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<front>
<journal-meta>
<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>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpubh.2024.1490458</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Public Health</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Moderate PM<sub>10</sub> exposure increases prostate cancer: a longitudinal nationwide cohort study (2010&#x02013;2020)</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Rho</surname> <given-names>Mi Jung</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author" corresp="yes">
<name><surname>Park</surname> <given-names>Yong Hyun</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x0002A;</sup></xref>
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<contrib contrib-type="author" corresp="yes">
<name><surname>Park</surname> <given-names>Jihwan</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<xref ref-type="corresp" rid="c002"><sup>&#x0002A;</sup></xref>
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<aff id="aff1"><sup>1</sup><institution>College of Health Science, Dankook University, Cheonan-si</institution>, <addr-line>Chungcheongnam-do</addr-line>, <country>Republic of Korea</country></aff>
<aff id="aff2"><sup>2</sup><institution>Department of Urology, Seoul St. Mary&#x00027;s Hospital, College of Medicine, The Catholic University of Korea</institution>, <addr-line>Seoul</addr-line>, <country>Republic of Korea</country></aff>
<aff id="aff3"><sup>3</sup><institution>College of Liberal Arts, Dankook University, Cheonan-si</institution>, <addr-line>Chungcheongnam-do</addr-line>, <country>Republic of Korea</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Nurzawani Md Sofwan, Universiti Teknologi MARA Sarawak Branch, Malaysia</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Yuzhu Liu, Nanjing University of Information Science and Technology, China</p>
<p>Ning Chen, Shanghai Jiao Tong University, China</p></fn>
<corresp id="c001">&#x0002A;Correspondence: Yong Hyun Park <email>lestat04&#x00040;catholic.ac.kr</email></corresp>
<corresp id="c002">Jihwan Park <email>jihwanpark&#x00040;dankook.ac.kr</email></corresp>
</author-notes>
<pub-date pub-type="epub">
<day>10</day>
<month>01</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>12</volume>
<elocation-id>1490458</elocation-id>
<history>
<date date-type="received">
<day>03</day>
<month>09</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>23</day>
<month>12</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2025 Rho, Park and Park.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Rho, Park and Park</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>Fine dust exposure has been reported to affect patients with prostate cancer, making it crucial to understand how environmental pollutants impact health. This study aimed to determine the risk of prostate cancer in South Korea associated with moderate levels of fine dust (PM<sub>10</sub>) exposure.</p>
</sec>
<sec>
<title>Methods</title>
<p>We analyzed data from 20,430 individuals in the National Health Insurance Sharing Service database from 2010 to 2020, comparing a new prostate cancer group (<italic>n</italic> = 4,071, 19.9%) with a non-prostate cancer group (<italic>n</italic> = 16,359, 80.1%). Using PM<sub>10</sub> data from Air Korea&#x00027;s annual average air quality database, we conducted logistic regression analysis to assess the risk of prostate cancer.</p>
</sec>
<sec>
<title>Results</title>
<p>Our findings indicate that even moderate PM<sub>10</sub> exposure is a risk factor for developing prostate cancer. Additionally, even at low levels of PM<sub>2.5</sub>, moderate PM<sub>10</sub> exposure significantly impacts prostate cancer development, with lifestyle ha bits potentially lowering this risk.</p>
</sec>
<sec>
<title>Discussion</title>
<p>These results underscore the need for stricter environmental standards for PM<sub>10</sub> and proactive policies to reduce public health and long-term social costs. Public awareness, including mask use and air quality management, is essential.</p>
</sec></abstract>
<kwd-group>
<kwd>particulate matter exposure</kwd>
<kwd>prostate cancer</kwd>
<kwd>PM<sub>10</sub></kwd>
<kwd>the National Health Insurance Sharing Service</kwd>
<kwd>national cohort study</kwd>
</kwd-group>
<contract-sponsor id="cn001">National Research Foundation of Korea<named-content content-type="fundref-id">10.13039/501100003725</named-content></contract-sponsor>
<counts>
<fig-count count="3"/>
<table-count count="4"/>
<equation-count count="0"/>
<ref-count count="45"/>
<page-count count="10"/>
<word-count count="6260"/>
</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>1 Introduction</title>
<p>Environmental pollutants, particularly particulate matter (PM) air pollution, have been increasingly recognized for their significant impact on human health. Numerous studies have established a strong correlation between environmental pollution and various types of cancer, including lung, heart, brain, and respiratory diseases (<xref ref-type="bibr" rid="B1">1</xref>). Among these pollutants, fine dust, specifically PM<sub>10</sub>, has been implicated in a range of diseases such as chronic obstructive pulmonary disease (COPD), asthma, and lung cancer (<xref ref-type="bibr" rid="B2">2</xref>&#x02013;<xref ref-type="bibr" rid="B6">6</xref>). Fine dust penetrates deep into the lungs, causing inflammation and increasing the risk of lung cancer. Additionally, emerging research suggests that fine dust exposure may also contribute to the development of urological cancers, including kidney cancer, urothelial cell carcinoma, and prostate cancer (PCa) (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B8">8</xref>). Some study have also found that renal function and chronic urologic diseases are associated with PM<sub>10</sub> (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>). There are also paper on the relationship between industrial pollution, including PM<sub>10</sub>, and the risk of PCa (<xref ref-type="bibr" rid="B11">11</xref>). However, research on PCa and PM<sub>10</sub> is still needed, and diverse well-designed studies on PCa are needed. In addition, in Korea, there is a public DB on air quality (the Air Korea&#x00027;s annual average air quality database), so research using it is possible.</p>
<p>While various environmental standards for fine dust exist globally, these standards vary by country, reflecting local conditions. In Korea, the environmental standards for fine dust have adopted the second stage of the World Health Organization&#x00027;s (WHO) 2005 interim targets for air quality (<xref ref-type="bibr" rid="B12">12</xref>). According to the 2021 WHO recommendation, the PM<sub>10</sub> standard levels is 15 &#x003BC;g/m<sup>2</sup> for the annual average and 45 &#x003BC;g/m<sup>2</sup> for the 24-h average (<xref ref-type="bibr" rid="B12">12</xref>). However, in Korea, the PM<sub>10</sub> standard levels is 50 &#x003BC;g/m<sup>2</sup> for the annual average and 100 &#x003BC;g/m<sup>2</sup> for the 24-h average (<xref ref-type="bibr" rid="B13">13</xref>). Despite efforts to reduce fine dust levels through various policies, Korea&#x00027;s standard levels concentration remains high compared to that in developed countries.</p>
<p>PCa is a significant health concern, particularly in Korea, where it ranks third among cancers in men and sixth in overall cancer incidence as of 2021 (<xref ref-type="bibr" rid="B14">14</xref>). In Western countries such as Europe and the United States, it has been the number one cancer in men for a long time (<xref ref-type="bibr" rid="B15">15</xref>). PCa is rapidly increasing along with the increase in the aging population. Its importance is increasing in Korea, which is entering a super-aging society. PCa is a cancer with a good prognosis when detected early, with a high survival rate of more than 5 years. However, the social costs caused by PCa remain enormous.</p>
<p>Given the rising incidence of PCa and the ongoing concerns about environmental pollution, it is crucial to understand the potential role of fine dust exposure in the development of this cancer. Therefore, this study aimed to investigate the risk of PCa due to moderate level fine dust (31&#x02013;80 &#x003BC;g/m<sup>2</sup>) concentration in Korea (<xref ref-type="bibr" rid="B13">13</xref>).</p>
</sec>
<sec sec-type="methods" id="s2">
<title>2 Methods</title>
<sec>
<title>2.1 Hypothesis</title>
<p>Previous research has established that PM<sub>10</sub> is associated with various diseases, including respiratory illnesses, lung cancer, heart disease, brain disorders, chronic obstructive pulmonary disease, asthma, COPD exacerbation, esophageal cancer, and corpus uteri cancer (<xref ref-type="bibr" rid="B6">6</xref>, <xref ref-type="bibr" rid="B16">16</xref>). Particulrly, PM<sub>10</sub> is a risk factor for the development of urological cancers, including kidney cancer, PCa, and urothelial cell carcinoma (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B17">17</xref>). This study hypothesized that even moderate exposure to PM<sub>10</sub> could influence the risk of developing PCa. The specific hypothesis was as follows.</p>
<p>H1: Moderate level PM<sub>10</sub> exposure has relationship with PCa.</p>
</sec>
<sec>
<title>2.2 Data source</title>
<p>We used customized health information data from the National Health Insurance Sharing Service (NHISS). In Korea, the NHISS discloses &#x0201C;customized health information data&#x0201D; to researchers (<xref ref-type="bibr" rid="B18">18</xref>). Customized health information refers to data provided by processing citizens&#x00027; health information collected, held, and managed by the NHISS into customized data that can be used for policy and academic research purposes. The NHISS provides researchers with a sample cohort database (DB), health examination cohort DB and older adult cohort DB. The entire data period provided by the NHISS was from 2002 to 2020 (as of 2023, when this study was first conducted). This study used data from 2010 to 2020.</p>
</sec>
<sec>
<title>2.3 Study population</title>
<p>Participants were selected from the NHISS database, including individuals who underwent a baseline health examination in 2013 (<italic>n</italic> = 3,480,795). Exclusions were made as follows: participants diagnosed with cancer before the baseline examination (<italic>N</italic> = 232,019), those diagnosed with cancer in the 1st year (<italic>n</italic> = 66,322), participants with missing health examination data between 2015 and 2020 (<italic>n</italic> = 1,816,822), and those with no data on air pollution between 2010 and 2013 (<italic>n</italic> = 674,728). The final cohort consisted of 690,904 participants, with 5,935 cases (0.9%) in the PCa group and 684,969 (99.1%) in the non-PCa group. Propensity score matching (PSM) was applied to minimize selection bias, resulting in 29,674 matched participants. After excluding cases with missing data on weekly walking and drinking habits, 20,430 participants were included in the final analysis, divided into PCa (<italic>n</italic> = 4,071, 19.9%) and non-PCa groups (<italic>n</italic> = 16,359, 80.1%; <xref ref-type="fig" rid="F1">Figure 1</xref>).</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p>Flowchart of participant inclusion.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1490458-g0001.tif"/>
</fig>
<p>The period of PM<sub>10</sub> exposure covered 3 years, from 2010 to 2012 (<xref ref-type="fig" rid="F2">Figure 2</xref>). A 1-year washout period followed. The follow-up period for the target data spanned 6 years, from 2015 to 2020.</p>
<fig id="F2" position="float">
<label>Figure 2</label>
<caption><p>Participants&#x00027; timeline.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1490458-g0002.tif"/>
</fig>
</sec>
<sec>
<title>2.4 Definition of prostate cancer</title>
<p>PCa was classified under ICD-10 code C61. In this study, PCa cases were identified based on this classification, with a total of 4,071 patients diagnosed with PCa.</p>
</sec>
<sec>
<title>2.5 Particulate matter exposure (PM<sub>10</sub>)</title>
<p>PM<sub>10</sub> exposure data were obtained from the Air Korea&#x00027;s annual average air quality database, which monitors air quality across various administrative districts in Korea. The Air Korea&#x00027;s annual average air quality database is categorized by area code. It was used by matching the area code of the subject in the NHISS database. PM<sub>10</sub> refers to particulate matter with a diameter of 10 &#x003BC;m or less (<xref ref-type="bibr" rid="B19">19</xref>). In Korea, fine dust forecast grades are divided into four levels: good (0&#x02013;30 &#x003BC;g/m<sup>3</sup>), moderate (31&#x02013;80 &#x003BC;g/m<sup>3</sup>), bad (81&#x02013;150 &#x003BC;g/m<sup>3</sup>), and very bad (over 151 &#x003BC;g/m<sup>3</sup>) (<xref ref-type="bibr" rid="B13">13</xref>).</p>
</sec>
<sec>
<title>2.6 Covariate assessment</title>
<p>Eight covariates were assessed: weekly walking frequency, alcohol consumption, smoking status, hypertension, diabetes mellitus, hyperlipidemia, body mass index (BMI), and PM<sub>2.5</sub> exposure. These variables were categorized as follows: Walking per week: (1) no walking, (2) 1&#x02013;2 times per week, (3) 3&#x02013;4 times per week, and (4) 5&#x02013;7 times per week. Drinking: (1) no drinking, (2) &#x0007E;2&#x02013;3 times a month, (3) &#x0007E;1&#x02013;2 times a week, (4) 3&#x02013;4 times a week, and (5) almost daily. Smoking status: (1) non-smokers, (2) ex-smokers, and (3) smokers. Hypertension was classified into three types based on systolic blood pressure and diastolic blood pressure values: (1) normal group [systolic blood pressure (sbp): &#x0003C;120 and diastolic blood pressure (dbp): &#x0003C;80], (2) normal border group (sbp: 120&#x02013;139 or dbp: 80&#x02013;89), and (3) group suspected of hypertension (sbp: &#x02265;140 or dbp: &#x02265;90) (<xref ref-type="bibr" rid="B20">20</xref>). Diabetes mellitus was divided into three types based on fasting blood sugar: (1) normal (&#x0003C;100 mg/dL), (2) prediabetes (100&#x02013;125 mg/dL), and (3) diabetes (&#x02265;126 mg/dL) (<xref ref-type="bibr" rid="B21">21</xref>). Hyperlipidemia was divided into three types based on total cholesterol: (1) low (under 200), (2) middle (200&#x02013;239), and (3) high (&#x02265;240) (<xref ref-type="bibr" rid="B22">22</xref>). BMI was divided into three types: (1) normal weights (18.5&#x02013;24.9), (2) normal weight-border (&#x0003C;18.5 or 25&#x02013;29.9), and (3) obesity (BMI of 30 or greater) (<xref ref-type="bibr" rid="B23">23</xref>). PM<sub>2.5</sub> exposure was classified into two groups based on 25 &#x003BC;g/m<sup>3</sup>: (1) low exposure group (Under 25 &#x003BC;g/m<sup>3</sup>) and (2) high exposure group (Under 25 &#x003BC;g/m<sup>3</sup>). The average value of PM<sub>2.5</sub> was 25.48 &#x003BC;g/m<sup>3</sup> and the median value was 24.79 &#x003BC;g/m<sup>3</sup>. Therefore, the groups were divided based on the value of 25 &#x003BC;g/m<sup>3</sup>.</p>
</sec>
<sec>
<title>2.7 Statistical analysis</title>
<p>Statistical analysis was conducted using R software for data preprocessing and Propensity Score Matching (PSM), and SPSS for basic statistical analysis, chi-square tests, and multivariate logistic regression. The chi-square test was used to compare demographic characteristics by PM<sub>10</sub> exposure levels, and logistic regression analysis was used to assess the risk of PCa associated with PM<sub>10</sub> exposure. All statistical tests were two-tailed, and the significance level was set at <italic>P</italic>-values &#x0003C; 0.05. The analyses were performed using R version 4.0.4 (2020-10-10) and IBM Statistical Package for the Social Sciences (SPSS) Statistics (version 25.0; SPSS Inc.).</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>3 Results</title>
<sec>
<title>3.1 Participant characteristics</title>
<p>The study included 20,430 participants, with 67.4% aged under 65 years and 32.6% over 65 years (<xref ref-type="table" rid="T1">Table 1</xref>). The average age was 60.76 years, and the median age was 61 years. Regarding physical activity, 22.3% of participants did not engage in any walking, while 32.5% walked more than 5 times per week. Overall, 77.7% of participants walked at least once per week. Additionally, 30.8% of participants consumed alcohol two to three times per month, and 12.4% abstained from drinking entirely. The analysis also revealed that 39.9% of participants were ex-smokers, and 29.1% were non-smokers. Hypertension was suspected in 19.5% of the participants, which aligns with the global variation in hypertension prevalence, reported to be 18% in America and 27% in Africa (<xref ref-type="bibr" rid="B20">20</xref>). The majority (51.4%) had a total cholesterol level below 200 mg/dL, and 58.9% had fasting blood sugar levels under 100 mg/dL. A total of 63.4 63.4% of participants were classified within the normal BMI range (18.5 to 24.9). A total of 80.1% belonged to the No PCa group and 19.9% belonged to the PCa group.</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>Characteristics of the participants.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="center" colspan="2"><bold>Variables</bold></th>
<th valign="top" align="center"><bold>Frequency</bold></th>
<th valign="top" align="center"><bold>Percent</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="2">Age</td>
<td valign="top" align="left">&#x0003C;65 years</td>
<td valign="top" align="center">13,768</td>
<td valign="top" align="center">67.4</td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;65 years</td>
<td valign="top" align="center">6,662</td>
<td valign="top" align="center">32.6</td>
</tr> <tr>
<td valign="top" align="left" rowspan="4">Walking per week</td>
<td valign="top" align="left">No walking</td>
<td valign="top" align="center">4,561</td>
<td valign="top" align="center">22.3</td>
</tr>
<tr>
<td valign="top" align="left">1&#x02013;2 times a week</td>
<td valign="top" align="center">4,377</td>
<td valign="top" align="center">21.4</td>
</tr>
<tr>
<td valign="top" align="left">3&#x02013;4 times a week</td>
<td valign="top" align="center">4,861</td>
<td valign="top" align="center">23.8</td>
</tr>
<tr>
<td valign="top" align="left">5&#x02013;7 times a week</td>
<td valign="top" align="center">6,631</td>
<td valign="top" align="center">32.5</td>
</tr> <tr>
<td valign="top" align="left" rowspan="5">Drinking</td>
<td valign="top" align="left">No-drinking</td>
<td valign="top" align="center">2,532</td>
<td valign="top" align="center">12.4</td>
</tr>
<tr>
<td valign="top" align="left">About 2&#x02013;3 times a month</td>
<td valign="top" align="center">6,297</td>
<td valign="top" align="center">30.8</td>
</tr>
<tr>
<td valign="top" align="left">About 1&#x02013;2 times a week</td>
<td valign="top" align="center">5,004</td>
<td valign="top" align="center">24.5</td>
</tr>
<tr>
<td valign="top" align="left">3&#x02013;4 times a week</td>
<td valign="top" align="center">4,452</td>
<td valign="top" align="center">21.8</td>
</tr>
<tr>
<td valign="top" align="left">Almost everyday</td>
<td valign="top" align="center">2,145</td>
<td valign="top" align="center">10.5</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Smoking</td>
<td valign="top" align="left">Non-smoker</td>
<td valign="top" align="center">5,936</td>
<td valign="top" align="center">29.1</td>
</tr>
<tr>
<td valign="top" align="left">Ex-smoker</td>
<td valign="top" align="center">8,153</td>
<td valign="top" align="center">39.9</td>
</tr>
<tr>
<td valign="top" align="left">Smoker</td>
<td valign="top" align="center">6,341</td>
<td valign="top" align="center">31.0</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hypertension (systolic blood pressure, diastolic blood pressure)</td>
<td valign="top" align="left">Normal group (<sup>&#x0002A;</sup>sbp: &#x0003C; 120 and <sup>&#x0002A;</sup>dbp: &#x0003C; 80)</td>
<td valign="top" align="center">4,991</td>
<td valign="top" align="center">24.4</td>
</tr>
<tr>
<td valign="top" align="left">Normal border group (sbp: 120&#x02013;139 or dbp: 80&#x02013;89)</td>
<td valign="top" align="center">11,450</td>
<td valign="top" align="center">56.0</td>
</tr>
<tr>
<td valign="top" align="left">Group suspected of hypertension (sbp: &#x02265;140 or dbp: &#x02265;90)</td>
<td valign="top" align="center">3,989</td>
<td valign="top" align="center">19.5</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Diabetes mellitus (fasting blood sugar, mg/dL)</td>
<td valign="top" align="left">Normal (&#x0003C;100)</td>
<td valign="top" align="center">10,500</td>
<td valign="top" align="center">51.4</td>
</tr>
<tr>
<td valign="top" align="left">Prediabetes (100&#x02013;125)</td>
<td valign="top" align="center">7,452</td>
<td valign="top" align="center">36.5</td>
</tr>
<tr>
<td valign="top" align="left">Diabetes (&#x02265;126)</td>
<td valign="top" align="center">2,478</td>
<td valign="top" align="center">12.1</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hyperlipidemia (total cholesterol, mg/dL)</td>
<td valign="top" align="left">Under 200</td>
<td valign="top" align="center">12,043</td>
<td valign="top" align="center">58.9</td>
</tr>
<tr>
<td valign="top" align="left">200&#x02013;239</td>
<td valign="top" align="center">6,339</td>
<td valign="top" align="center">31.0</td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;240</td>
<td valign="top" align="center">2,048</td>
<td valign="top" align="center">10.0</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3"><sup>&#x0002A;</sup>BMI (kg/m<sup>2</sup>)</td>
<td valign="top" align="left">Normal weight (18.5&#x02013;24.9)</td>
<td valign="top" align="center">12,948</td>
<td valign="top" align="center">63.4</td>
</tr>
<tr>
<td valign="top" align="left">Normal weight-border (&#x0003C;18.5 or 25&#x02013;29.9)</td>
<td valign="top" align="center">7,036</td>
<td valign="top" align="center">34.4</td>
</tr>
<tr>
<td valign="top" align="left">Obesity (BMI of 30 or greater)</td>
<td valign="top" align="center">446</td>
<td valign="top" align="center">2.2</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">PM<sub>2.5</sub> exposure group</td>
<td valign="top" align="left">Under 25 &#x003BC;g/m<sup>3</sup></td>
<td valign="top" align="center">10,673</td>
<td valign="top" align="center">52.2</td>
</tr>
<tr>
<td valign="top" align="left">Over 25 &#x003BC;g/m<sup>3</sup></td>
<td valign="top" align="center">9,757</td>
<td valign="top" align="center">47.8</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">PM<sub>10</sub> exposure group</td>
<td valign="top" align="left">Low exposure group (Under 47 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">9,920</td>
<td valign="top" align="center">48.6</td>
</tr>
<tr>
<td valign="top" align="left">High exposure group (Over 47 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">10,510</td>
<td valign="top" align="center">51.4</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">Group</td>
<td valign="top" align="left">No PCa group</td>
<td valign="top" align="center">16,359</td>
<td valign="top" align="center">80.1</td>
</tr>
<tr>
<td valign="top" align="left">PCa group</td>
<td valign="top" align="center">4,071</td>
<td valign="top" align="center">19.9</td>
</tr> <tr>
<td valign="top" align="center" colspan="2">Total</td>
<td valign="top" align="center">20,430</td>
<td valign="top" align="center">100</td>
</tr></tbody>
</table>
<table-wrap-foot>
<p><sup>&#x0002A;</sup>sbp, systolic blood pressure; dbp, diastolic blood pressure; BMI, body mass index.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec>
<title>3.2 PM<sub>10</sub> exposure and baseline statistics</title>
<p>The average PM<sub>10</sub> exposure level was 47.48 &#x003BC;g/m<sup>3</sup>, with a median of 47.49 &#x003BC;g/m<sup>3</sup>. Participants were categorized into low and high PM<sub>10</sub> exposure groups based on a threshold of 47 &#x003BC;g/m<sup>3</sup>. The minimum exposure level recorded was 32.44 &#x003BC;g/m<sup>3</sup>, and the maximum was 62.92 &#x003BC;g/m<sup>3</sup>. The skewness and kurtosis values were 0.345 and 0.851, respectively, indicating a relatively normal distribution. According to Korea&#x00027;s air quality classification, these values correspond to an &#x0201C;average&#x0201D; level of PM<sub>10</sub> exposure (31&#x02013;80 &#x003BC;g/m<sup>3</sup>) (<xref ref-type="fig" rid="F3">Figure 3</xref>).</p>
<fig id="F3" position="float">
<label>Figure 3</label>
<caption><p>Particulate matter distribution (PM<sub>10</sub>).</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-12-1490458-g0003.tif"/>
</fig>
<p><xref ref-type="table" rid="T2">Table 2</xref> shows the demographics according to PM<sub>10</sub> exposure. The PCa and non-PCa groups were divided into two groups according to PM<sub>10</sub> exposure. In the non-PCa group, significant differences were observed in weekly walking (<italic>P</italic> = 0.002), drinking (<italic>P</italic> &#x0003C; 0.001), smoking (<italic>P</italic> = 0.009), BMI (<italic>P</italic> = 0.034), and PM<sub>2.5</sub> exposure (<italic>P</italic> &#x0003C; 0.001). In the PCa group, there were significant differences in walking per week (<italic>P</italic> = 0.002) and PM<sub>2.5</sub> exposure (<italic>P</italic> &#x0003C; 0.001) between low PM<sub>10</sub> exposure and high PM<sub>10</sub> exposure.</p>
<table-wrap position="float" id="T2">
<label>Table 2</label>
<caption><p>Demographics according to the PM<sub>10</sub> exposure.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="center" colspan="2"><bold>Variables</bold></th>
<th valign="top" align="center" colspan="3"><bold>Non-PCa group (</bold><italic><bold>N</bold></italic> = <bold>16,359)</bold></th>
<th valign="top" align="center" colspan="3"><bold>PCa group (</bold><italic><bold>N</bold></italic> = <bold>4,071)</bold></th>
</tr>
</thead>
<tbody>
<tr style="background-color:#919498;color:#ffffff">
<td valign="top" align="left" colspan="2"/>
<td valign="top" align="center"><bold>Low PM</bold><sub>10</sub> <bold>exposure</bold></td>
<td valign="top" align="center"><bold>High PM</bold><sub>10</sub> <bold>exposure</bold></td>
<td valign="top" align="center"><italic><bold>p</bold></italic><bold>-value</bold></td>
<td valign="top" align="center"><bold>Low PM</bold><sub>10</sub> <bold>exposure</bold></td>
<td valign="top" align="center"><bold>High PM</bold><sub>10</sub> <bold>exposure</bold></td>
<td valign="top" align="center"><italic><bold>p</bold></italic><bold>-value</bold></td>
</tr> <tr>
<td valign="top" align="left" colspan="2">No. of patients</td>
<td valign="top" align="center">8,008 (49%)</td>
<td valign="top" align="center">8,351 (51%)</td>
<td valign="top" align="center">16,359 (100%)</td>
<td valign="top" align="center">1,912 (47%)</td>
<td valign="top" align="center">2,159 (53%)</td>
<td valign="top" align="center">4,071 (100%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">Age</td>
<td valign="top" align="left">&#x0003C;65 years</td>
<td valign="top" align="center">5,413 (68%)</td>
<td valign="top" align="center">5,666 (68%)</td>
<td valign="top" align="center" rowspan="2">0.729</td>
<td valign="top" align="center">1,237 (65%)</td>
<td valign="top" align="center">1,452 (67%)</td>
<td valign="top" align="center" rowspan="2">0.086</td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;65 years</td>
<td valign="top" align="center">2,595 (32%)</td>
<td valign="top" align="center">2,685 (32%)</td>
<td valign="top" align="left">675 (35%)</td>
<td valign="top" align="center">707 (33%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="4">Walking per week</td>
<td valign="top" align="left">No walking</td>
<td valign="top" align="center">1,698 (21%)</td>
<td valign="top" align="center">1,919 (23%)</td>
<td valign="top" align="center" rowspan="4">0.002<sup>&#x0002A;&#x0002A;</sup></td>
<td valign="top" align="center">397 (21%)</td>
<td valign="top" align="center">547 (25%)</td>
<td valign="top" align="center" rowspan="4">0.002<sup>&#x0002A;&#x0002A;</sup></td>
</tr>
<tr>
<td valign="top" align="left">1&#x02013;2 times a week</td>
<td valign="top" align="center">1,663 (21%)</td>
<td valign="top" align="center">1,831 (22%)</td>
<td valign="top" align="left">408 (21%)</td>
<td valign="top" align="center">475 (22%)</td>
</tr>
<tr>
<td valign="top" align="left">3&#x02013;4 times a week</td>
<td valign="top" align="center">1,962 (25%)</td>
<td valign="top" align="center">1,915 (23%)</td>
<td valign="top" align="left">483 (25%)</td>
<td valign="top" align="center">501 (23%)</td>
</tr>
<tr>
<td valign="top" align="left">5&#x02013;7 times a week</td>
<td valign="top" align="center">2,685 (34%)</td>
<td valign="top" align="center">2,686 (32%)</td>
<td valign="top" align="left">624 (33%)</td>
<td valign="top" align="center">636 (29%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="5">Drinking</td>
<td valign="top" align="left">No-drinking</td>
<td valign="top" align="center">867 (11%)</td>
<td valign="top" align="center">1,107 (13%)</td>
<td valign="top" align="center" rowspan="5">0.000<sup>&#x0002A;&#x0002A;&#x0002A;</sup></td>
<td valign="top" align="center">243 (13%)</td>
<td valign="top" align="center">315 (15%)</td>
<td valign="top" align="center" rowspan="5">0.137</td>
</tr>
<tr>
<td valign="top" align="left">About 2&#x02013;3 times a month</td>
<td valign="top" align="center">2,500 (31%)</td>
<td valign="top" align="center">2,481 (30%)</td>
<td valign="top" align="left">651 (34%)</td>
<td valign="top" align="center">665 (31%)</td>
</tr>
<tr>
<td valign="top" align="left">About 1&#x02013;2 times a week</td>
<td valign="top" align="center">1,962 (25%)</td>
<td valign="top" align="center">2,048 (25%)</td>
<td valign="top" align="left">468 (24%)</td>
<td valign="top" align="center">526 (24%)</td>
</tr>
<tr>
<td valign="top" align="left">3&#x02013;4 times a week</td>
<td valign="top" align="center">1,800 (22%)</td>
<td valign="top" align="center">1,831 (22%)</td>
<td valign="top" align="left">371 (19%)</td>
<td valign="top" align="center">450 (21%)</td>
</tr>
<tr>
<td valign="top" align="left">Almost everyday</td>
<td valign="top" align="center">879 (11%)</td>
<td valign="top" align="center">884 (11%)</td>
<td valign="top" align="left">179 (9%)</td>
<td valign="top" align="center">203 (9%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Smoking</td>
<td valign="top" align="left">Non-smoker</td>
<td valign="top" align="center">2,351 (29%)</td>
<td valign="top" align="center">2,293 (27%)</td>
<td valign="top" align="center" rowspan="3">0.009<sup>&#x0002A;&#x0002A;</sup></td>
<td valign="top" align="center">633 (33%)</td>
<td valign="top" align="center">659 (31%)</td>
<td valign="top" align="center" rowspan="3">0.124</td>
</tr>
<tr>
<td valign="top" align="left">Ex-smoker</td>
<td valign="top" align="center">3,126 (39%)</td>
<td valign="top" align="center">3,267 (39%)</td>
<td valign="top" align="left">797 (42%)</td>
<td valign="top" align="center">963 (45%)</td>
</tr>
<tr>
<td valign="top" align="left">Smoker</td>
<td valign="top" align="center">2,531 (32%)</td>
<td valign="top" align="center">2,791 (33%)</td>
<td valign="top" align="left">482 (25%)</td>
<td valign="top" align="center">537 (25%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hypertension (systolic blood pressure, diastolic blood pressure)</td>
<td valign="top" align="left">Normal group (sbp: &#x0003C;120 and dbp: &#x0003C;80)</td>
<td valign="top" align="center">1,896 (24%)</td>
<td valign="top" align="center">2,041 (24%)</td>
<td valign="top" align="center" rowspan="3">0.399</td>
<td valign="top" align="center">508 (27%)</td>
<td valign="top" align="center">546 (25%)</td>
<td valign="top" align="center" rowspan="3">0.234</td>
</tr>
<tr>
<td valign="top" align="left">Normal border group (sbp: 120&#x02013;139 or dbp: 80&#x02013;89)</td>
<td valign="top" align="center">4,520 (56%)</td>
<td valign="top" align="center">4,630 (55%)</td>
<td valign="top" align="left">1,087 (57%)</td>
<td valign="top" align="center">1,213 (56%)</td>
</tr>
<tr>
<td valign="top" align="left">Group suspected of hypertension (sbp: &#x02265;140 or dbp: &#x02265;90)</td>
<td valign="top" align="center">1,592 (20%)</td>
<td valign="top" align="center">1,680 (20%)</td>
<td valign="top" align="left">317 (17%)</td>
<td valign="top" align="center">400 (19%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Diabetes mellitus (fasting blood sugar, mg/dL)</td>
<td valign="top" align="left">Normal (&#x0003C;100)</td>
<td valign="top" align="center">4,025 (50%)</td>
<td valign="top" align="center">4,299 (51%)</td>
<td valign="top" align="center" rowspan="3">0.286</td>
<td valign="top" align="center">1,012 (53%)</td>
<td valign="top" align="center">1,164 (54%)</td>
<td valign="top" align="center" rowspan="3">0.700</td>
</tr>
<tr>
<td valign="top" align="left">Prediabetes (100&#x02013;125)</td>
<td valign="top" align="center">2,970 (37%)</td>
<td valign="top" align="center">3,010 (36%)</td>
<td valign="top" align="left">694 (36%)</td>
<td valign="top" align="center">778 (36%)</td>
</tr>
<tr>
<td valign="top" align="left">Diabetes (&#x02265;126)</td>
<td valign="top" align="center">1,013 (13%)</td>
<td valign="top" align="center">1,042 (12%)</td>
<td valign="top" align="left">206 (11%)</td>
<td valign="top" align="center">217 (10%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hyperlipidemia (total cholesterol, mg/dL)</td>
<td valign="top" align="left">Under 200</td>
<td valign="top" align="center">4,693 (59%)</td>
<td valign="top" align="center">4,975 (60%)</td>
<td valign="top" align="center" rowspan="3">0.252</td>
<td valign="top" align="center">1,090 (57%)</td>
<td valign="top" align="center">1,285 (60%)</td>
<td valign="top" align="center" rowspan="3">0.182</td>
</tr>
<tr>
<td valign="top" align="left">200&#x02013;239</td>
<td valign="top" align="center">2,521 (31%)</td>
<td valign="top" align="center">2,529 (30%)</td>
<td valign="top" align="left">617 (32%)</td>
<td valign="top" align="center">672 (31%)</td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;240</td>
<td valign="top" align="center">794 (10%)</td>
<td valign="top" align="center">847 (10%)</td>
<td valign="top" align="left">205 (11%)</td>
<td valign="top" align="center">202 (9%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">BMI (kg/m<sup>2</sup>)</td>
<td valign="top" align="left">Normal weight (18.5&#x02013;24.9)</td>
<td valign="top" align="center">5,079 (63%)</td>
<td valign="top" align="center">5,365 (64%)</td>
<td valign="top" align="center" rowspan="3">0.034<sup>&#x0002A;</sup></td>
<td valign="top" align="center">1,172 (61%)</td>
<td valign="top" align="center">1,332 (62%)</td>
<td valign="top" align="center" rowspan="3">0.415</td>
</tr>
<tr>
<td valign="top" align="left">Normal weight-border (&#x0003C;18.5 or 25&#x02013;29.9)</td>
<td valign="top" align="center">2,727 (34%)</td>
<td valign="top" align="center">2,824 (34%)</td>
<td valign="top" align="left">707 (37%)</td>
<td valign="top" align="center">778 (36%)</td>
</tr>
<tr>
<td valign="top" align="left">Obesity (BMI of 30 or greater)</td>
<td valign="top" align="center">202 (3%)</td>
<td valign="top" align="center">162 (2%)</td>
<td valign="top" align="left">33 (2%)</td>
<td valign="top" align="center">49 (2%)</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">PM<sub>2.5</sub> exposure group</td>
<td valign="top" align="left">Low exposure group (Under 25 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">5,367 (67%)</td>
<td valign="top" align="center">3,115 (37%)</td>
<td valign="top" align="center" rowspan="2">0.000<sup>&#x0002A;&#x0002A;&#x0002A;</sup></td>
<td valign="top" align="center">1,264 (66%)</td>
<td valign="top" align="center">927 (43%)</td>
<td valign="top" align="center" rowspan="2">0.000<sup>&#x0002A;&#x0002A;&#x0002A;</sup></td>
</tr>
<tr>
<td valign="top" align="left">High exposure group (Under 25 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">2,641 (33%)</td>
<td valign="top" align="center">5,236 (63%)</td>
<td valign="top" align="left">648 (34%)</td>
<td valign="top" align="center">1,232 (57%)</td>
</tr></tbody>
</table>
<table-wrap-foot>
<p><sup>&#x0002A;</sup>P &#x0003C; 0.05; <sup>&#x0002A;&#x0002A;</sup>P &#x0003C; 0.01; <sup>&#x0002A;&#x0002A;&#x0002A;</sup>P &#x0003C; 0.001.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec>
<title>3.3 Risk of prostate cancer by PM<sub>10</sub> exposure</title>
<p><xref ref-type="table" rid="T3">Table 3</xref> presents the odds ratios (95% CI) for PCa according to moderate PM<sub>10</sub> exposure, categorized into low (9,920 participants) and high (10,510 participants) exposure groups. Moderate PM<sub>10</sub> exposure was identified as a significant predictor of PCa in all models: Model 1 (OR = 1.118), Model 2 (OR = 1.119), and Model 3 (OR = 1.121). These models were adjusted for various factors, including age, PM<sub>2.5</sub>, drinking habits, walking frequency, smoking status, hypertension, diabetes, hyperlipidemia, and BMI.</p>
<table-wrap position="float" id="T3">
<label>Table 3</label>
<caption><p>Odds ratio of PCa according to the moderate PM<sub>10</sub> exposure.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left"><bold>PM<sub>10</sub></bold></th>
<th valign="top" align="center"><bold>Event</bold></th>
<th valign="top" align="center" colspan="3"><bold>Odds ratio (95% CI)</bold></th>
</tr>
</thead>
<tbody>
<tr style="background-color:#919498;color:#ffffff">
<td/>
<td/>
<td valign="top" align="center"><bold>Model 1</bold></td>
<td valign="top" align="center"><bold>Model 2</bold></td>
<td valign="top" align="center"><bold>Model 3</bold></td>
</tr> <tr>
<td valign="top" align="left">Low exposure group (under 47 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">9,920</td>
<td valign="top" align="center">1 (ref.)</td>
<td valign="top" align="center">1 (ref.)</td>
<td valign="top" align="center">1 (ref.)</td>
</tr> <tr>
<td valign="top" align="left">High exposure group (under 47 &#x003BC;g/m<sup>3</sup>)</td>
<td valign="top" align="center">10,510</td>
<td valign="top" align="center">1.118 (95% CI: 1.041, 1.201)</td>
<td valign="top" align="center">1.119 (95% CI: 1.042, 1.203)</td>
<td valign="top" align="center">1.121 (95% CI: 1.043, 1.204)</td>
</tr> <tr>
<td valign="top" align="left" colspan="2"><italic>P</italic> for trend</td>
<td valign="top" align="center">0.002<xref ref-type="table-fn" rid="TN3a"><sup>&#x0002A;&#x0002A;</sup></xref></td>
<td valign="top" align="center">0.002<xref ref-type="table-fn" rid="TN3a"><sup>&#x0002A;&#x0002A;</sup></xref></td>
<td valign="top" align="center">0.002<xref ref-type="table-fn" rid="TN3a"><sup>&#x0002A;&#x0002A;</sup></xref></td>
</tr></tbody>
</table>
<table-wrap-foot>
<p>Model 1 was adjusted for age, PM<sub>2.5</sub>. Model 2 was adjusted for age, PM<sub>2.5</sub>, alcohol consumption, walking, and smoking. Model 3 was adjusted for age, PM<sub>2.5</sub>, alcohol consumption, walking, smoking, Hypertension, Diabetes mellitus, Hyperlipidemia, and BMI.</p>
<fn id="TN3a">
<label>&#x0002A;&#x0002A;</label><p>P &#x0003C; 0.01.</p></fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec>
<title>3.4 Risk of prostate cancer in clinically relevant subgroups</title>
<p>The subgroup results according to moderate exposure to PM<sub>10</sub> are as follows: Not all the sub-variables were vulnerable to moderate PM<sub>10</sub> exposure (<xref ref-type="table" rid="T4">Table 4</xref>). However, some subgroups were found to be vulnerable to even moderate exposure to PM<sub>10</sub>: under 65 years group (OR =1.121), under 25 &#x003BC;g/m<sup>3</sup> group (OR = 1.264), no walking group (OR = 1.219), ex-smoker group (OR = 1.156), group suspected of hypertension (OR = 1.196), under 200 of hyperlipidemia (OR = 1.112), obesity group (BMI of 30 or greater) (OR = 1.851), and drinking group 3&#x02013;4 times a week (OR = 1.192).</p>
<table-wrap position="float" id="T4">
<label>Table 4</label>
<caption><p>Odds ratio of PCa in relevant subgroups.</p></caption>
<table frame="box" rules="all">
<thead>
<tr style="background-color:#919498;color:#ffffff">
<th valign="top" align="left" colspan="2"><bold>Factors</bold></th>
<th valign="top" align="left"><bold>Low exposure group (under 47 &#x003BC;g/m<sup>3</sup>)</bold></th>
<th valign="top" align="center"><bold>High exposure group (under 47 &#x003BC;g/m<sup>3</sup>)</bold></th>
<th valign="top" align="center"><bold>Sig</bold>.</th>
</tr>
</thead>
<tbody>
<tr style="background-color:#919498;color:#ffffff">
<td valign="top" align="left" colspan="2"/>
<td valign="top" align="left"><bold>Reference</bold></td>
<td valign="top" align="center"><bold>Odds ratio (95% CI)</bold></td>
<td/>
</tr> <tr>
<td valign="top" align="left" rowspan="2">Age</td>
<td valign="top" align="left"><bold>&#x0003C;65 years</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.121 (1.031&#x02013;1.220)</bold></td>
<td valign="top" align="center"><bold>0.008</bold><sup><bold>&#x0002A;&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;65 years</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.012 (0.899&#x02013;1.140)</td>
<td valign="top" align="center">0.840</td>
</tr> <tr>
<td valign="top" align="left" rowspan="2">PM<sub>2.5</sub></td>
<td valign="top" align="left"><bold>Under 25</bold> <bold>&#x003BC;g/m</bold><sup><bold>3</bold></sup></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.264 (1.148&#x02013;1.390)</bold></td>
<td valign="top" align="center"><bold>0.000</bold><sup><bold>&#x0002A;&#x0002A;&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">Over 25 &#x003BC;g/m<sup>3</sup></td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">0.959 (0.863&#x02013;1.066)</td>
<td valign="top" align="center">0.438</td>
</tr> <tr>
<td valign="top" align="left" rowspan="4">Walking per week</td>
<td valign="top" align="left"><bold>No walking</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.219 (1.055&#x02013;1.409)</bold></td>
<td valign="top" align="center"><bold>0.007</bold><sup><bold>&#x0002A;&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">1&#x02013;2 times a week</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.057 (0.912&#x02013; 1.226)</td>
<td valign="top" align="center">0.460</td>
</tr>
<tr>
<td valign="top" align="left">3&#x02013;4 times a week</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.063 (0.924&#x02013; 1.222)</td>
<td valign="top" align="center">0.394</td>
</tr>
<tr>
<td valign="top" align="left">5&#x02013;7 times a week</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.019 (0.901&#x02013; 1.152)</td>
<td valign="top" align="center">0.765</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Smoke</td>
<td valign="top" align="left">Non&#x02013;smoker</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.067 (0.944&#x02013;1.207)</td>
<td valign="top" align="center">0.300</td>
</tr>
<tr>
<td valign="top" align="left"><bold>Ex&#x02013;smoker</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.156 (1.040&#x02013; 1.285)</bold></td>
<td valign="top" align="center"><bold>0.007</bold><sup><bold>&#x0002A;&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">Smoker</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.010 (0.883&#x02013;1.155)</td>
<td valign="top" align="center">0.881</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hypertension (systolic blood pressure, diastolic blood pressure)</td>
<td valign="top" align="left">Normal group (sbp: &#x0003C;120 and dbp: &#x0003C;80)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">0.998 (0.871&#x02013;1.144)</td>
<td valign="top" align="center">0.982</td>
</tr>
<tr>
<td valign="top" align="left">Normal border group (sbp: 120&#x02013;139 or dbp: 80&#x02013;89)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.089 (0.994&#x02013;1.194)</td>
<td valign="top" align="center">0.067</td>
</tr>
<tr>
<td valign="top" align="left"><bold>Group suspected of hypertension (sbp:</bold> <bold>&#x02265;140 or dbp:</bold> <bold>&#x02265;90)</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.196 (1.016&#x02013;1.407)</bold></td>
<td valign="top" align="center"><bold>0.031</bold><sup><bold>&#x0002A;</bold></sup></td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Diabetes mellitus (fasting blood sugar, mg/dL)</td>
<td valign="top" align="left">Normal (&#x0003C;100)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.077 (0.980&#x02013;1.184)</td>
<td valign="top" align="center">0.125</td>
</tr>
<tr>
<td valign="top" align="left">Prediabetes (100&#x02013;125)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.106 (0.987&#x02013;1.240)</td>
<td valign="top" align="center">0.083</td>
</tr>
<tr>
<td valign="top" align="left">Diabetes (&#x02265;126)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.024 (0.831&#x02013;1.263)</td>
<td valign="top" align="center">0.824</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">Hyperlipidemia (total cholesterol, mg/dL)</td>
<td valign="top" align="left"><bold>Under 200</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.112 (1.016&#x02013;1.217)</bold></td>
<td valign="top" align="center"><bold>0.021</bold><sup><bold>&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">200&#x02013;239</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.086 (0.961&#x02013;1.227)</td>
<td valign="top" align="center">0.188</td>
</tr>
<tr>
<td valign="top" align="left">&#x02265;240</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">0.924 (0.743&#x02013;1.148)</td>
<td valign="top" align="center">0.474</td>
</tr> <tr>
<td valign="top" align="left" rowspan="3">BMI (kg/m<sup>2</sup>)</td>
<td valign="top" align="left">Normal weight (18.5&#x02013;24.9)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.076 (0.986&#x02013;1.174)</td>
<td valign="top" align="center">0.101</td>
</tr>
<tr>
<td valign="top" align="left">Normal weight&#x02013;border (&#x0003C;18.5 or 25&#x02013;29.9)</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.063 (0.948&#x02013;1.192)</td>
<td valign="top" align="center">0.299</td>
</tr>
<tr>
<td valign="top" align="left"><bold>Obesity (BMI of 30 or greater)</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.851 (1.137&#x02013;3.014)</bold></td>
<td valign="top" align="center"><bold>0.013</bold><sup><bold>&#x0002A;</bold></sup></td>
</tr> <tr>
<td valign="top" align="left" rowspan="5">Drinking</td>
<td valign="top" align="left">No&#x02013;drinking</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.015 (0.840&#x02013;1.227)</td>
<td valign="top" align="center">0.876</td>
</tr>
<tr>
<td valign="top" align="left">About 2&#x02013;3 times a month</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.029 (0.912&#x02013;1.162)</td>
<td valign="top" align="center">0.641</td>
</tr>
<tr>
<td valign="top" align="left">About 1&#x02013;2 times a week</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.077 (0.937&#x02013;1.237)</td>
<td valign="top" align="center">0.297</td>
</tr>
<tr>
<td valign="top" align="left"><bold>3&#x02013;4 times a week</bold></td>
<td valign="top" align="left"><bold>1 (ref.)</bold></td>
<td valign="top" align="center"><bold>1.192 (1.024&#x02013;1.388)</bold></td>
<td valign="top" align="center"><bold>0.023</bold><sup><bold>&#x0002A;</bold></sup></td>
</tr>
<tr>
<td valign="top" align="left">Almost everyday</td>
<td valign="top" align="left">1 (ref.)</td>
<td valign="top" align="center">1.128 (0.904&#x02013;1.407)</td>
<td valign="top" align="center">0.288</td>
</tr></tbody>
</table>
<table-wrap-foot>
<p><sup>&#x0002A;</sup>P &#x0003C; 0.05.</p>
<p><sup>&#x0002A;&#x0002A;</sup>P &#x0003C; 0.01.</p>
<p><sup>&#x0002A;&#x0002A;&#x0002A;</sup>P &#x0003C; 0.001.</p>
<p>The bold values are significant results.</p>
</table-wrap-foot>
</table-wrap>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>4 Discussion</title>
<p>This study aimed to determine the risks associated with moderate levels of PM<sub>10</sub> exposure for the development of PCa, based on the fine dust standards of the Korean Ministry of Environment (<xref ref-type="bibr" rid="B13">13</xref>). The findings reveal several important insights.</p>
<p>First, we observed that even moderate levels (31&#x02013;80 &#x003BC;g/m<sup>3</sup>, Korea standard) (<xref ref-type="bibr" rid="B13">13</xref>) of PM<sub>10</sub> exposure are significant risk factors for the development of PCa. According to the Korean air-quality classifications, a PM<sub>10</sub> level of 47 &#x003BC;g/m<sup>3</sup> is considered moderate level, a level at which masks are typically not worn by the public (<xref ref-type="bibr" rid="B13">13</xref>). However, our findings suggest that even at these moderate levels, PM<sub>10</sub> exposure can influence the development of urological cancers such as PCa. This aligns with previous studies that have highlighted detrimental effects of PM<sub>10</sub> on cancer risk (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B24">24</xref>). There is little research on moderate level PM<sub>10</sub>, so in-depth discussion on it is limited. However, it is very meaningful that disease risks were predicted even for moderate level fine dust, even based on Korean standards.</p>
<p>In Korea, days with poor air quality have increased since 2012 due to an increase in PM, and various measures have been sought along with public concerns (<xref ref-type="bibr" rid="B9">9</xref>). Since 2015, air quality alerts have increased nationwide (<xref ref-type="bibr" rid="B25">25</xref>). Nevertheless, as described in the introduction, Korea PM<sub>10</sub> standards are less stringent than those in other countries. The PM<sub>10</sub> standard levels of 2021 WHO recommendation is 15 &#x003BC;g/m<sup>3</sup> for the annual average and 45 &#x003BC;g/m<sup>3</sup> for the 24-h average (<xref ref-type="bibr" rid="B12">12</xref>). The PM<sub>10</sub> standard levels is 50 &#x003BC;g/m<sup>3</sup> for the annual average and 100 &#x003BC;g/m<sup>3</sup> for the 24-h average in Korea (<xref ref-type="bibr" rid="B13">13</xref>). This study emphasizes that Korea should further strengthen air quality standards for PM<sub>10</sub>.</p>
<p>In addition, it is critical to implement more detailed guidelines and actively promote the use of masks and air purification strategies when air quality deteriorates to hazardous levels. Prior research has demonstrated that education about the health risks associated with fine dust can influence public perceptions of susceptibility and severity (<xref ref-type="bibr" rid="B26">26</xref>). Our findings support the need for robust awareness campaigns to mitigate these risks.</p>
<p>Second, the study highlights the importance of individual physical characteristics in the relationship between PM<sub>10</sub> exposure and PCa development. We found that the risk of PCa due PM<sub>10</sub> exposure is higher in patients under 65 years of age, in those with suspected hypertension, in individuals with total cholesterol levels below 200 mg/dL, and in obese individuals. These findings contribute to the ongoing debate on the association between obesity, air pollution, and cancer risk (<xref ref-type="bibr" rid="B27">27</xref>). Previous research continues to explore the relationship between local environment factors and cancer incidence (<xref ref-type="bibr" rid="B28">28</xref>). Many studies have suggested that air pollution may negatively contribute to body weight status in adults (<xref ref-type="bibr" rid="B29">29</xref>&#x02013;<xref ref-type="bibr" rid="B33">33</xref>), our results also indicate that in obesity, PM<sub>10</sub> exposure is a significant risk factor for PCa. Thus, identifying high-risk groups based on major factors such as underlying health conditions is crucial, and targeted mid- to long-term support for these groups should be prioritized.</p>
<p>Third, lifestyle habits also play a crucial role in the relationship between PM<sub>10</sub> exposure and PCa. Our study found that the risk of developing PCa due to PM<sub>10</sub> exposure is elevated in individuals who do not engage in regular exercise, in ex-smokers, and in those who consume alcohol three to four times a week. These results are consistent with previous research indicating that lifestyle management can help mitigate the incidence of cancer related to air pollution (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B28">28</xref>, <xref ref-type="bibr" rid="B34">34</xref>, <xref ref-type="bibr" rid="B35">35</xref>). In order to reduce the social cost of cancer, a comprehensive solution approach is needed that addresses environmental issues such as air pollution and actively corrects people&#x00027;s lifestyle habits.</p>
<p>Finally, we observed that the risk of developing PCa due to PM<sub>10</sub> exposure was higher even in the presence of low PM<sub>2.5</sub>. This result was very interesting because even when PM<sub>2.5</sub> is low, increased PM<sub>10</sub> exposure increases the risk of developing PCa. Both PM<sub>10</sub> and PM<sub>2.5</sub> are air quality measurements, and although they are very important air quality measurement factors and global challenge issues (<xref ref-type="bibr" rid="B36">36</xref>&#x02013;<xref ref-type="bibr" rid="B40">40</xref>), they should be viewed separately. Depending on the disease, PM<sub>2.5</sub> and PM<sub>10</sub> exposure often affect the disease at the same time (<xref ref-type="bibr" rid="B40">40</xref>). In fact, there are days when PM<sub>2.5</sub> levels are low but PM<sub>10</sub> levels are high. Although it is important to understand the impact of the integrated air quality index or multiple pollutants together in some cases (<xref ref-type="bibr" rid="B41">41</xref>), the fact that PM<sub>10</sub> alone still increases the risk of disease is very significant.</p>
<p>Despite these significant findings, our study has several limitations. First, air pollution encompasses a range of pollutants, including PM<sub>10</sub>, NO<sub>2</sub>, and PM<sub>2.5</sub> (<xref ref-type="bibr" rid="B42">42</xref>), and the incidence of various cancers has been consistently linked to PM<sub>2.5</sub> exposure (<xref ref-type="bibr" rid="B43">43</xref>, <xref ref-type="bibr" rid="B44">44</xref>). However, our study focused mainly on the relationship between PM<sub>10</sub> exposure and PCa. Future research should consider a broader range of air pollutants to provide a more comprehensive understanding of their combined effects. Second, the study limited the period of PM<sub>10</sub> exposure to 3 years (2010&#x02013;2012). We used PM<sub>10</sub> exposure data from Air Korea&#x00027;s annual average air quality database. The Air Korea&#x00027;s annual average air quality database has been providing air quality data since 2009, we identified appropriate data for the study and used air quality data from 2010 to 2012, which provided the longest follow-up period. Therefore, we used only 3 years of data to select data with as many area codes as possible that can be matched with NHISS customized health information data and with PM<sub>10</sub> values that can be used in research. Additional research with longer exposure periods is needed to fully assess the long-term risks associated with fine dust exposure. Third, this study considered some lifestyle factors such as alcohol consumption, smoking, and physical activity. However, there may be other lifestyle factors, such as diet and occupational exposure, which could also influence the risk of prostate cancer. However, the customized health information data from NHISS does not provide additional lifestyle data (such as diet and occupational exposure), so it could not be utilized. Future research is needed to derive risk factors by including various lifestyles. Fourth, this study is based on Korea&#x00027;s environmental standards (<xref ref-type="bibr" rid="B13">13</xref>), and since environmental standards may differ from country to country, there may be limitations in the global applicability of the research results. Future research needs to be conducted based on global standards. Fifth, there is research that shows a relationship between air pollution and temperature (<xref ref-type="bibr" rid="B45">45</xref>). If we can secure data on temperature in the future, it would be desirable to analyze various environmental factors such as temperature in addition to air quality.</p>
<p>Despite these limitations, this study provides important insights into the relationship between moderate PM<sub>10</sub> exposure and increased PCa risk. The findings also underscore the need for more stringent and detailed environmental standards for PM<sub>10</sub>. Reducing the disease risk from fine dust requires a mid- to long-term, comprehensive solution approach to identify high-risk groups and reduce social costs. In addition, public health should emphasize the importance of wearing masks and managing air quality, and managing lifestyle habits to protect the negative health effects of fine dust exposure.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s5">
<title>Data availability statement</title>
<p>The national health insurance sharing service requires approval of institutional review board. Requests to access these datasets should be directed to NHISS bigdata service, <email>0075030&#x00040;nhis.or.kr</email>.</p>
</sec>
<sec sec-type="ethics-statement" id="s6">
<title>Ethics statement</title>
<p>We used the public data set from the National Health Insurance System that is not individually identifiable after approval by the Institutional Review Board of Dankook University (DKU2022-06-002).</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>MJR: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Project administration, Software, Validation, Visualization, Writing &#x02013; original draft, Writing &#x02013; review &#x00026; editing. YP: Conceptualization, Data curation, Investigation, Validation, Writing &#x02013; original draft, Writing &#x02013; review &#x00026; editing. JP: Conceptualization, Data curation, Funding acquisition, Investigation, Project administration, Supervision, Validation, Writing &#x02013; original draft, Writing &#x02013; review &#x00026; editing.</p>
</sec>
<sec sec-type="funding-information" id="s8">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea Government (MSIT; No. NRF-2022R1G1A1011635).</p>
</sec>
<ack><p>This study was performed using the database from the National Health Insurance System (NHIS-2023-1-160) and the results do not necessarily represent the opinion of the National Health Insurance Corporation.</p>
</ack>
<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>
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