&#x3bc;g/m<sup>3</sup>; 6) the study methods were cohort studies or case-control studies.</p>
<p>Exclusion criteria: 1) animal studies, <italic>in vitro</italic> toxicology studies, reviews and review articles; 2) studies with risk factors limited to indoor pollution, some kind of heavy metal or organic pollution; 3) studies examining the effects of air pollution due to occupational exposure on adverse pregnancy outcomes; 4) studies on the birth outcomes except premature delivery; 5) studies for which RR values and 95% CI were not available; 6) the original article contains no original data.</p>
</sec>
<sec id="s2-2">
<title>Literature Search Strategy</title>
<p>The literature on the effect of outdoor air pollution on preterm birth in China published at home and abroad before 31 April 2022, was collected by computer search of PubMed, Cochrane Library, Web of science, China Journal Full Text Database (CNKI), Wanfang Science and Technology Information Database and Weipu Chinese Science and Technology Journal Full Text Database, and by tracing the relevant literature. The retrieved keywords were: air pollution, environmental pollution, air quality, atmospheric pollution, atmospheric pollutants, PM<sub>10</sub>, PM<sub>2.5</sub>, NO<sub>2</sub>, SO<sub>2</sub>, O<sub>3</sub>, sulfur dioxide, nitrogen dioxide, ozone, particulate matter, adverse birth outcomes, adverse pregnancy outcomes, preterm birth premature birth, preterm delivery, small for gestational age, Chinese, China, atmospheric pollution, air pollution, particulate matter, respirable particulate matter, fine particulate matter, sulfur dioxide, nitrogen dioxide, ozone, adverse pregnancy outcomes, preterm birth, less than gestational age.</p>
</sec>
<sec id="s2-3">
<title>Literature Screening and Extraction</title>
<p>The literature search was conducted independently by two researchers, and the literature initially examined was screened one by one according to the inclusion and exclusion criteria, and relevant information was extracted and checked for differences. If they had different opinions, they all discussed and unified. The information extracted included authors, year of publication, study site, study duration, number of study participants, study method, exposure assessment method, type of air pollutant, and period of exposure. Because the sensitivity of fetuses to pollutant exposure in different periods is different, and the results of the influence of pollutant exposure on premature delivery in different periods may be different, most of the original documents are analyzed separately according to gestational period, so the data are extracted separately according to gestational period.</p>
</sec>
<sec id="s2-4">
<title>Statistical Analysis</title>
<p>Statistical software Stata 15.0 was used for meta-analysis of data, and <italic>I</italic>
<sup>
<italic>2</italic>
</sup> statistics were used to measure the heterogeneity of individual research results. If there was no heterogeneity between the studies (<italic>I</italic>
<sup>
<italic>2</italic>
</sup> &#x3c; 50% or <italic>p</italic> &#x3e; 0.10), the fixed effect model was used to calculate the comprehensive RR value and its 95% CI. If there is heterogeneity, a random effects model was used and subgroup analysis was used to explore the source of heterogeneity. Sensitivity analysis was used to evaluate the stability of the Meta-analysis findings and to determine the differences in the combined effect values before and after excluding a particular study. Egger linear regression analysis was used to analyze the publication bias, and the test level was bilateral &#x3b1; &#x3d; 0.01.</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>Results</title>
<sec id="s3-1">
<title>General Description</title>
<p>A total of 1,615 researches were retrieved. After a preliminary screening of the title and abstract, 78 potentially suitable studies were selected. <xref ref-type="fig" rid="F1">Figure 1</xref> depicts the flowchart of the study search and selection in the Meta-analysis and lists the 18 publications that were deemed eligible after additional assessment of the complete texts of these articles. The data features of the 18 papers included in this meta-analysis are shown in <xref ref-type="table" rid="T1">Table 1</xref>. In these 18 investigations, 11, 8, 4, 6 and 3 investigated the effects of PM<sub>2.5</sub>, PM<sub>10</sub>, SO<sub>2</sub>, NO<sub>2</sub> and O<sub>3</sub> on PTB respectively. Only two surveys have been conducted on Chinese national populations, most of which (<italic>n</italic> &#x3d; 11) were conducted in southern cities, followed by northern cities (<italic>n</italic> &#x3d; 5). There were about 1,882&#x2013;1,240,978 participants in these studies. Three researchers used satellite data, and 15 researchers used monitoring station data to determine exposure assessment methods.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Flow chart of literature screening (China, 2023).</p>
</caption>
<graphic xlink:href="ijph-68-1606226-g001.tif"/>
</fig>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Basic information of the literature included in the Meta-analysis. (China, 2023).</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Authors</th>
<th align="center">Publication date</th>
<th align="center">Study site</th>
<th align="center">Study years</th>
<th align="center">Sample size</th>
<th align="center">Pollutant</th>
<th align="center">Study design</th>
<th align="center">Exposure assessment</th>
<th align="center">NOS score</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">[<xref ref-type="bibr" rid="B34">34</xref>]</td>
<td align="center">2015</td>
<td align="left">Beijing</td>
<td align="center">2007&#x2013;2010</td>
<td align="center">50,874</td>
<td align="left">PM<sub>10</sub>, NO<sub>2</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B35">35</xref>]</td>
<td align="center">2016</td>
<td align="left">Taiyuan</td>
<td align="center">2013&#x2013;2014</td>
<td align="center">1,882</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B36">36</xref>]</td>
<td align="center">2015</td>
<td align="left">Wuhan</td>
<td align="center">2010&#x2013;2013</td>
<td align="center">95,911</td>
<td align="left">O<sub>3</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B37">37</xref>]</td>
<td align="center">2018</td>
<td align="left">China</td>
<td align="center">2013&#x2013;2014</td>
<td align="center">1,240,978</td>
<td align="left">PM<sub>2.5</sub>, PM<sub>10</sub>
</td>
<td align="left">cohort study</td>
<td align="left">satellite remote sensing</td>
<td align="center">8</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B38">38</xref>]</td>
<td align="center">2018</td>
<td align="left">Taizhou</td>
<td align="center">2013&#x2013;2016</td>
<td align="center">24,246</td>
<td align="left">PM<sub>2.5</sub>, PM<sub>10</sub>, NO<sub>2</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B39">39</xref>]</td>
<td align="center">2018</td>
<td align="left">Shanghai</td>
<td align="center">2011&#x2013;2014</td>
<td align="center">132,783</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">Case control study</td>
<td align="left">satellite remote sensing</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B40">40</xref>]</td>
<td align="center">2018</td>
<td align="left">Lanzhou</td>
<td align="center">2010&#x2013;2012</td>
<td align="center">8,969</td>
<td align="left">PM<sub>10</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">8</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B41">41</xref>]</td>
<td align="center">2019</td>
<td align="left">Shanghai</td>
<td align="center">2014&#x2013;2015</td>
<td align="center">25,493</td>
<td align="left">NO<sub>2</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">5</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B42">42</xref>]</td>
<td align="center">2019</td>
<td align="left">Guangdong</td>
<td align="center">2014&#x2013;2017</td>
<td align="center">1,455,026</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B43">43</xref>]</td>
<td align="center">2022</td>
<td align="left">Henan</td>
<td align="center">2013&#x2013;2018</td>
<td align="center">196,780</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B44">44</xref>]</td>
<td align="center">2019</td>
<td align="left">Guangdong</td>
<td align="center">2014&#x2013;2015</td>
<td align="center">3,550</td>
<td align="left">PM<sub>2.5</sub>, PM<sub>10</sub>, SO<sub>2</sub>, NO<sub>2</sub>, O<sub>3</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">5</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B45">45</xref>]</td>
<td align="center">2020</td>
<td align="left">Shanghai</td>
<td align="center">2013&#x2013;2016</td>
<td align="center">3,692</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">Case control study</td>
<td align="left">satellite remote sensing</td>
<td align="center">5</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B46">46</xref>]</td>
<td align="center">2019</td>
<td align="left">Guangdong</td>
<td align="center">2014&#x2013;2017</td>
<td align="center">1,455,026</td>
<td align="left">O<sub>3</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B47">47</xref>]</td>
<td align="center">2021</td>
<td align="left">Shiyan</td>
<td align="center">2015&#x2013;2017</td>
<td align="center">13,111</td>
<td align="left">PM<sub>10</sub>, PM<sub>2.5</sub>, NO<sub>2</sub>, SO<sub>2</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B48">48</xref>]</td>
<td align="center">2021</td>
<td align="left">China</td>
<td align="center">2009&#x2013;2011</td>
<td align="center">5,976</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B49">49</xref>]</td>
<td align="center">2022</td>
<td align="left">Yan&#x2019; an</td>
<td align="center">2018&#x2013;2019</td>
<td align="center">10,722</td>
<td align="left">PM<sub>2.5</sub>, PM<sub>10</sub>, SO<sub>2</sub>, NO<sub>2</sub>, O<sub>3</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B50">50</xref>]</td>
<td align="center">2022</td>
<td align="left">Shanghai</td>
<td align="center">2016.1&#x2013;2016.6</td>
<td align="center">10,370</td>
<td align="left">PM<sub>2.5</sub>
</td>
<td align="left">Case control study</td>
<td align="left">Monitoring station</td>
<td align="center">5</td>
</tr>
<tr>
<td align="left">[<xref ref-type="bibr" rid="B51">51</xref>]</td>
<td align="center">2022</td>
<td align="left">Chongqing</td>
<td align="center">2015&#x2013;2020</td>
<td align="center">572,116</td>
<td align="left">PM<sub>2.5</sub>, PM<sub>10</sub>, SO<sub>2</sub>, O<sub>3</sub>, NO<sub>2</sub>
</td>
<td align="left">cohort study</td>
<td align="left">Monitoring station</td>
<td align="center">7</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-2">
<title>Heterogeneity Test</title>
<p>The results of exposure to PM<sub>2.5</sub>, PM<sub>10</sub>, SO<sub>2</sub>, NO<sub>2</sub> and O<sub>3</sub> in different pregnancy were analyzed by heterogeneity. The heterogeneity of O<sub>3</sub> exposure results in the third trimester of pregnancy was low, and the effect is estimated by using fixed effect model, while the results of the other pollutants had high heterogeneity, the random effect model is used to the research results. The results showed that every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in PM<sub>2.5</sub> concentration during the whole pregnancy increases the risk of PTB by 4% (RR: 1.04, 95% CI: 1.01, 1.07). The risk of PTB increased by 1% (RR: 1.01, 95% CI: 1.01, 1.02) for every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in O<sub>3</sub> concentration in the third trimester. The effects of PM<sub>10</sub>, SO<sub>2</sub> and NO<sub>2</sub> exposure in different pregnancy on PTB were not found statistically significant. <xref ref-type="table" rid="T2">Table 2</xref> and <xref ref-type="fig" rid="F2">Figure 2</xref> (<xref ref-type="sec" rid="s8">Supplementary Figures S1&#x2013;S3</xref>).</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Summary of integrated impact estimates of premature birth associated with air pollution (PM<sub>2.5</sub>, PM<sub>10</sub>, NO<sub>2</sub>, SO<sub>2</sub> and O<sub>3</sub>) (China, 2023).</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Air pollution and PTB</th>
<th rowspan="2" align="center">Trimester</th>
<th rowspan="2" align="center">No. of studies</th>
<th colspan="2" align="center">Test of association</th>
<th colspan="2" align="center">Test of heterogeneity</th>
<th align="center">Egger&#x2019;s test</th>
</tr>
<tr>
<th align="center">
<italic>RR</italic>
</th>
<th align="center">95% <italic>CI</italic>
</th>
<th align="center">
<italic>I</italic>
<sup>2</sup> (%)</th>
<th align="center">
<italic>p</italic>-Value</th>
<th align="center">
<italic>p</italic>-Value</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="4" align="left">PM<sub>2.5</sub>
</td>
<td align="left">Entire</td>
<td align="center">10</td>
<td align="center">1.04</td>
<td align="center">1.01, 1.07</td>
<td align="center">91.5</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.916</td>
</tr>
<tr>
<td align="left">First</td>
<td align="center">11</td>
<td align="center">1.00</td>
<td align="center">0.97, 1.02</td>
<td align="center">94.3</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.209</td>
</tr>
<tr>
<td align="left">Second</td>
<td align="center">11</td>
<td align="center">1.00</td>
<td align="center">0.97, 1.02</td>
<td align="center">92.4</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.208</td>
</tr>
<tr>
<td align="left">Third</td>
<td align="center">10</td>
<td align="center">1.01</td>
<td align="center">0.97, 1.05</td>
<td align="center">96.5</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.453</td>
</tr>
<tr>
<td rowspan="4" align="left">PM<sub>10</sub>
</td>
<td align="left">Entire</td>
<td align="center">7</td>
<td align="center">1.03</td>
<td align="center">0.99, 1.06</td>
<td align="center">91.4</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.321</td>
</tr>
<tr>
<td align="left">First</td>
<td align="center">7</td>
<td align="center">0.97</td>
<td align="center">0.95, 1.00</td>
<td align="center">84.2</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.559</td>
</tr>
<tr>
<td align="left">Second</td>
<td align="center">8</td>
<td align="center">1.00</td>
<td align="center">0.97, 1.02</td>
<td align="center">72.0</td>
<td align="center">0.001</td>
<td align="center">0.546</td>
</tr>
<tr>
<td align="left">Third</td>
<td align="center">7</td>
<td align="center">1.03</td>
<td align="center">0.98, 1.08</td>
<td align="center">94.6</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.506</td>
</tr>
<tr>
<td rowspan="4" align="left">SO<sub>2</sub>
</td>
<td align="left">Entire</td>
<td align="center">4</td>
<td align="center">0.95</td>
<td align="center">0.69, 1.00</td>
<td align="center">63.9</td>
<td align="center">0.040</td>
<td align="center">0.978</td>
</tr>
<tr>
<td align="left">First</td>
<td align="center">4</td>
<td align="center">0.92</td>
<td align="center">0.72, 1.13</td>
<td align="center">98.3</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.851</td>
</tr>
<tr>
<td align="left">Second</td>
<td align="center">4</td>
<td align="center">0.96</td>
<td align="center">0.80, 1.10</td>
<td align="center">96.1</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.761</td>
</tr>
<tr>
<td align="left">Third</td>
<td align="center">4</td>
<td align="center">0.96</td>
<td align="center">0.85, 1.06</td>
<td align="center">92.0</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.462</td>
</tr>
<tr>
<td rowspan="4" align="left">NO<sub>2</sub>
</td>
<td align="left">Entire</td>
<td align="center">5</td>
<td align="center">1.06</td>
<td align="center">0.92, 1.20</td>
<td align="center">94.2</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.181</td>
</tr>
<tr>
<td align="left">First</td>
<td align="center">6</td>
<td align="center">0.97</td>
<td align="center">0.93, 1.01</td>
<td align="center">67.7</td>
<td align="center">0.009</td>
<td align="center">0.041</td>
</tr>
<tr>
<td align="left">Second</td>
<td align="center">6</td>
<td align="center">1.03</td>
<td align="center">0.94, 1.11</td>
<td align="center">91.7</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.060</td>
</tr>
<tr>
<td align="left">Third</td>
<td align="center">6</td>
<td align="center">1.00</td>
<td align="center">0.94, 1.06</td>
<td align="center">89.4</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.213</td>
</tr>
<tr>
<td rowspan="4" align="left">O<sub>3</sub>
</td>
<td align="left">Entire</td>
<td align="center">4</td>
<td align="center">0.98</td>
<td align="center">0.91, 1.05</td>
<td align="center">98.2</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.898</td>
</tr>
<tr>
<td align="left">First</td>
<td align="center">4</td>
<td align="center">0.98</td>
<td align="center">0.95, 1.02</td>
<td align="center">97.8</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.330</td>
</tr>
<tr>
<td align="left">Second</td>
<td align="center">4</td>
<td align="center">0.98</td>
<td align="center">0.93, 1.02</td>
<td align="center">98.6</td>
<td align="center">&#x3c;0.001</td>
<td align="center">0.449</td>
</tr>
<tr>
<td align="left">Third</td>
<td align="center">4</td>
<td align="center">1.01</td>
<td align="center">1.01, 1.02</td>
<td align="center">0.0</td>
<td align="center">0.712</td>
<td align="center">0.593</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Funnel plot of the association between exposure to PM<sub>2.5</sub> and premature birth. Pooled estimates of effect size are indicated by vertical points of diamonds, size of shaded area around the diamond is proportional to weight, and 95% <italic>CI</italic> are represented by horizontal line. (<bold>(A)</bold>, entire pregnancy; <bold>(B)</bold>, first trimester; <bold>(C)</bold>, second trimester; <bold>(D)</bold>, third trimester). (China, 2023).</p>
</caption>
<graphic xlink:href="ijph-68-1606226-g002.tif"/>
</fig>
</sec>
<sec id="s3-3">
<title>Subgroup Analysis</title>
<p>By further analysis of different research methods (cohort and case-control study). In the case-control study, every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in PM<sub>2.5</sub> concentration during the whole pregnancy increased the risk of PTB by 4% (RR:1.04, 95% CI: 1.01, 1.07). Every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the average concentration of SO<sub>2</sub> in early and late pregnancy will increase the risk of PTB by 4% (first pregnancy RR: 1.04, 95% CI: 1.02, 1.07, late pregnancy RR: 1.04, 95% CI: 1.01, 1.06). In the cohort study, the risk of PTB was reduced by 11%, 15%, and 12% for each 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in SO<sub>2</sub> concentration throughout pregnancy, mid-term and late in pregnancy (whole pregnancy RR: 0.89, 95% CI: 0.84, 0.94, second pregnancy RR: 0.85, 95% CI: 0.74, 0.97, late pregnancy RR: 0.88, 95% CI: 0.82). The risk of PTB was reduced by 6% for each 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in NO<sub>2</sub> concentration in first pregnancy (RR: 0.94, 95% CI: 0.90, 0.99). According to the study areas (southern cities, northern cities and the whole country), the influence of pollutant exposure on PTB was evaluated by stratified analysis. The results show that the influence of PM<sub>2.5</sub> on PTB has statistical significance in the study of northern cities (RR: 1.03, 95% CI: 1.01, 1.05). Studies conducted in southern cities showed that the risk of PTB increased by 5% for every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in PM<sub>10</sub> concentration during the whole pregnancy (RR: 1.05, 95% CI: 1.02, 1.09). Because the exposure concentration of pollutants may have different effects on health [<xref ref-type="bibr" rid="B28">28</xref>], we stratify the concentration of pollutants according to WHO standards. Stratified according to different concentrations of pollutants, when the concentration of PM<sub>2.5</sub> exceeds 50&#xa0;&#x3bc;g/m<sup>3</sup>, the PTB will increase by 2.5% (RR:1.025, 95% CI: 1.01, 1.04) for every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase of PM<sub>2.5</sub> during the whole pregnancy. 9% for every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase of PM<sub>2.5</sub> when the concentration is lower than 50&#xa0;&#x3bc;g/m<sup>3</sup>. The heterogeneity of PM<sub>2.5</sub> was significantly reduced in case-control study, northern city study and study with exposure concentration higher than 50&#xa0;&#x3bc;g/m<sup>3</sup>. The heterogeneity of PM<sub>10</sub> in southern cities, SO<sub>2</sub> in cohort study and case-control study, and NO<sub>2</sub> cohort study was significantly reduced. These may be the heterogeneous sources of merger effect. <xref ref-type="table" rid="T3">Table 3</xref> and <xref ref-type="fig" rid="F3">Figure 3</xref>.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Subgroup analysis of premature birth associated with air pollution (PM<sub>2.5</sub>, PM<sub>10,</sub> SO<sub>2</sub>, NO<sub>2</sub> and O<sub>3</sub>) in different late gestational periods. (China, 2023).</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Exposure</th>
<th rowspan="2" align="center">Subgroup</th>
<th align="center">PM2.5</th>
<th align="left"/>
<th align="center">PM10</th>
<th align="left"/>
</tr>
<tr>
<th align="center">Division</th>
<th align="center">RR (95% CI)</th>
<th align="center">
<italic>n</italic>
</th>
<th align="center">RR (95% CI)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="7" align="left">Entire</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 6</td>
<td align="center">1.03 (0.98, 1.08)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.03 (0.97, 1.09)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 5</td>
<td align="center">1.04 (1.01, 1.07)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.03 (1.00, 1.05)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 2</td>
<td align="center">1.03 (1.01, 1.05)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">1.01 (0.96, 1.05)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 7</td>
<td align="center">1.05 (0.98, 1.12)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.05 (1.02, 1.09)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 2</td>
<td align="center">0.99 (0.87, 1.11)</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.00 (1.00, 1.00)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="2" align="left">concentration</td>
<td align="left">&#x3e;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 7</td>
<td align="center">1.03 (1.01, 1.04)</td>
<td align="center">&#x3e;100&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (0.96, 1.07)</td>
</tr>
<tr>
<td align="left">&#x3c;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 5</td>
<td align="center">1.09 (1.03, 1.17)</td>
<td align="center">&#x3c;100&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 5</td>
<td align="center">1.03 (0.99, 1.07)</td>
</tr>
<tr>
<td rowspan="5" align="left">First</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 6</td>
<td align="center">0.98 (0.94, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.93 (0.86, 1.01)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 6</td>
<td align="center">1.03 (1.00, 1.05)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.00 (0.99, 1.01)</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 2</td>
<td align="center">0.99 (0.98, 1.01)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.00 (0.99, 1.01)</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 7</td>
<td align="center">0.99 (0.96, 1.03)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">0.96 (0.89, 1.02)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 2</td>
<td align="center">1.04 (1.00, 1.09)</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="left"/>
</tr>
<tr>
<td rowspan="5" align="left">Second</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 6</td>
<td align="center">1.00 (0.97, 1.02)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.01 (0.97, 1.04)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 6</td>
<td align="center">1.00 (0.96, 1.04)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.00 (0.98, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 2</td>
<td align="center">0.98 (0.88, 1.08)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.00 (0.99, 1.01)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 7</td>
<td align="center">1.01 (0.98, 1.04)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">0.96 (0.89, 1.02)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 2</td>
<td align="center">0.93 (0.75, 1.11)</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.01 (1.00, 1.01)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="5" align="left">Third</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 5</td>
<td align="center">1.00 (0.92, 1.07)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.04 (0.95, 1.08)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 6</td>
<td align="center">1.02 (0.98, 1.06)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.02 (1.00, 1.03)</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 2</td>
<td align="center">0.99 (0.95, 1.03)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (1.00, 1.03)</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 7</td>
<td align="center">1.04 (1.00, 1.08)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.04 (0.97, 1.11)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 2</td>
<td align="center">0.80 (0.73, 0.87)</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
</tbody>
</table>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Exposure</th>
<th rowspan="2" align="center">Subgroup</th>
<th align="center">SO<sub>2</sub>
</th>
<th align="left"/>
<th align="center">NO<sub>2</sub>
</th>
<th align="left"/>
<th align="center">O<sub>3</sub>
</th>
<th align="left"/>
</tr>
<tr>
<th align="center">
<italic>n</italic>
</th>
<th align="center">
<italic>RR</italic> (95% <italic>CI</italic>)</th>
<th align="center">
<italic>n</italic>
</th>
<th align="center">
<italic>RR</italic> (95% <italic>CI</italic>)</th>
<th align="center">
<italic>n</italic>
</th>
<th align="center">
<italic>RR</italic> (95% <italic>CI</italic>)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="7" align="left">Entire</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 2</td>
<td align="center">0.89 (0.84, 0.94)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.07 (0.81, 1.33)</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">0.89 (0.87, 0.90)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 2</td>
<td align="center">0.99 (0.90, 1.08)</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">1.05 (0.99, 1.11)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (0.99, 1.03)</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 1</td>
<td align="center">0.95 (0.93, 0.98)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.01 (0.62, 1.40)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.00 (0.96, 1.04)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 3</td>
<td align="center">0.94 (0.84, 1.05)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.06 (0.91, 1.22)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.97 (0.89, 1.05)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
<tr>
<td rowspan="2" align="left">concentration</td>
<td align="left">&#x3e;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">&#x3e;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 1</td>
<td align="center">0.98 (0.94, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">&#x3e;120&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
<tr>
<td align="left">&#x3c;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 4</td>
<td align="center">0.95 (0.89, 1.01)</td>
<td align="center">&#x3c;50&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 6</td>
<td align="center">1.05 (0.93, 1.18)</td>
<td align="center">&#x3c;120&#xa0;&#x3bc;g/m<sup>3</sup> <italic>n</italic> &#x3d; 5</td>
<td align="center">0.99 (0.94, 1.04)</td>
</tr>
<tr>
<td rowspan="5" align="left">First</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 2</td>
<td align="center">0.83 (0.63, 1.03)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.94 (0.90, 0.99)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.98 (0.89, 1.07)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 2</td>
<td align="center">1.04 (1.02, 1.07)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.00 (0.92, 1.08)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.97 (0.87, 1.06)</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 1</td>
<td align="center">1.05 (1.02, 1.07)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.98 (0.94, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.00 (0.99, 1.01)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 3</td>
<td align="center">0.87 (0.70, 1.05)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">0.98 (0.91, 1.05)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.96 (0.88, 1.04)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
<tr>
<td rowspan="5" align="left">Second</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study n &#x3d; 2</td>
<td align="center">0.85 (0.74, 0.97)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.05 (0.86, 1.24)</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.98 (0.86, 1.09)</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 2</td>
<td align="center">1.02 (1.00, 1.05)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.99 (0.93, 1.06)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.98 (0.93, 1.03)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 1</td>
<td align="center">1.02 (1.00, 1.05)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.97 (0.92, 1.01)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">0.99 (0.99, 1.00)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 3</td>
<td align="center">0.91 (0.76, 1.06)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.05 (0.90, 1.21)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.96 (0.87, 1.06)</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
<tr>
<td rowspan="5" align="left">Third</td>
<td rowspan="2" align="left">Research type</td>
<td align="left">cohort study <italic>n</italic> &#x3d; 2</td>
<td align="center">0.88 (0.82, 0.94)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (0.87, 1.15)</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.01 (1.00, 1.03)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">Case control study <italic>n</italic> &#x3d; 2</td>
<td align="center">1.04 (1.01, 1.06)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">0.99 (0.96, 1.02)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (1.00, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td rowspan="3" align="left">region</td>
<td align="left">north <italic>n</italic> &#x3d; 1</td>
<td align="center">1.03 (1.01, 1.06)</td>
<td align="center">
<italic>n</italic> &#x3d; 2</td>
<td align="center">0.99 (0.96, 1.02)</td>
<td align="center">
<italic>n</italic> &#x3d; 1</td>
<td align="center">1.02 (1.00, 1.04)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">south <italic>n</italic> &#x3d; 3</td>
<td align="center">0.92 (0.81, 1.04)</td>
<td align="center">
<italic>n</italic> &#x3d; 4</td>
<td align="center">1.00 (0.89, 1.11)</td>
<td align="center">
<italic>n</italic> &#x3d; 3</td>
<td align="center">1.01 (1.00, 1.02)<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">China <italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
<td align="center">
<italic>n</italic> &#x3d; 0</td>
<td align="center">&#x2014;</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn1">
<label>
<sup>a</sup>
</label>
<p>
<italic>I</italic>
<italic>
<sup>2</sup>
</italic> &#x3c; 50%.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Funnel plot of the association between exposure to O<sub>3</sub> and premature birth. Pooled estimates of effect size are indicated by vertical points of diamonds, size of shaded area around the diamond is proportional to weight, and 95% <italic>CI</italic> are represented by horizontal line. (<bold>(A)</bold>, entire pregnancy; <bold>(B)</bold> first trimester; <bold>(C)</bold>, second trimester; <bold>(D)</bold>, third trimester). (China, 2023).</p>
</caption>
<graphic xlink:href="ijph-68-1606226-g003.tif"/>
</fig>
</sec>
<sec id="s3-4">
<title>Publication Bias and Sensitivity Analysis</title>
<p>Taking lgRR as the abscissa and its standard deviation as the ordinate, the funnel diagram was drawn according to pregnancy periods, and it was found that there was no publication bias in the included literature. By excluding studies one by one in turn, the sensitivity analysis was conducted to evaluate the robustness of the effect, and it was found that the effect of various pollutants exposure on PTB risk were stable in this meta-analysis (<xref ref-type="sec" rid="s8">Supplementary Figures S4&#x2013;S25</xref>).</p>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>Discussion</title>
<p>The influence of air pollutants on premature delivery has become the focus of attention. This Meta-analysis included 18 eligible studies to investigate the correlation between the effects of each 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the mean concentration of five major ambient air pollutants (including PM<sub>2.5</sub>, PM <sub>10</sub>, NO<sub>2</sub>, SO<sub>2</sub> and O<sub>3</sub>) during pregnancy exposure on preterm birth. The results showed that exposure to PM<sub>2.5</sub> throughout pregnancy and O<sub>3</sub> in late pregnancy was positively correlated with PTB. Every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the average concentration of PM<sub>2.5</sub> in the whole pregnancy increased the risk of premature delivery by 4%, and every 10&#xa0;&#x3bc;g/m<sup>3</sup> increase in the average concentration of O<sub>3</sub> in the third trimester increased the risk of premature delivery by 1%. Every increase of 10&#xa0;&#x3bc;g/m<sup>3</sup> in the exposure concentration of residual pollutants during different pregnancy has no significant effect on the incidence of premature delivery. As a major component of air pollution mixture, PM<sub>2.5</sub> is more likely to harm human health due to its special characteristics, such as small size, large specific surface area, long floating time in the air, and adsorption capacity [<xref ref-type="bibr" rid="B29">29</xref>]. SUN, Chen et al. [<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>] similarly found that PM<sub>2.5</sub> exposure throughout pregnancy was associated with preterm delivery, and an increase of PM<sub>2.5</sub> in early to mid-late pregnancy 10&#xa0;&#x3bc;g/m<sup>3</sup>, the risk of preterm birth occurrence was not significant. Luo et al. [<xref ref-type="bibr" rid="B31">31</xref>] found that PM<sub>2.5</sub> exposure throughout pregnancy was not associated with preterm birth. Liu et al. [<xref ref-type="bibr" rid="B32">32</xref>] reported results shows that there is a significant correlation between low exposure of PM<sub>2.5</sub> in early pregnancy and premature delivery. This inconsistency may be due to the different number of studies involved due to different increments in pollutant exposure levels, search times, and search scopes, which may be the main reason for the discrepancy in study results. Current epidemiological evidence suggests that women in the first trimester of pregnancy tend to be less active outdoors when reported PM<sub>2.5</sub> concentrations are high, which may overestimate ambient PM<sub>2.5</sub> exposure and lead to bias. However, during periods of relatively low reported PM<sub>2.5</sub> concentrations, they are relatively less aware of self-protection against air pollution, which may lead to a high risk of preterm birth.</p>
<p>Pregnancy is a time when people are most susceptible to the effects of air pollution, although past researches have produced mixed findings. Early gestation (first or third month), according to some studies, is the window of susceptibility, however later gestation is supported by other studies (third gestation, last month, or last week). In the present study, the effect of different gestational pollutant exposures on preterm birth was investigated and only O<sub>3</sub> exposure in late pregnancy was found to promote preterm birth. The results of Ju et al. [<xref ref-type="bibr" rid="B33">33</xref>] also showed that O<sub>3</sub> exposure in early and mid-late pregnancy was significantly associated with preterm birth. This is similar to our results, suggesting that the susceptibility window may be related to the specificity of different pollutants and needs to be further explored.</p>
<p>It is well known that the toxicity and health effects of air pollutants may vary by geographic region. Therefore, it is reasonable to assess the effects of different gestational air pollutant exposures on PTB by regional subgroup analysis. Subgroup analyses in different regions showed regional differences in the effects of air pollution on PTB. The results showed that the exposure of PM<sub>2.5</sub> in the northern area and PM<sub>10</sub> in southern area during pregnancy was significantly related to the increase of PTB, but other pollutants did not find this correlation. Due to the differences in living habits, climate and pollutant concentrations between the northern and southern regions, it was found that the concentration of PM<sub>2.5</sub> in the northern region was higher than that in the southern region due to coal burning in winter. The quality of the results from long-term cohort studies is obviously better than that of case-control studies. Especially the prospective cohort studies, is considered to be the most reliable results in observational epidemiology. Therefore, we used different research methods to carry out subgroup analysis. The results showed that SO<sub>2</sub> exposure in the second and third trimester of pregnancy was significantly correlated with the decrease of PTB, while in the case-control study, SO<sub>2</sub> exposure in the first trimester of pregnancy was significantly correlated with the increase of PTB. The cohort study found that NO<sub>2</sub> exposure in early pregnancy was significantly correlated with the decrease of PTB, while NO<sub>2</sub> exposure in middle and late pregnancy was not significantly correlated with premature delivery.</p>
<p>We discovered substantial variability among the included studies, which is predictable in view of the limitations of our meta-analysis. In order to quantitatively aggregate individual estimates from studies with substantial heterogeneity, we employed a random effects model. Subgroup analysis was also used to investigate the causes of heterogeneity. The results show that, even though the study design and study area only partially explain the variability, most subgroup analyses still revealed significant heterogeneity. These results imply that due to the small number of related studies, variability of the included studies may be affected by other factors that are not considered in this analysis, such as socio-economic status and chemical composition of pollutants. Therefore, more studies are needed to investigate the causes of heterogeneity in the future. In several studies, personal samplers were used to measure the exposure of pregnant women to air pollutants, and the results were more accurate. Therefore, more research on personal information might be helpful for future analysis.</p>
<sec id="s4-1">
<title>Conclusion</title>
<p>Exposure to PM<sub>2.5</sub> throughout pregnancy may be related to the increased risk of PTB, but prenatal exposure to PM<sub>10</sub>, SO<sub>2</sub>, NO<sub>2</sub> and O<sub>3</sub> has no significant correlation. Analysis stratified by different gestational periods showed that O<sub>3</sub> exposure in late pregnancy may increase the risk of preterm birth occurrence, but the overall level of effect was not high. The sensitivity windows for different pollutants are different, suggesting that more in-depth research is needed in this field in the future.</p>
</sec>
</sec>
</body>
<back>
<sec id="s5">
<title>Author Contributions</title>
<p>All authors listed have made a substantial, direct, and intellectual contribution to the work and approved it for publication.</p>
</sec>
<sec id="s6">
<title>Funding</title>
<p>This study was supported by the Inner Mongolia Autonomous Region (Health science and Technology Program) under grant (202201229) and the Inner Mongolia Medical University (&#x201c;Zhiyuan Talents&#x201d; project) under grant (ZY0201028).</p>
</sec>
<sec sec-type="COI-statement" id="s7">
<title>Conflict of Interest</title>
<p>The authors declare that they do not have any conflicts of interest.</p>
</sec>
<ack>
<p>The authors would like to thank all the reviewers who participated in the review, as well as the Inner Mongolia People&#x2019;s Hospital, the Inner Mongolia Autonomous Region Health Committee Foundation Group, and Inner Mongolia Medical University for the &#x201c;Zhiyuan Talents&#x201d; project.</p>
</ack>
<sec id="s8">
<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.ssph-journal.org/articles/10.3389/ijph.2023.1606226/full#supplementary-material">https://www.ssph-journal.org/articles/10.3389/ijph.2023.1606226/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.docx" id="SM1" mimetype="application/docx" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
<ref-list>
<title>References</title>
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